Chapter 40. Existing Stationary Sources
Part I
Special Provisions
9VAC5-40-10. Applicability.
A. The provisions of this chapter, unless specified otherwise, shall apply to existing sources for which emission standards are prescribed under this chapter.
B. The provisions of this chapter shall not apply to sources specified below except in cases where the provisions of this chapter (i) specifically provide otherwise or (ii) are more restrictive than the provisions of 9VAC5-50, 9VAC5-80, or any permit issued pursuant to 9VAC5-80. Sources exempted under this subsection shall be subject to the provisions of 9VAC5-50 or 9VAC5-60, or both, as applicable.
1. Any stationary source (or portion of it), the construction, modification or relocation of which commenced on or after March 17, 1972.
2. Any stationary source (or portion of it), the reconstruction of which commenced on or after December 10, 1976.
C. If a facility becomes subject to any requirement in the Regulations for the Control and Abatement of Air Pollution because it exceeds an exemption level, the facility shall continue to be subject to all applicable requirements even if future conditions cause the facility to fall below the exemption level.
D. Any owner subject to the provisions of this chapter may provide any report, notification or other document by electronic media if acceptable to both the owner and board.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-01, eff. July 1, 1991; amended, Virginia Register Volume 18, Issue 21, eff. August 1, 2002; Volume 40, Issue 14, eff. April 11, 2024.
9VAC5-40-20. Compliance.
A. Ninety days after the effective date of any emission standard prescribed under this chapter, no owner or other person shall operate any existing source in violation of such standard.
1. Compliance with standards in this chapter, other than opacity standards, shall be determined by emission tests established by 9VAC5-40-30, unless specified otherwise in the applicable standard.
2. Compliance with federal requirements in this chapter may be determined by alternative or equivalent methods only if approved by the administrator. For purposes of this subsection, federal requirements consist of the following:
a. New source performance standards established pursuant to § 111 of the federal Clean Air Act.
b. All terms and conditions in a federal operating permit, including any provisions that limit a source's potential to emit, unless expressly designated as not federally enforceable.
c. Limitations and conditions that are part of an implementation plan.
d. Limitations and conditions that are part of a section 111(d) or section 111(d)/129 plan.
e. Limitations and conditions that are part of a federal construction permit issued under 40 CFR 52.21 or any construction permit issued under regulations approved by EPA in accordance with 40 CFR Part 51.
f. Limitations and conditions that are part of an operating permit issued pursuant to a program approved by EPA into an implementation plan as meeting EPA's minimum criteria for federal enforceability, including adequate notice and opportunity for EPA and public comment prior to issuance of the final permit and practicable enforceability.
3. Compliance with opacity standards in this chapter may be determined by one or more of the following means:
a. Conducting observations in accordance with Reference Method 9 or any alternative method approved by EPA. For purposes of determining initial compliance, the minimum total time of observations shall be three hours (30 six-minute averages) for the emission test or other set of observations (meaning those fugitive-type emission sources subject only to an opacity standard). Opacity readings of portions of plumes which contain condensed, uncombined water vapor shall not be used for purposes of determining compliance with opacity standards.
b. Evaluation of data resulting from use of continuous monitoring by transmissometer, provided the instrument used meets Performance Specification 1 in Appendix B of 40 CFR Part 60 and has been properly maintained and that the resulting data have not been altered in any way.
c. Use of any other method approved by EPA.
4. The opacity standards prescribed under this chapter shall apply at all times except during periods of startup, shutdown, malfunction, and as otherwise provided in the applicable standard. This exception shall not apply to the following federal requirements:
a. Limitations and conditions that are part of an implementation plan.
b. Limitations and conditions that are part of a federal construction permit issued under 40 CFR 52.21 or any construction permit issued under regulations approved by EPA in accordance with 40 CFR Part 51.
c. Limitations and conditions that are part of an operating permit issued pursuant to a program approved by EPA into an implementation plan as meeting EPA's minimum criteria for federal enforceability, including adequate notice and opportunity for EPA and public comment prior to issuance of the final permit and practicable enforceability.
B. No owner of an existing source subject to the provisions of this chapter shall fail to conduct emission tests as required under this chapter.
C. No owner of an existing source subject to the provisions of this chapter shall fail to install, calibrate, maintain and operate equipment for continuously monitoring and recording emissions or process parameters or both as required under this chapter.
D. No owner of an existing source subject to the provisions of this chapter shall fail to provide notifications and reports, revise reports, maintain records or report emission test or monitoring results as required under this chapter.
E. At all times, including periods of startup, shutdown, soot blowing and malfunction, owners shall, to the extent practicable, maintain and operate any affected facility including associated air pollution control equipment in a manner consistent with air pollution control practices for minimizing emissions. Determination of whether acceptable operating and maintenance procedures are being used will be based on information available to the board, which may include, but is not limited to, monitoring results, opacity observations, review of operating and maintenance procedures, and inspection of the source.
F. At all times the disposal of volatile organic compounds shall be accomplished by taking measures, to the extent practicable, consistent with air pollution control practices for minimizing emissions. Volatile organic compounds shall not be intentionally spilled, discarded in sewers which are not connected to a treatment plant, or stored in open containers or handled in any other manner that would result in evaporation beyond that consistent with air pollution control practices for minimizing emissions.
G. The following provisions apply with respect to demonstrating compliance with opacity standards.
1. For the purpose of demonstrating initial compliance, opacity observations shall be conducted concurrently with the initial emission test unless one of the following conditions apply:
a. If no emission test is required, then opacity observations shall be conducted within 60 days after achieving the maximum production rate at which the affected facility will be operated but no later than 180 days after the compliance date.
b. If visibility or other conditions prevent the opacity observations from being conducted concurrently with the initial emission test, the owner shall reschedule the opacity observations as soon after the initial emission test as possible, but not later than 30 days thereafter, and shall advise the board of the rescheduled date. In these cases, the 30-day prior notification to the board required by 9VAC5-40-50 A 3 shall be waived. The rescheduled opacity observations shall be conducted (to the extent possible) under the same operating conditions that existed during the initial emission test. The visible emissions observer shall determine whether visibility or other conditions prevent the opacity observations from being made concurrently with the initial emission test in accordance with procedures contained in Reference Method 9.
Opacity readings of portions of plumes which contain condensed, uncombined water vapor shall not be used for purposes of determining compliance with opacity standards. The owner of an affected facility shall make available, upon request by the board, such records as may be necessary to determine the conditions under which the visual observations were made and shall provide evidence indicating proof of current visible observer emission certification. The results of continuous monitoring by transmissometer which indicate that the opacity at the time visual observations were made was not in excess of the standard are probative but not conclusive evidence of the actual opacity of an emission, provided the source meets the burden of proving that the instrument used meets (at the time of the alleged violation) Performance Specification 1 in Appendix B of 40 CFR Part 60 and has been properly maintained and (at the time of the alleged violation) that the resulting data have not been altered in any way.
2. Except as provided in subdivision 3 of this subsection, the owner of an affected facility to which an opacity standard in this chapter applies shall conduct opacity observations in accordance with subdivision A 3 of this section, shall record the opacity of emissions, and shall report to the board the opacity results along with the results of the initial emission test. The inability of an owner to secure a visible emissions observer shall not be considered a reason for not conducting the opacity observations concurrent with the initial emission test.
3. The owner of an affected facility to which an opacity standard in this chapter applies may request the board to determine and to record the opacity of emissions from the affected facility during the initial emission test and at such times as may be required. The owner of the affected facility shall report the opacity results. Any request to the board to determine and to record the opacity of emissions from an affected facility shall be included in the notification required in 9VAC5-40-50 A 3. If, for some reason, the board cannot determine and record the opacity of emissions from the affected facility during the emission test, then the provisions of subdivision 1 of this subsection shall apply.
4. An owner of an affected facility using a continuous opacity monitor (transmissometer) shall record the monitoring data produced during the initial emission test and shall furnish the board a written report of the monitoring results along with the Reference Method 9 and initial emission test results.
H. The following provisions apply with respect to new or more stringent emission standards:
1. The following provisions apply with respect to emission standards for volatile organic compounds:
a. In the case of any emission standard for volatile organic compounds adopted by the board which is more stringent than the emission standard for the source in effect prior to such adoption, if any, or where there was no emission standard, the source shall not be considered in violation of the newly adopted emission standard provided that the owner accomplishes the following:
(1) Complies with the emission standard as expeditiously as possible but in no case later than one year after the effective date of the emission standard.
(2) Within one month of achieving compliance, notifies the board of same.
(3) Within six months of achieving compliance, demonstrates to the satisfaction of the board compliance with the emission standard.
b. The reprieve provided by subdivision 1 a of this subsection shall only apply in cases where it is necessary for the owner to:
(1) Install emission control equipment or other equipment that alters the facility in order to comply with the emission standard; or
(2) Switch fuel or raw materials or both in order to comply with the emission standard.
c. Owners of sources not in compliance with the newly adopted emission standard, but in compliance with the provisions of subdivision 1 a of this subsection shall not be subject to any penalties for violation of the newly adopted emission standard that may be required by the Virginia Air Pollution Control Law.
d. Any reprieve from the sanctions of any provision of the Virginia Air Pollution Control Law pursuant to subdivision 1 a of this subsection shall not extend beyond the date by which compliance is to be achieved.
e. Nothing in subdivision 1 a of this subsection shall prevent the board from promulgating a separate compliance schedule for any source if the board finds that it is technologically infeasible or it is infeasible due to the nonavailability of necessary equipment or materials or other circumstances beyond the owner's control for the source to achieve compliance within one year of the effective date of an emission standard.
f. All compliance schedules proposed or prescribed under this section shall provide for compliance with the applicable emission standards as expeditiously as practicable.
g. Any compliance schedule approved under this subsection may be revoked at any time if the source owner does not meet the stipulated increments of progress, and if the failure to meet an increment is likely to result in failure to meet the date for final compliance, and the failure to meet the increment is due to causes within the owner's control.
2. The following provisions apply with respect to emission standards for pollutants other than volatile organic compounds:
a. In the case of any emission standard adopted by the board which is more stringent than the emission standard for the source in effect prior to such adoption, if any, or where there was no emission standard, the source shall not be considered in violation of the newly adopted emission standard provided that the owner accomplishes the following:
(1) Submits in a form and manner satisfactory to the board, a control program showing how compliance shall be achieved within the time frame in the applicable compliance schedule prescribed under 9VAC5-40-21; or, where no applicable compliance schedule is prescribed under 9VAC5-40-21, how compliance shall be achieved as expeditiously as possible; but in no case later than three years after the effective date of such emission standard.
(2) Receives approval of the board of such control program.
(3) Complies with all provisions, terms and conditions of the control program including the increments of progress.
b. The reprieve provided by subdivision 2 a of this subsection shall only apply in cases where it is necessary for the owner to:
(1) Install emission control equipment or other equipment that alters the facility in order to comply with the emission standard; or
(2) Switch fuel or raw materials or both in order to comply with the emission standard.
c. Owners of sources not in compliance with the newly adopted emission standard, but in compliance with the provisions of subdivision 2 a of this subsection shall not be subject to any penalties for violation of the newly adapted emission standard that may be required by the Virginia Air Pollution Control Law.
d. Any reprieve from the sanctions of any provision of the Virginia Air Pollution Control Law pursuant to subdivision 2 a of this subsection shall not extend beyond the date, specified in the emission standard or approved control program, by which compliance is to be achieved.
e. Control programs submitted under the provisions of subdivision 2 a of this subsection shall be processed in accordance with the provisions of 9VAC5-20-170. However, if the control program contains a compliance schedule which conforms to the applicable schedule prescribed in 9VAC5-40-21, the public hearing provision of 9VAC5-20-170 shall not apply.
f. Nothing in this section shall prevent the board from promulgating a separate compliance schedule for any source if the board finds that the application of a compliance schedule in 9VAC5-40-21 is technologically infeasible, or if the board finds that the application of a compliance schedule in 9VAC5-40-21 is infeasible due to the nonavailability of necessary equipment or materials or other circumstances beyond the owner's control.
g. Nothing in this section shall prevent the owner of a source subject to a compliance schedule in 9VAC5-40-21 from submitting to the board a proposed alternative compliance schedule provided the following conditions are met:
(1) The proposed alternative compliance schedule is submitted within six months of the effective date of the emission standard;
(2) The final control plans for achieving compliance with the applicable emission standard are submitted simultaneously;
(3) The alternative compliance schedule contains the same increments of progress as the schedule for which it is proposed as an alternative; and
(4) Sufficient documentation is submitted by the owner of the source to justify the alternative dates proposed for the increments of progress.
h. All compliance schedules proposed or prescribed under this section shall provide for compliance with the applicable emission standards as expeditiously as practicable.
i. Any compliance schedule approved under this subsection may be revoked at any time if the source owner does not meet the stipulated increments of progress, and if the failure to meet an increment is likely to result in failure to meet the date for final compliance, and the failure to meet the increment is due to causes within the owner's control.
j. The provisions of 9VAC5-40-21 shall not apply to owners of sources which are in compliance with the applicable emission standard and for which the owners have determined and certified compliance to the satisfaction of the board within 12 months of the effective date of the applicable emission standard.
I. The following provisions apply with respect to stack heights:
1. The degree of emission limitation required of any source owner for control of any air pollutant shall not be affected in any manner by:
a. So much of the stack height of any source as exceeds good engineering practice; or
b. Any other dispersion technique.
2. The provisions of subdivision 1 of this subsection shall not apply to:
a. Stack heights in existence, or dispersion techniques implemented on or before December 31, 1970, except where pollutants are being emitted from such stacks or using such dispersion techniques by sources, as defined in § 111(a)(3) of the federal Clean Air Act, which were constructed, or reconstructed, or for which major modifications, as defined in Article 8 (9VAC5-80-1700 et seq.) and Article 9 (9VAC5-80-2000 et seq.) of Part II of 9VAC5 Chapter 80, were carried out after December 31, 1970; or
b. Coal-fired steam electric generating units subject to the provisions of § 118 of the federal Clean Air Act, which commenced operation before July 1, 1957, and whose stacks were constructed under a construction contract awarded before February 8, 1974.
3. Prior to the adoption of a new or revised emission limitation that is based on a good engineering practice stack height that exceeds the height allowed by subdivision 1 or 2 of the GEP definition, the board shall notify the public of the availability of the demonstration study and shall provide the opportunity for public hearing on it.
4. For purposes of this subsection, such height shall not exceed the height allowed by subdivision 1 or 2 of the GEP definition unless the owner demonstrates to the satisfaction of the board, after 30 days notice to the public and opportunity for public hearing, that a greater height is necessary as provided under subdivision 3 of the GEP definition.
5. In no event may the board prohibit any increase in any stack height or restrict in any manner the maximum stack height of any source.
6. Compliance with emission standards in this chapter shall not be affected in any manner by the stack height of any source or any other dispersion technique.
J. For the purpose of submitting compliance certifications or establishing whether or not a person has violated or is in violation of any standard in this chapter, nothing in this chapter shall preclude the use, including the exclusive use, of any credible evidence or information, relevant to whether a source would have been in compliance with applicable requirements if the appropriate emission or compliance test or procedure had been performed.
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from VR120-04-02, eff. July 1, 1986; amended, Virginia Register Volume 7, Issue 14, eff. July 1, 1991; Volume 18, Issue 21, eff. August 1, 2002; Volume 24, Issue 5, eff. December 12, 2007.
9VAC5-40-21. Compliance schedules.
A. The provisions of this section are a supplement to and shall be applied in context with the provisions of 9VAC5-40-20 H 2.
B. Compliance by process and emission control equipment installations.
1. Owners proposing to comply with an emission standard by the installation and operation of emission control equipment or replacement process equipment or both shall adhere to the increments of progress contained in the following schedule:
a. Final plans for the installation and operation of emission control equipment or process equipment or both shall be submitted within six months of the effective date of the applicable emission standard.
b. Contracts for the installation of emission control equipment or process equipment shall be awarded, or orders shall be issued for purchase of component parts to accomplish installation, within 16 months of the effective date of the applicable emission standard.
c. Initiation of on-site construction for the installation of the emission control equipment or process equipment or both shall begin within 22 months of the effective date of the applicable emission standard.
d. On-site construction or installation of the emission control equipment or process equipment or both shall be completed within 30 months of the effective date of the applicable emission standard.
e. Final compliance, determined in accordance with test methods acceptable to the board, shall be achieved within 32 months of the effective date of the applicable emission standard.
2. Owners of sources subject to the compliance schedule in subdivision 1 of this subsection shall certify to the board within five days after deadline for each increment of progress, whether the required increment of progress has been met.
C. Compliance by process equipment modification.
1. Owners proposing to comply with an emission standard by the modification of existing processing equipment shall adhere to the increments of progress contained in the following schedule.
a. Final plans for the process equipment modification shall be submitted within six months of the effective date of the applicable emission standard.
b. Contracts for the process equipment modification shall be awarded, or orders shall be issued for the purchase of component parts to accomplish the process equipment modification, within 15 months of the effective date of the applicable emission standard.
c. Initiation of on-site construction for the modification of the process equipment shall begin within 18 months of the effective date of the emission standard.
d. On-site construction or installation of process modifications shall be completed within 22 months of the effective date of the applicable emission standard.
e. Final compliance, determined in accordance with test methods acceptable to the board, shall be achieved within 24 months of the effective date of the applicable emission standard.
2. Owners of sources subject to the compliance schedule in subdivision 1 of the subsection shall certify to the board within five days after the deadline for each increment of progress, whether the required increment of progress has been met.
D. Compliance by use of process materials modification.
1. Except as provided under subdivision D 3 of this section, owners proposing to comply with an emission standard by the use of new process materials shall adhere to the increments of progress contained in the following schedule:
a. Final plans for the use of new process materials shall be submitted within six months of the effective date of the applicable emission standard.
b. Research and development of new process materials shall be completed within 18 months of the effective date of the applicable emission standard.
c. Evaluation of new process materials product quality and commercial acceptance shall be completed within 24 months of the effective date of the applicable emission standard.
d. Purchase orders shall be issued for new process materials and process modifications within 26 months of the effective date of the applicable emission standard.
e. Initiation of process modifications shall begin within 28 months of the effective date of the applicable emission standard.
f. Process modifications shall be completed and use of new process materials shall begin within 34 months of the effective date of the applicable emission standard.
g. Final compliance, determined in accordance with test methods acceptable to the board, shall be achieved within 36 months of the effective date of the applicable emission standard.
2. Owners of sources subject to the compliance schedule in subdivision D 1 of this section shall certify to the board within five days after the deadline for each increment of progress, whether the required increment of progress has been met.
3. Where the board determines that the use of new process materials has been sufficiently researched and developed for a particular application, owners proposing to comply with an emission standard by the use of new process materials shall adhere to the increments of progress contained in the following schedule:
a. Final plans for the use of new process materials shall be submitted within six months of the effective date of the applicable emission standard.
b. Evaluation of new process materials product quality and commercial acceptance shall be completed within 16 months of the effective date of the applicable emission standard.
c. Purchase orders shall be issued for new process materials and process modifications within 18 months of the effective date of the applicable emission standard.
d. Initiation of process modifications shall begin within 22 months of the effective date of the applicable emission standard.
e. Process modifications shall be completed and use of new process materials shall begin within 30 months of the effective date of the applicable emission standard.
f. Final compliance, determined in accordance with test methods acceptable to the board, shall be achieved within 32 months of the effective date of the applicable emission standard.
4. Owners of sources subject to the compliance schedule in subdivision D 3 of this section shall certify to the board within five days after deadline for each increment of progress, whether the required increment of progress has been met.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 13, Issue 18, eff. July 1, 1997.
9VAC5-40-22. Interpretation of emission standards based on process weight rate tables.
A. General. Unless otherwise approved by the board, interpretation of emission standards based on process weight rate tables shall be in accordance with this section.
B. Definitions.
1. For the purpose of these regulations and subsequent amendments of any orders issued by the board, the words or terms shall have the meaning given them in subdivision B 3 of this section.
2. As used in this section, all terms not defined here shall have the meaning given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
3. Terms defined.
"Manufacturing operation" means any process operation or combination of physically connected dissimilar process operations which is operated to effect physical or chemical changes, or both, in an article.
"Materials handling equipment" means any equipment used as a part of a process operation or combination of process operations which does not effect a physical or chemical change in the material or in an article, such as, but not limited to, conveyors, elevators, feeders or weighers.
"Physically connected" means any combination of process operations connected by materials handling equipment and designed for simultaneous complementary operation.
"Process operations" means any method, from, action, operation or treatment of manufacturing or processing, including any storage or handling of materials or products before, during or after manufacturing or processing.
"Process unit" means any step in a manufacturing or process operation which results in the emission of pollutants to the atmosphere.
"Process weight" means total weight of all materials introduced into any process unit which may cause any emission of pollutants. Process weight includes solid fuels charged, but does not include liquid and gaseous fuels charged or combustion air for all fuels.
"Process weight rate" means a rate established as follows:
(1) For continuous or long-run steady-state process operations, the total process weight for the entire period of continuous operation or for a typical portion of it, divided by the number of hours of such period or portion of it.
(2) For cyclical or batch process operations, the total weight for a period that covers a complete operation or an integral number of cycles, divided by the hours of actual process operation during such a period.
"Production rate" means the weight of final product obtained per hour of operation. If the rate of product going to storage can vary, the production rate shall be determined by calculation from the feed rates of raw material.
C. Interpretation of standards.
1. The total process weight rate for each individual process unit at a plant or premises shall be used for determining the maximum allowable emission rate of particulate that passes through a stack or stacks.
2. Unless otherwise specified, the allowable particulate mass emission rate shall be determined for individual units of equipment.
3. Unless otherwise specified or unless an equation is provided, the particulate emission limit above the maximum process weight rate shall be determined by linear interpolation. For interpolation between two values on a process weight rate table the following equation should be used:
| E = [EG - EL] | P - PL | + EL |
| PG - PL |
where: E = emission rate being calculated.
EL = emission rate for PL as determined from the process weight rate table.
EG = emission rate for PG as determined from the process weight rate table.
P = process weight rate of the unit.
PL = process weight rate in the process weight rate table which is closest to but less than the process weight rate of the unit.
PG = process weight rate listed in the process weight rate table which is closest to but greater than the process weight rate of the unit.
4. Where the nature of any process or design of any equipment is such as to permit more than one interpretation of a regulation, the interpretation that results in the minimum value for allowable emissions shall apply.
5. The following are examples that illustrate how the requirements apply to similar units manifolded to a common stack and a number of process units that are combined in a row. (For the purposes of this illustration an emission rate of 0.551 pounds per hour for a process weight rate of 100 pounds per hour was used.)
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 13, Issue 18, eff. July 1, 1997.
9VAC5-40-30. Emission testing.
A. Emission tests for existing sources shall be conducted and reported, and data shall be reduced as set forth in this chapter and in the appropriate reference methods unless the board (i) specifies or approves, in specific cases, the use of a reference method with minor changes in methodology; (ii) approves the use of an equivalent method; (iii) approves the use of an alternative method the results of which the board has determined to be adequate for indicating whether a specific source is in compliance; (iv) waives the requirement for emission tests because the owner of a source has demonstrated by other means to the board's satisfaction that the affected facility is in compliance with the standard; or (v) approves shorter sampling times and smaller sample volumes when necessitated by process variables or other factors. In cases where no appropriate reference method exists for an existing source subject to an emission standard for volatile organic compounds, the applicable test method in 9VAC5-20-121 may be considered appropriate.
B. Emission testing for existing sources shall be subject to testing guidelines approved by the board. Procedures may be adjusted or changed by the board to suit specific sampling conditions or needs based upon good practice, judgement and experience. When such tests are adjusted, consideration shall be given to the effect of such change on established emission standards. Tests shall be performed under the direction of persons whose qualifications are acceptable to the board.
C. Emission tests for existing sources shall be conducted under conditions which the board shall specify to the owner, based on representative performance of the source. The owner shall make available to the board such records as may be necessary to determine the conditions of the emission tests. Operations during periods of startup, shutdown and malfunction shall not constitute representative conditions for the purpose of an emission test. During the initial emission test, emissions in excess of the level of the applicable emission limit during periods of startup, shutdown, and malfunction shall not be considered a violation of the applicable emission limit unless otherwise specified in the applicable standard.
D. An owner may request that the board determine the opacity of emissions from an existing source during the emission tests required by this section.
E. Each emission test for an existing source shall consist of three separate runs using the applicable test method. Each run shall be conducted for the time and under the conditions acceptable to the board. For the purpose of determining compliance with an applicable standard, the arithmetic mean of the results of the three runs shall apply. In the event that a sample is accidentally lost, or if conditions occur in which one of the three runs must be discontinued because of forced shutdown, failure of an irreplaceable portion of the sample train, extreme meteorological conditions or other circumstances beyond the owner's control, compliance may, upon the approval of the board, be determined using the arithmetic mean of the results of the two other runs.
F. The board may test emissions of air pollutants from any existing source. Upon request of the board the owner shall provide, or cause to be provided, emission testing facilities as follows:
1. Sampling ports adequate for test methods applicable to such source. This includes (i) constructing the air pollution control system such that volumetric flow rates and pollutant emission rates can be accurately determined by applicable test methods and procedures and (ii) providing a stack or duct with acceptable flow characteristics during emission tests, as demonstrated by applicable test methods and procedures.
2. Safe sampling platforms.
3. Safe access to sampling platforms.
4. Utilities for sampling and testing equipment.
G. Upon request of the board the owner of any existing source subject to the provisions of this chapter shall conduct emission tests in accordance with procedures approved by the board.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-03, eff. July 1, 1991; amended, Virginia Register Volume 18, Issue 21, eff. August 1, 2002.
9VAC5-40-40. Monitoring.
A. Unless otherwise approved by the board, owners of existing sources specified in the applicable emission standard shall install, calibrate, maintain and operate systems for continuously monitoring and recording emissions of specified pollutants. However, nothing in this chapter shall exempt any owner from complying with subsection F of this section.
B. All continuous monitoring systems and monitoring devices shall be installed and operational by July 5, 1983. Verification of operational status shall, as a minimum, consist of the completion of the conditioning period specified by applicable requirements in Appendix B of 40 CFR Part 60.
C. Within 30 days after the date set forth in subsection B of this section and at such other times as may be requested by the board, the owner of any existing source shall conduct continuous monitoring system performance evaluations and furnish the board within 60 days of them two or, upon request, more copies of a written report of the results of such tests.
D. Unless otherwise approved by the board, all continuous monitoring systems required by subsection A of this section shall be installed, calibrated, maintained and operated in accordance with applicable requirements in this section, 9VAC5-40-41, and the applicable emission standard.
E. After receipt and consideration of written application, the board may approve alternatives to any monitoring procedures or requirements of this chapter including, but not limited to, the following:
1. Alternative monitoring requirements when installation of a continuous monitoring system or monitoring device specified by this chapter would not provide accurate measurements due to liquid water or other interferences caused by substances within the effluent gases.
2. Alternative monitoring requirements when the source is infrequently operated.
3. Alternative monitoring requirements to accommodate continuous monitoring systems that require additional measurements to correct for stack moisture conditions.
4. Alternative locations for installing continuous monitoring systems or monitoring devices when the owner can demonstrate the installation at alternate locations will enable accurate and representative measurements.
5. Alternative methods of converting pollutant concentration measurements to units of the standards.
6. Alternative procedures for computing emission averages that do not require integration of data (e.g., some facilities may demonstrate that the variability of their emissions is sufficiently small to allow accurate reduction of data based upon computing averages from equally spaced data points over the averaging period).
7. Alternative monitoring requirements when the effluent from a single source or the combined effluent from two or more sources are released to the atmosphere through more than one point.
8. Alternative procedures for performing calibration checks.
9. Alternative monitoring requirements when the requirements of this section would impose an extreme economic burden on the owner.
10. Alternative monitoring requirements when the continuous monitoring systems cannot be installed due to physical limitations at the source.
11. Alternative continuous monitoring systems that do not meet the design or performance requirements in Performance Specification 1 of Appendix B of 40 CFR Part 60, but which adequately demonstrate a definite and consistent relationship between its measurements and the measurements of opacity by a system complying with the requirements in Performance Specification 1 of Appendix B of 40 CFR Part 60. The board may require that such demonstration be performed for each source.
12. Alternative monitoring systems that meet the requirements of 40 CFR Part 75 (i) if a source is subject to 40 CFR Part 75 or (ii) if the board determines that the requirements of 40 CFR Part 75 are more appropriate for the source than the pertinent provisions of this chapter.
F. Upon request of the board, the owner of an existing source subject to the provisions of this chapter shall install, calibrate, maintain and operate equipment for continuously monitoring and recording emissions or process parameters or both in accordance with methods and procedures acceptable to the board.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-04, eff. July 1, 1991; amended, Virginia Register Volume 18, Issue 21, eff. August 1, 2002.
9VAC5-40-41. Emission monitoring procedures for existing sources.
A. The provisions of this section shall apply to existing sources. These provisions may also apply, at the discretion of the board, to new and modified sources if the source type is not subject to Article 5 (9VAC5-50-400 et seq.) of 9VAC5 Chapter 50.
B. General procedures.
1. Continuous monitoring system performance evaluations shall be conducted in accordance with the requirements and procedures contained in the applicable performance specification in Appendix B of 40 CFR Part 60 as follows:
a. Continuous monitoring systems for measuring opacity of emissions shall comply with performance specification 1.
b. Continuous monitoring systems for measuring nitrogen oxides emissions shall comply with performance specification 2.
c. Continuous monitoring systems for measuring sulfur dioxide emissions shall comply with performance specification 2.
d. Continuous monitoring systems for measuring oxygen content or carbon dioxide content of effluent gases shall comply with performance specification 3.
2. Owners of all continuous monitoring systems installed in accordance with the provisions of this section shall check the zero and span drift at least once daily in accordance with the method prescribed by the manufacturer of such systems unless the manufacturer recommends adjustments at shorter intervals, in which case such recommendations shall be followed. The zero and span shall, as a minimum, be adjusted whenever the 24-hour zero drift or 24-hour calibration drift limits of the applicable performance specifications in Appendix B of 40 CFR Part 60 are exceeded. For continuous monitoring systems measuring opacity of emissions, the optical surfaces exposed to the effluent gases shall be cleaned prior to performing the zero or span drift adjustment except that for systems using automatic zero adjustments, the optical surfaces shall be cleaned when the cumulative automatic zero compensation exceeds 4% opacity. Unless otherwise approved by the board, the following procedures, as applicable, shall be followed:
a. For extractive continuous monitoring systems measuring gases, minimum procedures shall include introducing applicable zero and span gas mixtures into the measurement system as near the probe as is practical. Span and zero gases certified by their manufacturer to be traceable to National Bureau of Standards reference gases shall be used whenever these reference gases are available. The span and zero gas mixtures shall be the same composition as specified in Appendix B of 40 CFR Part 60. Every six months from date of manufacturer, span and zero gases shall be reanalyzed by conducting triplicate analyses with Reference Methods 6 for SO2, 7 for NOX, and 3 for O2 and CO2, respectively. The gases may be analyzed at less frequent intervals if longer shelf lives are guaranteed by the manufacturer.
b. For nonextractive continuous monitoring systems measuring gases, minimum procedures shall include upscale checks using a certified calibration gas cell or test cell which is functionally equivalent to a known gas concentration. The zero check may be performed by computing the zero value from upscale measurements or by mechanically producing zero condition.
c. For continuous monitoring systems measuring opacity of emissions, minimum procedures shall include a method for producing a simulated zero opacity condition and an upscale (span) opacity condition using a certified neutral density filter or other related technique to produce a known obscuration of the light beam. Such procedures shall provide a system check of the analyzer internal optical surfaces and all electronic circuitry including the lamp and photodetector assembly.
3. Except for system breakdowns, repairs, calibration checks, and zero and span adjustments required under subdivision B 2 of this section, all continuous monitoring systems shall be in continuous operation and shall meet minimum frequency of operation requirements as follows:
a. All continuous monitoring systems for measuring opacity of emissions shall complete a minimum of one cycle of sampling and analyzing for each successive 15-second period and one cycle of data recording for each successive six-minute period.
b. All continuous monitoring systems for measuring nitrogen oxides, sulfur dioxide, carbon dioxide or oxygen shall complete a minimum of one cycle of operation (sampling, analyzing and data recording) for each successive 15-minute period.
4. All continuous monitoring systems or monitoring devices shall be installed such that representative measurements of emissions or process parameters from the affected facility are obtained. Additional procedures for location of continuous monitoring systems contained in the applicable performance specifications in Appendix B of 40 CFR Part 60 shall be used.
5. When the effluents from a single affected facility or two or more affected facilities subject to the same standards are combined before being released to the atmosphere, the owner may install applicable continuous monitoring systems on each effluent or on the combined effluent. When the affected facilities are not subject to the same standards, separate continuous monitoring systems shall be installed on each effluent. When the effluent from one affected facility is released to the atmosphere through more than one point, the owner shall install applicable continuous monitoring systems on each separate effluent unless the installation of fewer systems is approved by the board.
6. Owners of all continuous monitoring systems for measurement of opacity shall reduce all data to six-minute averages for six-minute periods and for systems other than opacity to one-hour averages for one-hour periods. Six-minute opacity averages shall be calculated from 24 or more data points spaced at approximately equal intervals over each six-minute period. For systems other than opacity, one-hour averages shall be computed from four or more date points spaced at approximately equal intervals over each one-hour period. Data recorded during periods of system breakdowns, repairs, calibration checks and zero and span adjustments shall not be included in the data averages computed under this subdivision. An arithmetic or integrated average of all data may be used. The data output of all continuous monitoring systems may be recorded in reduced or nonreduced form (e.g., ppm pollutant and percent O2 of lb or pollutant per million Btu). All excess emissions should be converted into units of the standard using the applicable conversion procedures specified in the applicable standard. After conversion into units of the standard, the data may be rounded to the same number of significant digits used to specify the applicable standard (e.g., rounded to the nearest one percent opacity).
C. Specific procedures. Specific procedures for emission monitoring may be found in the rule covering the source type in question.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 13, Issue 18, eff. July 1, 1997.
9VAC5-40-50. Notification, records and reporting.
A. Any owner of an existing source subject to the provisions of this chapter shall provide written notifications to the board of the following:
1. The date upon which demonstration of the continuous monitoring system performance begins in accordance with 9VAC5-40-40 C. Notification shall be postmarked or submitted electronically not less than 30 days prior to such date.
2. The date of any emission test the owner wishes the board to consider in determining compliance with a standard. Notification shall be postmarked or submitted electronically not less than 30 days prior to such date.
3. The anticipated date for conducting the opacity observations required by 9VAC5-40-20 G 1. The notification shall also include, if appropriate, a request for the board to provide a visible emissions reader during an emission test. The notification shall be postmarked or submitted electronically not less than 30 days prior to such date.
B. Any owner of an existing source subject to the provisions of 9VAC5-40-40 A shall maintain records of the occurrence and duration of any startup, shutdown or malfunction in the operation of such source; any malfunction of the air pollution control equipment; or any periods during which a continuous monitoring system or monitoring device is inoperative.
C. Each owner required to install a continuous monitoring system (CMS) or monitoring device shall submit a written report of excess emissions (as defined in the applicable emission standard) and either a monitoring systems performance report or a summary report form, or both, to the board semiannually, except when (i) more frequent reporting is specifically required by an applicable emission standard or the CMS data are to be used directly for compliance determination, in which case quarterly reports shall be submitted; or (ii) the board, on a case-by-case basis, determines that more frequent reporting is necessary to accurately assess the compliance status of the source. The summary report and form shall meet the requirements of 40 CFR 60.7(d). The frequency of reporting requirements may be reduced as provided in 40 CFR 60.7(e). All reports shall be postmarked or submitted electronically by the 30th day following the end of each calendar half (or quarter, as appropriate). Written reports of excess emissions shall include the following information:
1. The magnitude of excess emissions computed in accordance with 9VAC5-40-41 B 6, any conversion factors used, and the date and time of commencement and completion of each period of excess emissions. The process operating time during the reporting period.
2. Specific identification of each period of excess emissions that occurs during startups, shutdowns and malfunctions of the source. The nature and cause of any malfunction (if known), the corrective action taken or preventative measures adopted.
3. The date and time identifying each period during which the continuous monitoring system was inoperative except for zero and span checks and the nature of the system repairs or adjustments.
4. When no excess emissions have occurred or the continuous monitoring systems have not been inoperative, repaired or adjusted, such information shall be stated in the report.
D. Any owner of an existing source subject to the provisions of this chapter shall maintain a file of all measurements, including continuous monitoring system, monitoring device, and emission testing measurements; all continuous monitoring system performance evaluations; all continuous monitoring system or monitoring device calibration checks; adjustments and maintenance performed on these systems or devices; and all other information required by this chapter recorded in a permanent form suitable for inspection. The file shall be retained for at least two years (unless a longer period is specified in the applicable standards) following the date of such measurements, maintenance, reports and records.
E. Any data or information required by the Regulations for the Control and Abatement of Air Pollution, any permit or order of the board, or that the owner wishes the board to consider, to determine compliance with an emission standard shall be recorded or maintained in a timeframe consistent with the averaging period of the standard.
F. The owner of a stationary source shall keep records as may be necessary to determine its emissions. Any owner claiming that a facility is exempt from the provisions of the Regulations for the Control and Abatement of Air Pollution shall keep records as may be necessary to demonstrate to the satisfaction of the board its continued exempt status.
G. The owner of an existing source subject to any emission standard in Article 26 (9VAC5-40-3560 et seq.) through Article 36 (9VAC5-40-5060 et seq.) of 9VAC5-40 shall maintain records in accordance with the applicable procedure in 9VAC5-20-121.
H. Upon request of the board, the owner of an existing source subject to the provisions of this chapter shall provide notifications and report, revise reports, maintain records or report emission test or monitoring result in a manner and form and using procedures acceptable to board.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-05, eff. July 1, 1991; amended, Virginia Register Volume 18, Issue 21, eff. August 1, 2002; Volume 40, Issue 14, eff. April 11, 2024.
Part II
Emission Standards
Article 1
Visible Emissions and Fugitive Dust/Emissions (Rule 4‑1)
9VAC5-40-60. Applicability and designation of affected facility.
Article 1
Visible Emissions and Fugitive Dust/Emissions (Rule 4‑1)
A. The affected facilities to which the provisions of this article apply are the following:
1. Each source of visible emissions; and
2. Each source of fugitive dust/emissions.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0101, eff. January 1, 1985.
9VAC5-40-70. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words and terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Fugitive dust" means particulate matter composed of soil or other materials, or both, of natural origin. Fugitive dust may include emissions from haul roads, wind erosion of exposed surfaces and storage piles and other activities in which the material is either removed, stored, transported or redistributed.
"Fugitive emissions" means emissions which are generated by industrial or other activities and which do not pass through a stack, chimney, vent or other functionally equivalent opening, but which may escape from openings (such as windows, doors, ill-fitting closures or poorly maintained equipment) or material handling equipment.
"Opacity" means the degree to which emissions reduce the transmission of light and obscure the view of an object in the background, expressed as a percentage.
"Six-minute period" means any one of the 10 equal parts of one hour or a one-hour period, as may be applicable.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0102, eff. January 1, 1985.
9VAC5-40-80. Standard for visible emissions.
Unless specified otherwise in this part, no owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any visible emissions which exhibit greater than 20% opacity, except for one six-minute period in any one hour of not more than 60% opacity. Failure to meet the requirements of this section because of the presence of water vapor shall not be a violation of this section.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120‑04‑0103, eff. January 1, 1985.
9VAC5-40-90. Standard for fugitive dust/emissions.
No owner or other person shall cause or permit any materials or property to be handled, transported, stored, used, constructed, altered, repaired or demolished without taking reasonable precautions to prevent particulate matter from becoming airborne. Such reasonable precautions may include, but are not limited to, the following:
1. Use, where possible, of water or chemicals for control of dust in the demolition of existing buildings or structures, construction operations, the grading of roads or the clearing of land.
2. Application of asphalt, water, or suitable chemicals on dirt roads, materials stockpiles and other surfaces which may create airborne dust; the paving of roadways and maintaining them in a clean condition.
3. Installation and use of hoods, fans and fabric filters to enclose and vent the handling of dusty materials. Adequate containment methods shall be employed during sandblasting or other similar operations.
4. Open equipment for conveying or transporting materials likely to create objectionable air pollution when airborne shall be covered or treated in an equally effective manner at all times when in motion.
5. The prompt removal of spilled or tracked dirt or other materials from paved streets and of dried sediments resulting from soil erosion.
Statutory Authority
§ 10.1-1308 of the Code of Virginia and §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from VR120-04-0104, eff. January 1, 1985; amended, Virginia Register Volume 19, Issue 6, eff. February 1, 2003.
9VAC5-40-100. Monitoring.
A. Unless otherwise approved by the board, all continuous monitoring systems required by this article shall be installed, calibrated, maintained and operated in accordance with applicable requirements in 9VAC5-40-40 and 9VAC5-40-41.
B. Each owner required to install a continuous monitoring system shall provide notifications and reports and maintain records and monitoring results in accordance with the requirements of 9VAC5-40-50.
C. In cases where the requirements of 9VAC5-40-40 and 9VAC5-40-41 are not appropriate for a particular source type, the owner shall comply with other procedures acceptable to the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0105, eff. January 1, 1985.
9VAC5-40-110. Test methods and procedures.
The provisions of 9VAC5-40-20 A 2 apply to determine compliance with the standard prescribed in 9VAC5-40-80.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0106, eff. January 1, 1985.
9VAC5-40-120. Waivers.
A. A waiver from the opacity emission limitation in 9VAC5-40-80 may be granted by the director, provided that a technical decision is reached that the plume opacity observations made in accordance with 9VAC5-40-20 and 9VAC5-40-110 are not representative of the pollutant loading of the plume.
B. Upon granting the above waiver, the director shall require one or more alternate source surveillance methods, which may include, but are not limited to, the following:
1. Requiring the owner to install, calibrate, maintain and operate systems for continuously monitoring and recording emissions of specified pollutants in accordance with 9VAC5-40-40 and 9VAC5-40-100.
2. Requiring the owner to conduct, at specified intervals, emission tests for measuring emissions of specified pollutants in accordance with 9VAC5-40-30.
3. Establishing an opacity emission limitation for the facility based on a correlation between tests of visible and other specified pollutant emissions.
C. The waiver may be granted for an indefinite period of time; however, approval may be withdrawn by the director:
1. For failure to adhere to any terms or conditions of the waiver;
2. If the affected facility is found to be in violation of any applicable emission standard; or
3. For failure to conduct or adhere to any alternate source surveillance method required for waiver approval.
Statutory Authority
§ 10.1-1308 of the Code of Virginia and §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from VR120-04-0107, eff. January 1, 1985; amended, Virginia Register Volume 19, Issue 6, eff. February 1, 2003.
Article 2
Emission Standards for Odor (Rule 4‑2)
9VAC5-40-130. Applicability and designation of affected facility.
Article 2
Emission Standards for Odor (Rule 4‑2)
A. Except as provided in subsection C of this section, the affected facility to which the provisions of this article apply is each facility that emits odor.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
C. The provisions of this article do not apply to accidental or other infrequent emissions of odors.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120‑04‑0201, eff. January 1, 1985.
9VAC5-40-140. Standard for odor.
No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any emissions which cause an odor objectionable to individuals of ordinary sensibility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0203, eff. January 1, 1985.
9VAC5-40-150. Determination of violation.
A. The determination of objectionable odor shall be made after a thorough review of all data or evidence relating to the situation which may be obtained by an investigation directed by the board. As a part of the investigation, the board, at its discretion, may hold a public hearing in accordance with 9VAC5-20-40 A 1 to hear complaints. The investigation may also include use of an odor panel survey and other methods approved by the board, or both.
B. Upon determination that an odor violates 9VAC5-40-140 the owner shall use such measures as approved by the board for the economically and technologically feasible control of odorous emissions.
Article 3
Emission Standards for Toxic Pollutants (Rule 4-3) [Repealed]
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0204, eff. January 1, 1985.
Article 3
Emission Standards for Toxic Pollutants (Rule 4-3) [Repealed]
9VAC5-40-160. (Repealed.)
Article 3
Emission Standards for Toxic Pollutants (Rule 4-3) [Repealed]
Historical Notes
Derived from VR120-04-0301, eff. October 15, 1991; repealed, Virginia Register Volume 18, Issue 14, eff. May 1, 2002.
Article 4
Emission Standards for General Process Operations (Rule 4-4)
9VAC5-40-240. Applicability and designation of affected facility.
Article 4
Emission Standards for General Process Operations (Rule 4-4)
A. Except as provided in subsections C and D of this section, the affected facility to which the provisions of this article apply is each process operation, each process gas stream and each combustion installation.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
C. Exempted from the provisions of this article are the following:
1. Process operations with a process weight rate capacity less than 100 pounds per hour.
2. Any combustion unit using solid fuel with a maximum heat input of less than 350,000 Btu per hour.
3. Any combustion unit using liquid fuel with a maximum heat input of less than 1,000,000 Btu per hour.
4. Any combustion unit using gaseous fuel with a maximum heat input of less than 10,000,000 Btu per hour.
D. The provisions of this article do not apply to a particular pollutant from an affected facility if the affected facility is subject to other emission standards in this chapter covering the same pollutant.
Statutory Authority
§ 10.1-1308 of the Code of Virginia, §§ 110 and 182 of the Clean Air Act, and 40 CFR Part 51.
Historical Notes
Derived from VR120-04-0401, eff. January 1, 1985; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996; Volume 18, Issue 4, eff. January 1, 2002; Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-250. Definitions.
A. For the purpose of the Regulations for the Control and Abatement of Air Pollution and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined herein shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Combustion installation" means all combustion units within a stationary source in operation prior to October 5, 1979.
"Combustion unit" means any type of stationary equipment in which solid, liquid or gaseous fuels and refuse are burned, including, but not limited to, furnaces, ovens, and kilns.
"Heat input" means the total gross calorific value of all fuels burned.
"Manufacturing operation" means any process operation or combination of physically connected dissimilar process operations which is operated to effect physical or chemical changes or both in an article.
"Materials handling equipment" means any equipment used as a part of a process operation or combination of process operations which does not effect a physical or chemical change in the material or in an article, such as, but not limited to, conveyors, elevators, feeders or weighers.
"Physically connected" means any combination of process operations connected by materials handling equipment and designed for simultaneous complementary operation.
"Process operation" means any method, form, action, operation or treatment of manufacturing or processing, including any storage or handling of materials or products before, during or after manufacturing or processing.
"Process unit" means any step in a manufacturing or process operation which results in the emission of pollutants to the atmosphere.
"Process weight" means total weight of all materials introduced into any process unit which may cause any emission of pollutants. Process weight includes solid fuels charged, but does not include liquid and gaseous fuels charged or combustion air for all fuels.
"Process weight rate" means a rate established as follows:
a. For continuous or long-run steady-state process operations, the total process weight for the entire period of continuous operation or for a typical portion of it, divided by the number of hours of such period or portion of it.
b. For cyclical or batch process operations, the total weight for a period that covers a complete operation or an integral number of cycles, divided by the hours of actual process operation during such a period.
"Rated capacity" means, the capacity as stipulated in the purchase contract for the condition of 100% load, or such other capacities as mutually agreed to by the board and owner using good engineering judgment.
"Total capacity" means with reference to a combustion installation, the sum of the rated capacities (expressed as heat input) of all units of the installation which must be operated simultaneously under conditions of 100% use load.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from VR120-04-0402, eff. July 1, 1991; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996; Volume 18, Issue 4, eff. January 1, 2002; Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-260. Standard for particulate matter (AQCR 1-6).
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any process unit any particulate emissions in excess of the limits in Table 4-4A.
Process Weight Rate | Maximum Allowable Emission Rate | |
Lb/Hr | Tons/Hr | Lb/Hr |
100 | 0.05 | 0.551 |
200 | 0.10 | 0.877 |
400 | 0.20 | 1.40 |
600 | 0.30 | 1.83 |
800 | 0.40 | 2.22 |
1000 | 0.50 | 2.58 |
1500 | 0.75 | 3.38 |
2000 | 1.00 | 4.10 |
2500 | 1.25 | 4.76 |
3000 | 1.50 | 5.38 |
3500 | 1.75 | 5.96 |
4000 | 2.00 | 6.52 |
5000 | 2.50 | 7.58 |
6000 | 3.00 | 8.56 |
7000 | 3.50 | 9.49 |
8000 | 4.00 | 10.4 |
9000 | 4.50 | 11.2 |
10000 | 5.00 | 12.0 |
12000 | 6.00 | 13.6 |
16000 | 8.00 | 16.5 |
18000 | 9.00 | 17.9 |
20000 | 10.00 | 19.2 |
30000 | 15.00 | 25.2 |
40000 | 20.00 | 30.5 |
50000 | 25.00 | 35.4 |
60000 | 30.00 | 40.0 |
70000 | 35.00 | 41.3 |
80000 | 40.00 | 42.5 |
90000 | 45.00 | 43.6 |
100000 | 50.00 | 44.6 |
120000 | 60.00 | 46.3 |
140000 | 70.00 | 47.8 |
160000 | 80.00 | 49.1 |
200000 | 100.00 | 51.3 |
1000000 | 500.00 | 69.0 |
2000000 | 1000.00 | 77.6 |
6000000 | 3000.00 | 92.7 |
B. Except as provided in subsections C and D of this section, interpretation of the emission standard in subsection A of this section shall be in accordance with 9VAC5-40-22.
C. Interpolation of the data in Table 4-4A for process weight rates up to 60,000 lb/hr shall be accomplished by use of the following equation:
E = 4.10 P0.67
where:
E = emission rate in lb/hr.
P = process weight rate in tons/hr.
D. Interpolation and extrapolation of the data for process weight rates in excess of 60,000 lb/hr shall be accomplished by use of the following equation:
E = 55.0 P0.11 - 40
where:
E = emission rate in lb/hr.
P = process weight rate in tons/hr.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0403, eff. January 1, 1985.
9VAC5-40-270. Standard for particulate matter (AQCR 7).
A. Noncombustion process operations. No owner or other person shall cause or permit to be discharged into the atmosphere from any process unit any particulate emissions in excess of the limits in Table 4-4B.
TABLE 4-4B | ||
Process Weight Rate | Maximum Allowable Emission Rate | |
Lb/Hr | Tons/Hr | Lb/Hr |
100 | 0.050 | 0.46 |
150 | 0.075 | 0.66 |
200 | 0.100 | 0.85 |
250 | 0.125 | 1.03 |
300 | 0.150 | 1.20 |
350 | 0.175 | 1.35 |
400 | 0.200 | 1.50 |
450 | 0.225 | 1.63 |
500 | 0.250 | 1.77 |
550 | 0.275 | 1.85 |
600 | 0.300 | 2.01 |
650 | 0.325 | 2.12 |
700 | 0.350 | 2.24 |
750 | 0.375 | 2.34 |
800 | 0.400 | 2.43 |
850 | 0.425 | 2.53 |
900 | 0.450 | 2.62 |
950 | 0.475 | 2.72 |
1000 | 0.500 | 2.80 |
1100 | 0.55 | 2.97 |
1200 | 0.60 | 3.12 |
1300 | 0.65 | 3.26 |
1400 | 0.70 | 3.40 |
1500 | 0.75 | 3.54 |
1600 | 0.80 | 3.66 |
1700 | 0.85 | 3.79 |
1800 | 0.90 | 3.91 |
1900 | 0.95 | 4.03 |
2000 | 1.00 | 4.14 |
2100 | 1.05 | 4.24 |
2200 | 1.10 | 4.34 |
2300 | 1.15 | 4.44 |
2400 | 1.20 | 4.55 |
2500 | 1.25 | 4.64 |
2600 | 1.30 | 4.74 |
2700 | 1.35 | 4.84 |
2800 | 1.40 | 4.92 |
2900 | 1.45 | 5.02 |
3000 | 1.50 | 5.10 |
3100 | 1.55 | 5.18 |
3200 | 1.60 | 5.27 |
3300 | 1.65 | 5.36 |
3400 | 1.70 | 5.44 |
3500 | 1.75 | 5.52 |
3600 | 1.80 | 5.61 |
3700 | 1.85 | 5.69 |
3800 | 1.90 | 5.77 |
3900 | 1.95 | 5.85 |
4000 | 2.00 | 5.93 |
4100 | 2.05 | 6.01 |
4200 | 2.10 | 6.08 |
4300 | 2.15 | 6.15 |
4400 | 2.20 | 6.22 |
4500 | 2.25 | 6.30 |
4600 | 2.30 | 6.37 |
4700 | 2.35 | 6.45 |
4800 | 2.40 | 6.52 |
4900 | 2.45 | 6.60 |
5000 | 2.50 | 6.67 |
5500 | 2.75 | 7.03 |
6000 | 3.00 | 7.37 |
6500 | 3.25 | 7.71 |
7000 | 3.50 | 8.05 |
7500 | 3.75 | 8.39 |
8000 | 4.00 | 8.71 |
8500 | 4.25 | 9.03 |
9000 | 4.50 | 9.36 |
9500 | 4.75 | 9.67 |
10000 | 5.00 | 10.00 |
11000 | 5.50 | 10.63 |
12000 | 6.00 | 11.28 |
13000 | 6.50 | 11.89 |
14000 | 7.00 | 12.50 |
15000 | 7.50 | 13.13 |
16000 | 8.00 | 13.74 |
17000 | 8.50 | 14.36 |
18000 | 9.00 | 14.97 |
19000 | 9.50 | 15.58 |
20000 | 10.00 | 16.19 |
30000 | 15.00 | 22.22 |
40000 | 20.00 | 28.30 |
50000 | 25.00 | 34.30 |
60000 or more | 30.00 or more | 40.00 |
B. Combustion installations. Interpretation of the emission standard in subsection A of this section shall be in accordance with 9VAC5-40-22.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0404, eff. January 1, 1985.
9VAC5-40-280. Standard for sulfur dioxide.
A. Noncombustion process operations. No owner or other person shall cause or permit to be discharged into the atmosphere from any process operation any sulfur dioxide emissions in excess of an in-stack concentration of 2000 ppm by volume.
B. Combustion installations.
1. No owner or other person shall cause or permit to be discharged into the atmosphere from any combustion installation any sulfur dioxide emissions in excess of the following limits:
a. S = 2.64K (AQCR 1 through 6)
b. S = 1.06K (for liquid or gaseous fuels - AQCR 7)
c. S = 1.52K (for solid fuels - AQCR 7)
where:
S = allowable emission of sulfur dioxide
expressed in lbs/hr.
K = actual heat input at total capacity expressed in Btu X 106 per hour.
2. Where there is more than one unit in a combustion installation and where the installation can be shown, to the satisfaction of the board, to be in compliance when the installation is operating at total capacity, the installation will be deemed to still be in compliance when the installation is operated at reduced load or one or more units are shut down for maintenance or repair, provided that the same type of fuel with the same sulfur content, or an equivalent, is continued in use.
3. For installations in AQCR 7 at which different fossil fuels are burned simultaneously, whether in the same or different units, the allowable emissions shall be determined by proration using the following formula:
| PS = K | X(1.06) + Y(1.52) |
| X + Y |
where:
PS = prorated allowable emissions of sulfur dioxide expressed in lb/hr.
X = percentage of actual heat input at total capacity derived from liquid or gaseous fuel.
Y = percentage of actual heat input at total capacity derived from solid fuels.
K = actual heat input at total capacity expressed in Btu X 106 per hour.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0405, eff. January 1, 1985.
9VAC5-40-290. Standard for hydrogen sulfide.
No owner or other person shall cause or permit to be discharged into the atmosphere from any process gas stream any hydrogen sulfide emissions in excess of a concentration greater than 15 grains per 100 cubic feet of gas without burning or removing H2S in excess of this concentration, provided that SO2 emissions in the burning operation meet the requirements of 9VAC5-40-280 A.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0406, eff. January 1, 1985.
9VAC5-40-300. (Repealed.)
Historical Notes
Derived from VR120-04-0407, eff. July 1, 1991, VR120-04-0408, eff. July 1, 1991 or Virginia Register Volume 13, Issue 18, eff. July 1, 1997; amended, Virginia Register Volume 9, Issue 5, eff. January 1, 1993; Volume 12, Issue 11, eff. April 1, 1996; Volume 18, Issue 4, eff. January 1, 2002; Volume 19, Issue 17, eff. June 4, 2003; Volume 20, Issue 12, eff. March 24, 2004; Errata 20:15 VA.R. 1498-1504 April 5, 2004; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; repealed, Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-320. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0409, eff. January 1, 1985.
9VAC5-40-330. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0410, eff. January 1, 1985.
9VAC5-40-340. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0411, eff. January 1, 1985.
9VAC5-40-350. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0412, eff. January 1, 1985.
9VAC5-40-360. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0413, eff. January 1, 1985.
9VAC5-40-370. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0414, eff. January 1, 1985.
9VAC5-40-380. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0415, eff. January 1, 1985.
9VAC5-40-390. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0416, eff. January 1, 1985.
9VAC5-40-400. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0417, eff. January 1, 1985.
9VAC5-40-410. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0418, eff. January 1, 1985.
9VAC5-40-420. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0419, eff. January 1, 1985; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
Article 5
Emission Standards for Synthesized Pharmaceutical Products Manufacturing Operations (Rule 4-5)
9VAC5-40-430. Applicability and designation of affected facility.
Article 5
Emission Standards for Synthesized Pharmaceutical Products Manufacturing Operations (Rule 4-5)
A. The affected facility to which the provisions of this article apply is each process unit or operation.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0501, eff. July 1, 1991.
9VAC5-40-440. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Condenser" means a device which removes condensable vapors by a reduction in the temperature of the captured gases.
"Production equipment exhaust system" means a device for collecting and directing out of the work area volatile organic compound fugitive emissions from reactor openings, centrifuge openings and other vessel openings for the purpose of protecting workers from excessive volatile organic compound exposure.
"Reactor" means a vessel designed to carry out chemical reactions under controlled conditions.
"Synthesized pharmaceutical products manufacturing" means manufacture of pharmaceutical products by chemical synthesis.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0502, eff. January 1, 1985.
9VAC5-40-450. Standard for volatile organic compounds.
A. Reactors, distillation operations, crystallizers, centrifuges and vacuum dryers.
1. No owner or other person shall use or permit the use of any reactor, distillation operation, crystallizer, centrifuge or vacuum dryer process unit unless such unit is equipped with a vapor control system that will remove, destroy or prevent the discharge into the atmosphere of at least 90% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subsection A 1 of this section by use of methods in 9VAC5-40-460 A and E will be acceptable to the board.
B. Air dryers and production equipment exhaust systems.
1. No owner or other person shall use or permit the use of any air dryer or production equipment exhaust system process unit unless such unit is equipped with a vapor control system that will remove, destroy or prevent the discharge into the atmosphere of at least 90% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subsection B 1 of this section by use of methods in 9VAC5-40-460 B and E will be acceptable to the board.
C. Filling of storage tanks.
1. No owner or other person shall use or permit the use of any stationary storage tank of more than 2,000 gallons capacity for storage of any volatile organic compound unless such tank is equipped with a vapor control system that will remove, destroy or prevent the discharge into the atmosphere of at least 90% by weight of volatile organic compound emissions during the filling of such tank.
2. Achievement of the emission standard in subsection C 1 of this section by use of the methods in 9VAC5-40-460 C and E will be acceptable to the board.
3. The provisions of subsection C of this section shall not be applicable to facilities using volatile organic compounds with a vapor pressure less than 4.1 pounds per square inch absolute at 68°F.
D. Volatile organic compound storage.
1. No owner or other person shall use or permit the use of any tank for storage of volatile organic compounds, unless such tank is equipped with a vapor control system which will remove, destroy or prevent the discharge into the atmosphere of at least 90% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subsection D 1 of this section by use of control methods in 9VAC5-40-460 D and E will be acceptable to the board.
3. The provisions of subsection D of this section shall not be applicable to facilities using volatile organic compounds with a vapor pressure less than 1.5 pounds per square inch absolute at 68°F.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0503, eff. July 1, 1991.
9VAC5-40-460. Control technology guidelines.
A. Reactors, distillation operations, crystallizers, centrifuges and vacuum dryers. The control system should consist of one of the following:
1. Surface condensation system with an outlet temperature not greater than:
a. -13°F when condensing volatile organic compounds of vapor pressure greater than 5.8 psi;
b. 5°F when condensing volatile organic compounds of vapor pressure greater than 2.9 psi;
c. 32°F when condensing volatile organic compounds of vapor pressure greater than 1.5 psi;
d. 50°F when condensing volatile organic compounds of vapor pressure greater than 1.0 psi; or
e. 77°F when condensing volatile organic compounds of vapor pressure greater than 0.5 psi.
2. Any system of equal or greater control efficiency when compared to the standard in 9VAC5-40-450 A 1, provided such system is approved by the board.
B. Air dryers and production equipment exhaust systems. The control system should consist of one of the following:
1. Condensation system.
2. Wet scrubbing system.
3. Carbon adsorption system.
4. Incineration.
5. Any system of equal or greater control efficiency when compared to the standard in 9VAC5-40-450 B 1, provided such system is approved by the board.
C. Filling of storage tanks. The tank should be a pressure tank maintaining working pressure sufficient at all times to prevent vapor loss to the atmosphere, or be designed and equipped with one of the following vapor control systems:
1. A submerged fill pipe.
2. A vapor control system with the vapor recovery portion consisting of one of the following:
a. A vapor tight return line from the storage container to the tank truck which shall be connected before liquids are transferred into the container.
b. Any adsorption system or condensation system.
3. A vapor control system with the vapor balance portion meeting the following criteria:
a. There should be no leaks in the tank trucks' pressure vacuum relief valves and hatch covers, nor truck tanks, storage tanks and associated vapor return lines during loading or unloading operations.
b. The pressure relief valves on storage containers and tank trucks should be set to release at no less than 0.7 psi or the highest possible pressure in accordance with the following National Fire Prevention Association Standards: "Standard for Tank Vehicles for Flammable and Combustible Liquids," "Flammable and Combustible Liquids Code, "Code for Motor Fuel Dispensing Facilities and Repair Garages" (see 9VAC5-20-21).
c. Pressure in the vapor collection lines should not exceed tank truck pressure relief valve settings.
d. All loading and vapor lines should be equipped with fittings which make vapor tight connections and which close when disconnected.
4. Any system of equal or greater control efficiency when compared to the standard in 9VAC5-40-450 C 1, provided such system is approved by the board.
D. Volatile organic compound storage.
1. The tank should be a pressure tank maintaining working pressure sufficient at all times to prevent vapor loss to the atmosphere, or be designed and equipped with one of the following vapor control systems:
a. Use of pressure/vacuum conservation vent set at + or %68 .030 psi.
b. Vent condensation system.
c. Carbon adsorption system.
d. An internal floating roof resting on the surface of the liquid contents and equipped with a closure seal, or seals, to close the space between the roof edge and tank shell. All tank gauging and sampling devices should be vapor tight except when gauging or sampling is taking place.
e. Any system of equal or greater control efficiency when compared to the standard in 9VAC5-40-450 D 1, provided such system is approved by the board.
2. There should be no visible holes, tears or other openings in the seal or any seal fabric.
3. All openings, except stub drains, should be equipped with a cover, seal or lid. The cover, seal or lid should be in a closed position at all times except when the device is in actual use. Automatic bleeder vents should be closed at all times except when the roof is floated off or landed on the roof leg supports. Rim vents, if provided, should be set to open when the roof is being floated off the roof leg supports or at the manufacturer's recommended setting.
4. The exterior aboveground surfaces (exposed to sunlight) should be painted white, light pastels or light metallic and such exterior paint should be periodically maintained in good condition. Repainting may be performed during normal maintenance periods.
E. General.
1. All centrifuges containing volatile organic compounds, rotary vacuum filters processing liquids containing volatile organic compounds and any other filters having an exposed liquid surface where the liquid contains volatile organic compounds should be enclosed. This applies to liquids exerting a total volatile organic compound vapor pressure of 0.5 psi or more at 68°F.
2. All in-process tanks should have covers. Covers should be closed when possible.
3. For liquids containing volatile organic compounds, all leaks in which liquids can be observed to be running or dripping from vessels and equipment (for example: pumps, valves, flanges) should be repaired as soon as is practical.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0504, eff. July 1, 1991; amended, Virginia Register Volume 18, Issue 7, eff. February 1, 2002.
9VAC5-40-470. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0505, eff. January 1, 1985.
9VAC5-40-480. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0506, eff. January 1, 1985.
9VAC5-40-490. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0507, eff. January 1, 1985.
9VAC5-40-500. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0508, eff. January 1, 1985.
9VAC5-40-510. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0509, eff. January 1, 1985.
9VAC5-40-520. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0510, eff. January 1, 1985.
9VAC5-40-530. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0511, eff. January 1, 1985.
9VAC5-40-540. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0512, eff. January 1, 1985.
9VAC5-40-550. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0513, eff. January 1, 1985.
9VAC5-40-560. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0514, eff. January 1, 1985.
9VAC5-40-570. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0515, eff. January 1, 1985.
Article 6
Emission Standards for Rubber Tire Manufacturing Operations (Rule 4-6)
9VAC5-40-580. Applicability and designation of affected facility.
Article 6
Emission Standards for Rubber Tire Manufacturing Operations (Rule 4-6)
A. The affected facility to which the provisions of this article apply is each process unit or operation.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0601, eff. July 1, 1991.
9VAC5-40-590. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Bead dipping" means the dipping of an assembled tire bead into a solvent based cement.
"Green tires" means assembled tires before molding and curing have occurred.
"Green tire spraying" means the spraying of green tires, both inside and outside, with release compounds which help remove air from the tire during molding and prevent the tire from sticking to the mold after curing.
"Pneumatic rubber tire manufacture" means the production of passenger car tires, light and medium truck tires, and other tires manufactured on assembly lines using automated equipment.
"Tread end cementing" means the application of a solvent based cement to the tire tread ends.
"Undertread cementing" means the application of a solvent based cement to the underside of a tire tread.
"Water based sprays" means release compounds, sprayed on the inside and outside of green tires, in which solids, water and emulsifiers have been substituted for all organic solvents.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0602, eff. January 1, 1985.
9VAC5-40-600. Standard for volatile organic compounds.
A. Undertread cementing.
1. No owner or other person shall use or permit the use of any undertread cementing process unit unless such unit is equipped with a vapor control system that will remove, destroy or prevent the discharge into the atmosphere of at least 85% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subsection A 1 of this section by use of methods in 9VAC5-40-610 A will be acceptable to the board.
B. Tread end cementing.
1. No owner or other person shall use or permit the use of any tread end cementing process unit unless such unit is equipped with a vapor control system that will remove, destroy or prevent the discharge into the atmosphere of at least 85% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subsection B 1 of this section by use of methods in 9VAC5-40-610 A will be acceptable to the board.
C. Bead dipping.
1. No owner or other person shall use or permit the use of any bead dipping process unit unless such unit is equipped with a vapor control system that will remove, destroy or prevent the discharge into the atmosphere of at least 85% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subsection C 1 of this section by use of methods in 9VAC5-40-610 A will be acceptable to the board.
D. Green tire spraying.
1. No owner or other person shall use or permit the use of any green tire spraying operation unless such vapor control methods are applied that will remove, destroy or prevent the discharge into the atmosphere of at least 95% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subsection D 1 of this section by use of methods in 9VAC5-40-610 B will be acceptable to the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0603, eff. July 1, 1991.
9VAC5-40-610. Control technology guidelines.
A. Undertread cementing, tread end cementing and bead dipping. The control system should consist of one of the following:
1. Carbon adsorption system.
2. Incineration system.
3. Any system of equal or greater control efficiency when compared to the standard in 9VAC5-40-600 A 1, B 1, or C 1 as applicable, provided such system is approved by the board.
B. Green tire spraying. The control method should consist of one of the following:
1. Use of water based sprays;
2. Carbon adsorption;
3. Incineration; or
4. Any method of equal or greater control efficiency when compared to the standard in 9VAC5-40-600 D 1, of this section, provided such method is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0604, eff. July 1, 1991.
9VAC5-40-620. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0605, eff. January 1, 1985.
9VAC5-40-630. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0606, eff. January 1, 1985.
9VAC5-40-640. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0607, eff. January 1, 1985.
9VAC5-40-650. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0608, eff. January 1, 1985.
9VAC5-40-660. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0609, eff. January 1, 1985.
9VAC5-40-670. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0610, eff. January 1, 1985.
9VAC5-40-680. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0611, eff. January 1, 1985.
9VAC5-40-690. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0612, eff. January 1, 1985.
9VAC5-40-700. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0613, eff. January 1, 1985.
9VAC5-40-710. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0614, eff. January 1, 1985.
9VAC5-40-720. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0615, eff. January 1, 1985.
Article 7
Emission Standards for Incinerators (Rule 4-7)
9VAC5-40-730. Applicability and designation of affected facility.
Article 7
Emission Standards for Incinerators (Rule 4-7)
A. The affected facility to which the provisions of this article apply is each incinerator.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
C. The provisions of this article do not apply to facilities that are designed as boilers to produce steam or heated water and are designed to burn either fossil fuel or refuse derived fuel. It does apply to such facilities if designed to burn raw refuse.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0701, eff. January 1, 1985.
9VAC5-40-740. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Incinerator" means any furnace or device used in the process of burning waste for the primary purpose of destroying matter or reducing the volume, or both, of the waste by removing combustible matter.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0702, eff. January 1, 1985.
9VAC5-40-750. Standard for particulate matter.
No owner or other person shall cause or permit to be discharged into the atmosphere from any incinerator any particulate emissions in excess of .14 grains per standard cubic foot of dry flue gas corrected to 12% carbon dioxide (without the contribution of auxiliary fuel).
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0703, eff. January 1, 1985.
9VAC5-40-760. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0704, eff. January 1, 1985.
9VAC5-40-770. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0705, eff. January 1, 1985.
9VAC5-40-780. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0706, eff. January 1, 1985.
9VAC5-40-790. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0707, eff. January 1, 1985.
9VAC5-40-800. Prohibition of flue-fed incinerators.
Incinerators which use the same flue for feeding the refuse and discharging the gases of combustion are prohibited.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0708, eff. January 1, 1985.
9VAC5-40-810. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0709, eff. January 1, 1985.
9VAC5-40-820. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0710, eff. January 1, 1985.
9VAC5-40-830. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0711, eff. January 1, 1985.
9VAC5-40-840. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0712, eff. January 1, 1985.
9VAC5-40-850. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0713, eff. January 1, 1985.
9VAC5-40-860. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0714, eff. January 1, 1985.
9VAC5-40-870. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0715, eff. January 1, 1985.
Article 8
Emission Standards for Fuel Burning Equipment (Rule 4-8)
9VAC5-40-880. Applicability and designation of affected facility.
Article 8
Emission Standards for Fuel Burning Equipment (Rule 4-8)
A. Except as provided in subsections C, D, and E of this section, the affected facility to which provisions of this article apply is fuel burning equipment.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
C. Exempted from the provisions of this article are the following:
1. Any fuel burning equipment unit using solid fuel with a maximum heat input of less than 350,000 Btu per hour.
2. Any fuel burning equipment unit using liquid fuel (exclusive of coal slurry mixtures) with a maximum input of less than 1,000,000 Btu per hour.
3. Any fuel burning equipment unit using gaseous fuel with a maximum heat input of less than 10,000,000 Btu per hour.
D. The provisions of this article do not apply to fuel burning equipment units that power mobile sources but are removed for maintenance or repair and testing.
E. The provisions of this article do not apply to stationary internal combustion engines.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0801, eff. January 1, 1985; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999.
9VAC5-40-890. Definitions.
A. For the purpose of the Regulations for the Control and Abatement of Air Pollution and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Capacity factor" means the ratio of the average load on a machine or equipment for the period of time considered to the capacity rating of the machine or equipment.
"Fossil-fuel fired steam generator" means furnace or boiler, or both, used in the process of burning fossil fuel for the primary purpose of providing steam by heat transfer.
"Fuel burning equipment" means any furnace, with fuel burning equipment appurtenances thereto, used in the process of burning fuel for the primary purpose of producing heat to be utilized by indirect heat transfer, or by indirect production of power. This includes facilities that are designed as boilers to produce steam or heated water and are designed to burn either fossil fuel or refuse derived fuel. It does not include such facilities if designed primarily to burn raw refuse. This includes fuel burning equipment units (both permanently installed units and portable units) used to replace the power used by mobile sources. For the purposes of this article, stationary combustion turbines are considered to be fuel burning equipment.
"Fuel burning equipment installation" means all fuel burning equipment units within a stationary source in operation prior to October 5, 1979.
"Heat input" means the total gross calorific value of all fuels burned.
"Rated capacity" means the capacity as stipulated in the purchase contract for the condition of 100% load, or such other capacities as mutually agreed to by the board and owner using good engineering judgment.
"Refuse derived fuel (RDF)" means fuel produced from solid or liquid waste (includes materials customarily referred to as refuse and other discarded materials), or both, which has been segregated and classified, with the useable portions being put through a size reduction and classification process which results in a relatively homogeneous mixture.
"Stationary combustion turbine" means any air-breathing internal combustion engine consisting of an air compressor, combustion chamber, and a turbine wheel.
"Stationary internal combustion engine" means an engine in which fuel is burned within a machine in which energy is converted directly into mechanical motion or work. The energy is used directly for the production of power, locomotion or work. Internal combustion engines include, but are not limited to, diesel engines, gasoline engines, and diesel pumps. For the purposes of this article, stationary combustion turbines are not considered to be stationary internal combustion engines.
"Total capacity" means with reference to a fuel burning equipment installation, the sum of the rated capacities (expressed as heat input) of all units of the installation which must be operated simultaneously under conditions of 100% use load.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0802, eff. January 1, 1985; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999; Volume 18, Issue 4, eff. January 1, 2002.
9VAC5-40-900. Standard for particulate matter.
A. Fuel burning equipment installations.
No owner or other person shall cause or permit to be discharged into the atmosphere from any fuel burning equipment installation any gaseous products of combustion containing particulate emissions in excess of the following limits.
1. In AQCR 1 through 6.
a. For fuel burning equipment installations with total capacity less than 10 million (10 X 106) Btu per hour, the maximum allowable emission ratio shall be 0.6 pounds of particulate per million Btu input.
b. For fuel burning equipment installations with total capacity between 10 million (10 X 106) and 10 billion (10,000 X 106) Btu per hour, the maximum allowable emission ration, E, in pounds of particulate per million Btu input, shall be determined by the following equation: E = 1.0906H-0.2594, where H is the total capacity in millions of Btu per hour.
c. For fuel burning equipment installations with total capacity in excess of 10 billion (10,000 X 106) Btu per hour, the maximum allowable emission ratio shall be 0.1 pounds of particulate per million Btu input.
2. In AQCR 7.
a. For fuel burning equipment installations with total capacity less than 100 million (100 X 106) Btu per hour, the maximum allowable emission ratio shall be 0.3 pounds of particulate per million Btu input.
b. For fuel burning equipment installations with total capacity between 100 million (100 X 106) and 10 billion (10,000 X 106) Btu per hour, the maximum allowable emission ratio, E, in pounds of particulate per million Btu input, shall be determined by the following equation: E = .9000H-0.2386, where H is the total capacity in millions of Btu per hour.
c. For fuel burning equipment installations with total capacity in excess of 10 billion (10,000 X 106) Btu per hour, the maximum allowable emission ratio shall be 0.1 pounds of particulate per million Btu input.
B. Fuel burning equipment units.
1. The maximum allowable particulate emissions for each fuel burning equipment unit shall be the product of the rated capacity and the emission ratio (determined in accordance with subsection A of this section).
2. The allowable particulate emissions for each fuel burning equipment unit when operating at less than rated capacity shall be the product of the emission ratio, actual heat input and efficiency factor for the collection equipment. The efficiency factor for the collection equipment of each unit shall be determined using procedures set forth in 9VAC5-40-920.
3. For fuel burning equipment installations consisting of multiple fuel burning equipment units, except where all of the units burn liquid or gaseous fuels, or both, exclusively, the maximum allowable particulate emissions for each unit may be determined as provided in 9VAC5-40-910.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0803, eff. January 1, 1985; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999.
9VAC5-40-910. Emission allocation system.
A. This section applies only to fuel burning equipment installations consisting of multiple fuel burning equipment units which do not burn liquid or gaseous fuels, or both, exclusively.
B. The maximum allowable particulate emissions for a fuel burning equipment installation shall be the product of the total capacity and the emission ratio (determined in accordance with 9VAC5-40-900 A).
C. The allowable particulate emissions for a fuel burning equipment installation when operating at less than total capacity, shall be the product of the percent load, emission allocation and efficiency factor for the collection equipment. The percent load shall be the quotient of the actual load and the rated capacity. The efficiency factor for the collection equipment of each unit shall be determined using procedures set forth in 9VAC5-40-920. The emission allocation shall be determined using procedures set forth in subsection D of this section.
D. The emission allocation for each of the fuel burning equipment units of the fuel burning equipment installation shall be its designated portion of the maximum allowable particulate emissions from the fuel burning equipment installation when operating at total capacity. The portions shall be proposed by the owner initially and determined in a manner mutually acceptable to the board and the owner. Once accepted by the board, the portions may not be changed without the consent of the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0804, eff. January 1, 1985.
9VAC5-40-920. Determination of collection equipment efficiency factor.
The efficiency factor for the collection equipment shall be established as follows:
1. For all collection equipment, except mechanical collectors, the efficiency factor shall be 1.0.
2. For mechanical collectors, the efficiency factor shall be the quotient of the design efficiency of the collector at rated capacity and the actual efficiency of the collector at the reduced actual load. The actual efficiency shall be the product of the design efficiency and the correction factor where:
| Correction Factor = | 1 + log10 (actual load) |
| 1 + log10 (rated capacity) |
3. For collection equipment where the owner does not wish to accept the efficiency factor established by subdivision 1 or 2 of this section, the owner may provide information and data as a substitute. Such information and data may be emissions test results or other conclusive evidence. If such information and data is found acceptable by the board, it may be used to establish the efficiency factor for the collection equipment.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0805, eff. January 1, 1985.
9VAC5-40-930. Standard for sulfur dioxide.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any fuel burning equipment installation any sulfur dioxide emissions in excess of the following limits:
1. S = 2.64K (AQCR 1 through 6).
2. S = 1.06K (for liquid or gaseous fuels - AQCR 7).
3. S = 1.52K (for solid fuels - AQCR 7).
where:
S = allowable emission of sulfur dioxide expressed in pounds per hour.
K = heat input at total capacity expressed in Btu X 106 per hour.
B. Where there is one or more units in a fuel burning equipment installation and where the installation can be shown, to the satisfaction of the board, to be in compliance when the installation is operating at total capacity, the installation will be deemed to still be in compliance when the installation is operated at reduced load or one or more units are shut down for maintenance or repair, provided that the same type of fuel with the same sulfur content, or an equivalent, is continued in use.
C. For installations in AQCR 7 at which different fossil fuels are burned simultaneously, whether in the same or different units, the allowable emissions shall be determined by proration using the following formula:
where
PS = prorated allowable emissions of sulfur dioxide expressed in pounds per hour.
X = percentage of heat input at total capacity derived from liquid or gaseous fuel.
Y = percentage of heat input at total capacity derived from solid fuels.
K = heat input at total capacity expressed in Btu x 106 per hour.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0806, eff. January 1, 1985.
9VAC5-40-940. Standard for visible emissions.
A. The provisions of Article 1 (9VAC5-40-60 et seq.) of this part (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply except that the provisions in subsection B of this section apply instead of 9VAC5-40-80 A.
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any fuel burning equipment unit any visible emissions which exhibit greater than 20% opacity, except for one, six-minute period in any one hour of not more than 60% opacity. Failure to meet the requirements of this section because of the presence of water vapor shall not be a violation of this section.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0807, eff. January 1, 1985; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999.
9VAC5-40-950. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0808, eff. January 1, 1985.
9VAC5-40-960. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0809, eff. January 1, 1985.
9VAC5-40-970. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0810, eff. January 1, 1985.
9VAC5-40-980. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0811, eff. January 1, 1985.
9VAC5-40-990. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0812, eff. January 1, 1985.
9VAC5-40-1000. Monitoring.
A. The provisions of 9VAC5-40-40 (Monitoring) apply.
B. Unless otherwise approved by the board, owners of fossil-fuel fired steam generators specified in subsection C of this section shall install, calibrate, maintain and operate systems for continuously monitoring and recording specified emissions in accordance with 9VAC5-40-40 and 9VAC5-40-41.
C. Fossil-fuel fired steam generators of greater than 250 million Btu per hour maximum heat input with an annual average capacity factor of greater than 30% (as reported to the Federal Power Commission for calendar year 1974, or as otherwise demonstrated to the board by the owner) shall be monitored for opacity except where:
1. Gaseous fuel is the only fuel burned, or
2. Oil or a mixture of gas and oil are the only fuels burned and the facility is able to comply with applicable particulate matter and visible emission standards without utilization of particulate matter collection equipment, and where the facility has never been found, through any administrative or judicial proceedings, to be in violation of any visible emission standard.
D. The continuous monitoring system shall be spanned at 80, 90 or 100% opacity.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0813, eff. January 1, 1985.
9VAC5-40-1010. Notification, records and reporting.
A. The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
B. For the purpose of reports required under 9VAC5-40-50 C periods of excess emissions that shall be reported are defined as any one-hour period during which there are two or more six-minute periods when the average opacity exceeds 20%.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0814, eff. January 1, 1985.
9VAC5-40-1020. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0815, eff. January 1, 1985.
9VAC5-40-1030. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0816, eff. January 1, 1985.
9VAC5-40-1040. Permits.
A permit may be required prior to beginning any of the activities specified below if the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0817, eff. January 1, 1985; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999.
Article 9
Emission Standards for Coke Ovens (Rule 4-9)
9VAC5-40-1050. Applicability and designation of affected facility.
Article 9
Emission Standards for Coke Ovens (Rule 4-9)
A. The affected facilities in coke plants to which the provisions of this article apply are: horizontal slot sole-flue nonrecovery ovens and horizontal slot nonrecovery ovens.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0901, eff. January 1, 1985.
9VAC5-40-1060. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Charging" means the process by which coal is introduced into a coke oven beginning when coal enters the oven and ending when the door is closed.
"Coking" means the process by which coal is converted to coke by means of destructive distillation using heat.
"Pushing" means the process by which coke is removed from a coke oven, including the period marked by the time when the doors are first removed from a coke oven until quench water is applied to the hot coke.
"Quenching" means the process by which the combustion of hot coke is stopped by application of water or any other procedure achieving the same affect.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0902, eff. January 1, 1985.
9VAC5-40-1070. Standard for particulate matter.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any horizontal slot sole-flue nonrecovery oven any particulate emissions from coking, charging and pushing operations in excess of a combined total of 0.15 pounds of particulate/hour/ton of coal, as charged.
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any horizontal slot nonrecovery oven any particulate emissions from coking, charging and pushing operations in excess of a combined total of 0.13 pounds of particulate/hour/ton of coal, as charged.
C. No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility during the quenching operation any particulate emissions in excess of that resultant from use of a quench tower incorporating state-of-the-art engineering design.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0903, eff. January 1, 1985.
9VAC5-40-1080. Standard for sulfur dioxide.
No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any sulfur dioxide emissions in excess of the following limit:
S = 2.64K
where:
S = allowable emission of sulfur dioxide expressed in pounds per hour.
K = actual heat input expressed in Btu X 106 per hour.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0904, eff. January 1, 1985.
9VAC5-40-1090. Standard for visible emissions.
No owner or other person shall cause to be discharged into the atmosphere from any affected facility any visible emissions in excess of the following limits:
1. The limits in 9VAC5-40-80 during the coking operation.
2. An average of 20% opacity from the coke side enclosure during the pushing operation.
3. An average of 20% opacity during the charging operation.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0905, eff. January 1, 1985.
9VAC5-40-1100. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0906, eff. January 1, 1985.
9VAC5-40-1110. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0907, eff. January 1, 1985.
9VAC5-40-1120. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0908, eff. January 1, 1985.
9VAC5-40-1130. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0909, eff. January 1, 1985.
9VAC5-40-1140. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply, except:
1. Compliance with particulate standards prescribed by 9VAC5-40-1070 A and B shall be determined by three or more emission tests conducted at different times during the total operation of the affected facility. The emission tests and times shall be acceptable to the board.
2. Compliance with opacity standards for fugitive visible emissions prescribed by 9VAC5-40-1090 B and C shall be determined by conducting observations in accordance with the test methods and procedures prescribed in subsections B 1 and 2 of this section.
a. The opacity of coke oven fugitive particulate emissions is determined by an observer, qualified in accordance with Reference Method 9, using the following procedures:
(1) The qualified observer shall, to the extent practicable, stand in a position meeting the guidelines of Reference Method 9. Notwithstanding any Method 9 guideline, the observer shall stand in a safe position with an unobstructed view of the emission source.
(2) Field records shall be in accordance with Reference Method 9.
(3) Each opacity observation shall be made at the point of greatest opacity after the emissions leave the coke oven. Observations shall be recorded at 15 second intervals for the entire duration of the charge or push. Observations which cannot be made due to the interference of another plume or any other obstruction shall be noted with an asterisk.
(4) Recording observations shall be in accordance with Reference Method 9, except that the minimum number of observations shall be determined by the duration of the operation being observed.
(5) Opacity shall be determined as an average of all 15 second observations recorded during either charging or pushing, as appropriate. Opacity of emissions shall be determined individually for each charge or push, and shall not be averaged over more than one coke oven. Missing observations due to interferences shall not affect the opacity determination.
b. All certification and testing requirements are identical to those of Reference Method 9.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0910, eff. January 1, 1985.
9VAC5-40-1150. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0911, eff. January 1, 1985.
9VAC5-40-1160. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0912, eff. January 1, 1985.
9VAC5-40-1170. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0913, eff. January 1, 1985.
9VAC5-40-1180. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0914, eff. January 1, 1985.
9VAC5-40-1190. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-0915, eff. January 1, 1985.
Article 10
Emission Standards for Asphalt Concrete Plants (Rule 4-10)
9VAC5-40-1200. Applicability and designation of affected facility.
Article 10
Emission Standards for Asphalt Concrete Plants (Rule 4-10)
A. The affected facility to which the provisions of this article apply is each asphalt concrete plant. For the purpose of this article, an asphalt concrete plant is comprised only of any combination of the following: dryers; systems for screening, handling, storing, and weighing aggregate; systems for loading, transferring, and storing mineral filler; systems for mixing asphalt concrete; and the loading, transfer, and storage systems associated with emission control systems.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1001, eff. January 1, 1985.
9VAC5-40-1210. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Asphalt concrete plant" means any facility used to manufacture asphalt concrete by heating and drying aggregate and mixing with asphalt cements.
"Process operation" means any method, form, action, operation or treatment of manufacturing or processing, including any storage or handling of materials or products before, during or after manufacturing or processing.
"Process unit" means any step in a manufacturing or process operation which results in emission of pollutants to the atmosphere.
"Process weight" means total weight of all materials introduced into any process unit which may cause any emission of pollutants. Process weight includes solid fuels charged, but does not include liquid and gaseous fuels charged or combustion air for all fuels.
"Process weight rate" means a rate established as follows:
a. For continuous or long-run steady-state process operations, the total process weight for the entire period of continuous operation or for a typical portion of it, divided by the number of hours of such period or portion of it.
b. For cyclical or batch process operations, the total weight for a period that covers a complete operation or an integral number of cycles, divided by the hours of actual process operation during such a period.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1002, eff. January 1, 1985.
9VAC5-40-1220. Standard for particulate matter.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any asphalt concrete plant any particulate emissions in excess of the limits in Table 4-10.
TABLE 4-10 | |
Process Weight Rate | Maximum Allowable Emission Rate |
Tons/Hr | Lb/Hr |
5 or less | 10 |
10 | 16 |
15 | 22 |
20 | 28 |
25 | 31 |
50 | 33 |
100 | 37 |
150 | 40 |
200 | 43 |
250 | 47 |
300 or more | 50 |
B. Interpretation of the emission standard in subsection A of this section shall be in accordance with 9VAC5-40-22.
C. The provisions of this section shall not apply to affected facilities identified in subsection A of this section and located in AQCR 7; however, the provisions of 9VAC5-40-270 shall apply to the facilities.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1003, eff. January 1, 1985.
9VAC5-40-1230. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1004, eff. January 1, 1985.
9VAC5-40-1240. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1005, eff. January 1, 1985.
9VAC5-40-1250. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1006, eff. January 1, 1985.
9VAC5-40-1260. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1007, eff. January 1, 1985.
9VAC5-40-1270. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1008, eff. January 1, 1985.
9VAC5-40-1280. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1009, eff. January 1, 1985.
9VAC5-40-1290. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1010, eff. January 1, 1985.
9VAC5-40-1300. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1011, eff. January 1, 1985.
9VAC5-40-1310. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1012, eff. January 1, 1985.
9VAC5-40-1320. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1013, eff. January 1, 1985.
9VAC5-40-1330. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1014, eff. January 1, 1985.
Article 11
Emission Standards for Petroleum Refinery Operations (Rule 4-11) [Repealed]
9VAC5-40-1340. (Repealed.)
Historical Notes
Derived from VR120-04-1101, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1350. (Repealed.)
Historical Notes
Derived from VR120-04-1102, eff. July 1, 1991; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1360. (Repealed.)
Historical Notes
Derived from VR120-04-1103, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1370. (Repealed.)
Historical Notes
Derived from VR120-04-1104, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1380. (Repealed.)
Historical Notes
Derived from VR120-04-1105, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1390. (Repealed.)
Historical Notes
Derived from VR120-04-1106, eff. July 1, 1991; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1400. (Repealed.)
Historical Notes
Derived from VR120-04-1107, eff. July 1, 1991; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1410. (Repealed.)
Historical Notes
Derived from VR120-04-1108, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1420. (Repealed.)
Historical Notes
Derived from VR120-04-1109, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1430. (Repealed.)
Historical Notes
Derived from VR120-04-1110, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1440. (Repealed.)
Historical Notes
Derived from VR120-04-1111, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1450. (Repealed.)
Historical Notes
Derived from VR120-04-1112, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1460. (Repealed.)
Historical Notes
Derived from VR120-04-1113, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1470. (Repealed.)
Historical Notes
Derived from VR120-04-1114, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1480. (Repealed.)
Historical Notes
Derived from VR120-04-1115, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1490. (Repealed.)
Historical Notes
Derived from VR120-04-1116, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1500. (Repealed.)
Historical Notes
Derived from VR120-04-1117, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-1510. (Repealed.)
Historical Notes
Derived from VR120-04-1118, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
Article 12
Emission Standards for Chemical Fertilizer Manufacturing Operations
9VAC5-40-1520. Applicability and designation of affected facility.
Article 12
Emission Standards for Chemical Fertilizer Manufacturing Operations
A. The affected facility to which the provisions of this article apply is each chemical fertilizer manufacturing operation. For the purpose of this article, a chemical fertilizer manufacturing operation is comprised only of any combination of the following: grinders, dryers, coolers and ammoniator-granulators.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1201, eff. January 1, 1985.
9VAC5-40-1530. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Chemical fertilizer" means a compound or mixture, whose chief ingredients are nitrogen, phosphorous, potassium or any combination of these ingredients, which has agronomic value.
"Manufacturing operation" means any process operation or combination of physically connected dissimilar process operations which is operated to effect physical or chemical changes, or both, in an article.
"Materials handling equipment" means any equipment used as a part of a process operation or combination of process operations which does not effect a physical or chemical change in the material or in an article, such as, but not limited to, conveyors, elevators, feeders or weighers.
"Physically connected" means any combination of process operations connected by materials handling equipment and designed for simultaneous complementary operation.
"Process operation" means any method, form, action, operation or treatment of manufacturing or processing, including any storage or handling of materials or products before, during or after manufacturing or processing.
"Process unit" means any step in a manufacturing or process operation which results in the emission of pollutants to the atmosphere.
"Process weight" means total weight of all materials introduced into any process unit which may cause any emission of pollutants. Process weight includes solid fuels charged, but does not include liquid and gaseous fuels charged or combustion air for all fuels.
"Process weight rate" means a rate established as follows:
a. For continuous or long-run steady-state process operations, the total process weight for the entire period of continuous operation or for a typical portion of it, divided by the number of hours of such period or portion of it.
b. For cyclical or batch process operations, the total weight for a period that covers a complete operation or an integral number of cycles, divided by the hours of actual process operation during such a period.
"Production rate" means the weight of final product obtained per hour of operation. If the rate of product going to storage can vary, the production rate shall be determined by calculation from the feed rates of raw material.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1202, eff. January 1, 1985.
9VAC5-40-1540. Standard for particulate matter.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any chemical fertilizer manufacturing operation, which utilizes recycle and physically connected dissimilar processes as a part of the manufacturing operation, any particulate emissions in excess of the limits in Table 4-12.
TABLE 4-12 | |
Process Weight Rate | Maximum Allowable Emission Rate |
15 or less | 19.2 |
30 | 30.5 |
60 | 42.5 |
90 | 46.3 |
120 | 49.0 |
150 | 51.2 |
180 | 53.1 |
B. Except as provided in subsections C and D of this section, interpretation of the emission standard in subsection A of this section shall be in accordance with 9VAC5-40-22.
C. The process weight rate entry to be used in Table 4-12 for chemical fertilizer manufacturing operations shall be considered as the production rate, or for chemical fertilizer manufacturing operations involving physically connected dissimilar process operations shall be the sum of the process weight rates of each of the dissimilar process operations. The materials handling and screening equipment shall not be considered as a part of the process operation for the determination of process weight rate. For a process weight rate between any two consecutive rates stated in Table 4-14 maximum allowable emissions of particulate matter shall be calculated by the following equation:
1. For process weight rates up to 45 tons per hour:
| E = 4.10 ( | 2P(0.67) | ) |
| 3 |
where:
E = emission rate in lb/hr.
P = process weight rate in tons/hr.
2. For process weight rates over 45 tons per hour:
| E = 55.0 ( | 2P(0.11) | ) - 40 |
| 3 |
where:
E = emission rate in lb/hr.
P = process weight rate in tons/hr
D. When one manufacturing operation, or combination of physically connected process operations, is vented through separate stacks, the allowable emission rate for each stack shall be such that the sum of the emission rates for all of the stacks from that operation is equal to the allowable rates from that operation vented through a single stack.
E. For purpose of emission testing, samples taken of separate stacks within a three-day period, on the same fertilizer grade, shall be considered as simultaneous for the purpose of determining total operation emissions.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1203, eff. January 1, 1985.
9VAC5-40-1550. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1204, eff. January 1, 1985.
9VAC5-40-1560. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1205, eff. January 1, 1985.
9VAC5-40-1570. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1206, eff. January 1, 1985.
9VAC5-40-1580. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1207, eff. January 1, 1985.
9VAC5-40-1590. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1208, eff. January 1, 1985.
9VAC5-40-1600. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1209, eff. January 1, 1985.
9VAC5-40-1610. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1210, eff. January 1, 1985.
9VAC5-40-1620. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1211, eff. January 1, 1985.
9VAC5-40-1630. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1212, eff. January 1, 1985.
9VAC5-40-1640. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1213, eff. January 1, 1985.
9VAC5-40-1650. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1214, eff. January 1, 1985.
Article 13
Emission Standards for Pulp and Paper Mills (Rule 4-13)
9VAC5-40-1660. Applicability and designation of affected facilities.
Article 13
Emission Standards for Pulp and Paper Mills (Rule 4-13)
A. The affected facilities in pulp and paper mills to which the provisions of this article apply are: each recovery furnace, each smelt dissolving tank, each lime kiln, each slaker tank, and each kraft wood pulping operation. For the purpose of this article, a kraft wood pulping operation is comprised only of any combination of the following units: recovery furnaces, lime kilns, digester systems, multiple-effect evaporator systems, condensate stripper systems and smelt dissolving tanks.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
C. The provisions of this article do not apply to affected facilities subject to Article 5 (9VAC5-50-400 et seq.) of Part II of 9VAC5 Chapter 50, except to the extent such pollutants are emitted which are not subject to standards of performance in Article 5 (9VAC5-50-400 et seq.) of Part II of 9VAC5 Chapter 50.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1301, eff. October 1, 1989; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999.
9VAC5-40-1670. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Black liquor solids" means the dry weight of the solids which enter the recovery furnace in the black liquor.
"Condensate stripper system" means a column, and associated condensers, used to strip, with air or steam, total reduced sulfur compounds from condensate streams from various processes within a kraft pulp mill.
"Cross recovery furnace" means a furnace used to recover chemicals consisting primarily of sodium and sulfur compounds by burning black liquor which on a quarterly basis contains more than 7.0% by weight of the total pulp solids from the neutral sulfite or other semichemical process and has a green liquor sulfidity of more than 28%.
"Digester system" means each continuous digester or each batch digester used for the cooking of wood in white liquor, and associated flash tanks, below tanks, chip steamers, and condensers.
"Green liquor sulfidity" means the sulfidity of the liquor which leaves the smelt dissolving tank.
"Kraft pulp mill" means any facility which produces pulp from wood by cooking (digesting) wood chips in a water solution of sodium hydroxide and sodium sulfide (white liquor) at high temperature and pressure. Regeneration of the cooking chemicals through a recovery process is also considered part of the kraft pulp mill.
"Lime kiln" means a unit used to calcine lime mud, which consists primarily of calcium carbonate, into quicklime, which is calcium oxide.
"Multiple-effect evaporator system" means the multiple-effect evaporators and associated condensers and hotwells used to concentrate the spent cooking liquid that is separated from the pulp (black liquor).
"Neutral sulfite semichemical pulping operation" means any operation in which pulp is produced from wood by cooking (digesting) wood chips in a solution of sodium sulfite and sodium bicarbonate, followed by mechanical defibrating (grinding).
"New design recovery furnace" means a straight kraft recovery furnace that has both membrane wall or welded wall construction and emission control designed air systems. A new design furnace shall have stated in its contract a TRS performance guarantee or that it was designed with air pollution control as an objective.
"Old design recovery furnace" means a straight kraft recovery furnace that does not have membrane wall or welded wall construction or emission control designed air systems.
"Pulp and paper mill" means any kraft pulp mill or any paper mill using a semichemical pulping process.
"Recovery furnace" means either a straight kraft recovery furnace or a cross recovery furnace, and includes the direct-contact evaporator for a direct-contact furnace.
"Semichemical pulping process" means any pulp manufacturing process in which the active chemicals of the liquor used in cooking (digesting) wood chips to their component parts in a pressurized vessel (digester) are primarily a liquor of sodium hydroxide and sodium carbonate. The major difference between all semichemical techniques and those of kraft and acid sulfite processes is that only a portion of the lignin is removed during the cooking (digesting), after which the pulp is further reduced by mechanical disintegration.
"Smelt dissolving tank" means a vessel used for dissolving the smelt collected from the recovery furnace.
"Straight kraft recovery furnace" means a furnace used to recover chemicals consisting primarily of sodium and sulfur compounds by burning black liquor which on a quarterly basis contains 7.0% by weight or less of the total pulp solids from the neutral sulfite or other semichemical process or has green liquor sulfidity of 28% or less.
"Total reduced sulfur" or "TRS" means the sum of the following sulfur compounds (hydrogen sulfide, methyl mercaptan, dimethyl sulfide and dimethyl disulfide, reported as hydrogen sulfide) that are released during any kraft wood pulping operation.
"Twenty-four hour average" means the average of data over a 24-hour period beginning at midnight.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1302, eff. October 1, 1989; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999.
9VAC5-40-1680. Standard for particulate matter.
No owner or other person shall cause or permit to be discharged into the atmosphere from any group of similar affected facilities specified below any particulate emissions in excess of the following limits:
Affected Facility | Maximum Allowable Emission of Particulate in Lb/Equivalent Ton of Air Dried Pulp |
All Recovery Furnace Units | 3.00 |
All Smelt Dissolving Tank Units | 0.75 |
All Lime Kiln Units | 1.00 |
All Slaker Tank Units | 0.30 |
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1303, eff. January 1, 1985.
9VAC5-40-1690. Standard for total reduced sulfur.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any kraft wood pulping operation unit specified below any total reduced sulfur emissions in excess of the following limits:
1. Recovery furnaces.
a. Old design furnaces -- 20 ppm by volume on a dry basis, corrected to 8.0% oxygen.
b. New design furnaces -- 5 ppm by volume on a dry basis, corrected to 8.0% oxygen.
c. Cross recovery furnaces -- 25 ppm by volume on a dry basis, corrected to 8.0% oxygen.
2. Digester systems -- 5 ppm by volume on a dry basis, corrected to 10% oxygen.
3. Multiple-effect evaporator systems -- 5 ppm by volume on a dry basis, corrected to 10% oxygen.
4. Lime kilns -- 20 ppm by volume on a dry basis, corrected to 10% oxygen.
5. Condensate stripper systems -- 5 ppm by volume on a dry basis, corrected to 10% oxygen.
6. Smelt dissolving tanks -- 0.033 pounds per ton black liquor solids as H2S.
B. Achievement of the emission standards in this section by use of methods in 9VAC5-40-1700 will be acceptable to the board.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1304, eff. October 1, 1989; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999.
9VAC5-40-1700. Control technology guidelines.
The control method should consist of one of the following:
1. Combustion of gases in a lime kiln or recovery furnace subject to the provisions of this article.
2. Combustion of gases in equipment or a device which is not subject to the provisions of this article and which is subjected to a minimum temperature of 1200°F for at least 0.5 seconds.
3. Any control method of equal or greater efficiency to the method in subsection B of this section, provided such method is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1305, eff. October 1, 1989.
9VAC5-40-1710. Standard for visible emissions.
A. The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply except with regard to recovery furnaces; for such facilities the provisions in subsection B of this section apply instead of 9VAC5-40-80 A.
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any recovery furnace any visible emissions which exhibit greater than 35% opacity. Failure to meet the requirements of this section because of the presence of water vapor shall not be a violation of this section.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1306, eff. January 1, 1985.
9VAC5-40-1720. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1307, eff. January 1, 1985.
9VAC5-40-1730. Standard for odor.
The provisions of Article 2 ( 9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply, except for total reduced sulfur emissions.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1308, eff. October 1, 1989.
9VAC5-40-1740. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1309, eff. January 1, 1985.
9VAC5-40-1750. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1310, eff. October 1, 1989; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999.
9VAC5-40-1760. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1311, eff. January 1, 1985.
9VAC5-40-1770. Monitoring.
A. The provisions of 9VAC5-40-40 (Monitoring) apply, with any addition or modification deemed appropriate to meet the needs of subsection B of this section.
B. The owner of a kraft pulp mill shall by October 1, 1990:
1. Install, certify, maintain and operate continuous monitoring equipment to monitor and record the concentration of TRS emissions on a dry basis and the percentage of oxygen by volume on a dry basis in the gases discharged into the atmosphere from any lime kiln or recovery furnace. The location of each monitoring system must be approved by the board.
2. Install, calibrate, maintain, and operate a monitoring device which measures the combustion temperature at the point of incineration of effluent gases which are emitted from any lime kiln, recovery furnace, digester system, multiple-effect evaporator system, or condensate stripper system. The monitoring device is to be certified by the manufacturer to be accurate within 1.0% of the temperature being measured.
C. The minimum data capture and validity requirements shall be as follows:
1. Valid TRS and oxygen data shall be obtained for no less than 75% of the operating hours of each quarter. Section 4 of Procedure 1 of Appendix F of 40 CFR Part 60 shall be used to determine valid data.
2. For TRS or oxygen concentrations, a valid data hour shall have at least 50% valid readings.
3. A 24-hour average TRS or oxygen concentration shall be considered valid if at least 50% of the operating hours in the 24-hour period are valid data hours.
4. Valid temperature data shall be obtained for no less than 90% of the operating time of each quarter.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1312, eff. October 1, 1989; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999.
9VAC5-40-1780. Notification, records, and reporting.
A. The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
B. Any owner subject to the provisions of 9VAC5-40-1770 B shall:
1. Calculate and record on a daily basis the 24-hour average TRS concentration for each operating day for each recovery furnace and lime kiln. Each 24-hour average shall be determined as the arithmetic mean of the appropriate 24 contiguous 1-hour average TRS concentrations provided by each continuous monitoring system installed under 9VAC5-40-1770 B 1.
2. Calculate and record on a daily basis the 24-hour average oxygen concentration for each operating day for each recovery furnace and lime kiln. These 24-hour averages shall correspond to the 24-hour average TRS concentration under subsection B 1 of this section and shall be determined as an arithmetic mean of the appropriate 24 contiguous one-hour average oxygen concentrations provided by each continuous monitoring system installed under 9VAC5-40-1770 B 1.
3. Correct all 24-hour average TRS concentrations to 10 volume percent oxygen, except that all 24-hour average TRS concentrations from a recovery furnace shall be corrected to 8 volume percent using the following equation:
Ccorr = Cuncorr x (21-X)/(21-Y)
where:
Ccorr = the concentration corrected for oxygen.
Cuncorr = the concentration uncorrected for oxygen.
X = the volumetric oxygen concentration in percentage to be corrected (8.0 for recovery furnaces and 10 for lime kilns, incinerators, or other devices).
Y = the measured 24-hour average volumetric oxygen concentration.
4. Record continuously on a daily basis the temperature of any applicable point of incineration.
5. Record on a daily basis the periods of operation for each operating day for each recovery furnace and lime kiln.
C. For the purpose of reports required under 9VAC5-40-50 C, the following information shall be reported:
1. For emissions from any recovery furnace, all 24-hour average TRS concentrations above the applicable emission standard in 9VAC5-40-1690.
2. For emissions from any lime kiln, all 24-hour average TRS concentrations above the applicable emission standard in 9VAC5-40-1690.
3. For emissions from any digester system, multiple-effect evaporator system, or condensate stripper system, all periods in excess of five minutes and their duration during which the combustion temperature is less than 1200°F if the gases are combusted in an incinerator or other device approved by the board which does not generate TRS.
4. For each recovery furnace or lime kiln, the periods of operation.
D. Each owner subject to the provisions of 9VAC5-40-1770 B 1 shall develop and implement a quality assurance plan. At a minimum the plan shall provide for daily calibration drift checks, periodic preventive maintenance, and annual audits. Section 3 of Procedure 1 of Appendix F of 40 CFR Part 60 may be used as a guide by which to pattern the plan.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1313, eff. October 1, 1989; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999.
9VAC5-40-1790. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1314, eff. January 1, 1985.
9VAC5-40-1800. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1315, eff. January 1, 1985.
9VAC5-40-1810. Permits.
A permit may be required prior to beginning any of the activities specified below if the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1316, eff. January 1, 1985; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999.
Article 14
Emission Standards for Sand and Gravel Processing Operations and Stone Quarrying and Processing Operations (Rule 4-14)
9VAC5-40-1820. Applicability and designation of affected facility.
Article 14
Emission Standards for Sand and Gravel Processing Operations and Stone Quarrying and Processing Operations (Rule 4-14)
A. The affected facility to which the provisions of this article apply is each sand and gravel processing operation and each stone quarrying and processing operation.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1401, eff. January 1, 1985.
9VAC5-40-1830. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Process operation" means a method, form, action, operation or treatment of manufacturing or processing, including any storage or handling of materials or products before, during or after manufacturing or processing.
"Process unit" means any step in a manufacturing or process operation which results in the emission of pollutants to the atmosphere.
"Process weight" means total weight of all materials introduced into any process unit which may cause any emission of pollutants. Process weight includes solid fuels charged, but does not include liquid and gaseous fuels charged or combustion air for all fuels.
"Process weight rate" means a rate established as follows:
a. For continuous or long-run steady-state process operations the total process weight for the entire period of continuous operation or for a typical portion of it, divided by the number of hours of such period or portion of it.
b. For cyclical or batch process operations, the total weight for a period that covers a complete operation or an integral number of cycles, divided by the hours of actual process operation during such a period.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1402, eff. January 1, 1985.
9VAC5-40-1840. Standard for particulate matter.
A. No owner or other person shall cause or permit any material to be produced, handled, stockpiled or transported without taking measures to reduce to a minimum any particulate matter from becoming airborne. Where it is practical to measure the emission, the emission shall not exceed the limits established by Table 4-14. All such airborne particulate matter emanating from the yards, sidings or roads of such operations shall be considered fugitive dust and shall be controlled as stipulated in 9VAC5-40-1860. All crushers shall be fitted with liquid sprays or other appropriate systems which effectively limit the escape of airborne dust. Vibrating and shaker screens handling dry materials shall be enclosed or fitted with a collector system which will prevent the release of more than 0.05 grains per standard cubic foot. All feeders, elevators, conveyors, transfer points, discharge points and loading points shall be equipped with collectors, sprays or other means when necessary to minimize the escape of dust.
TABLE 4-14 | ||
Process Weight | Maximum Allowable Emission Rate | |
Lb/Hr | Tons/Hr | Lb/Hr |
100 or less | 0.05 or less | 0.551 |
200 | 0.10 | 0.877 |
400 | 0.20 | 1.40 |
600 | 0.30 | 1.83 |
800 | 0.40 | 2.22 |
1000 | 0.50 | 2.58 |
1500 | 0.75 | 3.38 |
2000 | 1.00 | 4.10 |
2500 | 1.25 | 4.76 |
3000 | 1.50 | 5.38 |
3500 | 1.75 | 5.96 |
4000 | 2.00 | 6.52 |
5000 | 2.50 | 7.58 |
6000 | 3.00 | 8.56 |
7000 | 3.50 | 9.49 |
8000 | 4.00 | 10.4 |
9000 | 4.50 | 11.2 |
10000 | 5.00 | 12.0 |
12000 | 6.00 | 13.6 |
16000 | 8.00 | 16.5 |
18000 | 9.00 | 17.9 |
20000 | 10.00 | 19.2 |
30000 | 15.00 | 25.2 |
40000 | 20.00 | 30.5 |
50000 | 25.00 | 35.4 |
60000 | 30.00 | 40.0 |
70000 | 35.00 | 41.3 |
80000 | 40.00 | 42.5 |
90000 | 50.00 | 44.6 |
120000 | 60.00 | 46.3 |
140000 | 70.00 | 47.8 |
160000 | 80.00 | 49.1 |
200000 | 100.00 | 51.3 |
1000000 | 500.00 | 69.0 |
2000000 | 1000.00 | 77.6 |
6000000 | 3000.00 | 92.7 |
B. Interpretation of emission standard in subsection A of this section shall be in accordance with 9VAC5-40-22.
C. The provisions of this section shall not apply to affected facilities identified in subsection A of this section and located in AQCR 7; however, the provisions of 9VAC5-40-270 shall apply to the facilities.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1403, eff. January 1, 1985.
9VAC5-40-1850. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1404, eff. January 1, 1985.
9VAC5-40-1860. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1405, eff. January 1, 1985.
9VAC5-40-1870. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1406, eff. January 1, 1985.
9VAC5-40-1880. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1407, eff. January 1, 1985.
9VAC5-40-1890. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1408, eff. January 1, 1985.
9VAC5-40-1900. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1409, eff. January 1, 1985.
9VAC5-40-1910. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1410, eff. January 1, 1985.
9VAC5-40-1920. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1411, eff. January 1, 1985.
9VAC5-40-1930. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1412, eff. January 1, 1985.
9VAC5-40-1940. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1413, eff. January 1, 1985.
9VAC5-40-1950. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1414, eff. January 1, 1985.
Article 15
Emission Standards for Coal Preparation Plants (Rule 4-15)
9VAC5-40-1960. Applicability and designation of affected facility.
Article 15
Emission Standards for Coal Preparation Plants (Rule 4-15)
A. The affected facilities in coal preparation plants to which the provisions of this article apply are: thermal dryers, pneumatic coal- cleaning equipment (air tables), coal processing and conveying equipment (including breakers and crushers), coal storage systems, and coal transfer and loading systems.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1501, eff. January 1, 1985.
9VAC5-40-1970. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Coal preparation plant" means any facility (excluding underground mining operations) which prepares coal by one or more of the following processes: breaking, crushing, screening, wet or dry cleaning, and thermal drying.
"Coal processing and conveying equipment" means any machinery used to reduce the size of coal or to separate coal from refuse, and the equipment used to convey coal to or remove coal and refuse from the machinery. This includes, but is not limited to, breakers, crushers, screens and conveyor belts.
"Coal storage system" means any facility used to store coal except for open storage piles.
"Pneumatic coal-cleaning equipment" means any facility which classifies bituminous coal by size or separates bituminous coal from refuse by application of air streams.
"Process operation" means any method, form, action, operation or treatment of manufacturing or processing, including any storage or handling of materials or products before, during or after manufacturing or processing.
"Process unit" means any step in a manufacturing or process operation which results in the emission of pollutants to the atmosphere.
"Process weight" means the total weight of all materials introduced into any process unit which may cause any emission of pollutants. Process weight includes solid fuels charged, but does not include liquid and gaseous fuels charged or combustion air for all fuels.
"Process weight rate" means a rate established as follows:
a. For continuous or long-run steady-state process operations, the total process weight for the entire period of continuous operation or for a typical portion of it, divided by the number of hours of such period or portion of it.
b. For cyclical or batch process operations, the total weight for a period that covers a complete operation or an integral number of cycles, divided by the hours of actual process operation during such a period.
"Thermal drier" means any facility in which the moisture content of bituminous coal is reduced by contact with a heated gas stream which is exhausted to the atmosphere.
"Transfer and loading system" means any facility used to transfer and load coal for shipment.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1502, eff. January 1, 1985.
9VAC5-40-1980. Standard for particulate matter.
A. Thermal driers.
1. No owner or other person shall cause or permit to be discharged into the atmosphere from any thermal drier any particulate emissions in excess of the limits in Table 4-15A.
TABLE 4-15A | |
Process Weight Rate | Maximum Allowable Emission Rate |
100 or less | 45 |
200 or more | 105 |
2. Interpretation of the emission standard in subdivision A 1 of this section shall be in accordance with 9VAC5-40-22.
B. Pneumatic coal-cleaning equipment.
1. No owner or other person shall cause or permit to be discharged into the atmosphere from any pneumatic coal-cleaning equipment any particulate emissions in excess of 0.05 grains per standard cubic foot of exhaust gas. In no event shall the emission rate exceed the appropriate limit in Table 4-15B.
2. Interpretation of the emission standard in subdivision B 1 of this section shall be in accordance with 9VAC5-40-22.
TABLE 4-15B | ||
Process Weight Rate | Maximum Allowable Emission Rate | |
Lb/Hr | Tons/Hr | Lb/Hr |
100 | 0.05 | 0.551 |
200 | 0.10 | 0.877 |
400 | 0.20 | 1.40 |
600 | 0.30 | 1.83 |
800 | 0.40 | 2.22 |
1000 | 0.50 | 2.58 |
1500 | 0.75 | 3.38 |
2000 | 1.00 | 4.10 |
2500 | 1.25 | 4.76 |
3000 | 1.50 | 5.38 |
3500 | 1.75 | 5.96 |
4000 | 2.00 | 6.52 |
5000 | 2.50 | 7.58 |
6000 | 3.00 | 8.56 |
7000 | 3.50 | 9.49 |
8000 | 4.00 | 10.4 |
9000 | 4.50 | 11.2 |
10000 | 5.00 | 12.0 |
12000 | 6.00 | 13.6 |
16000 | 8.00 | 16.5 |
18000 | 9.00 | 17.9 |
20000 | 10.00 | 19.2 |
30000 | 15.00 | 25.2 |
40000 | 20.00 | 30.5 |
50000 | 25.00 | 35.4 |
60000 | 30.00 | 40.0 |
70000 | 35.00 | 41.3 |
80000 | 40.00 | 42.5 |
90000 | 45.00 | 43.6 |
100000 | 50.00 | 44.6 |
120000 | 60.00 | 46.3 |
140000 | 70.00 | 47.8 |
160000 | 80.00 | 49.1 |
200000 | 100.00 | 51.3 |
1000000 | 500.00 | 69.0 |
2000000 | 1000.00 | 77.6 |
6000000 | 3000.00 | 92.7 |
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1503, eff. January 1, 1985.
9VAC5-40-1990. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1504, eff. January 1, 1985.
9VAC5-40-2000. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1505, eff. January 1, 1985.
9VAC5-40-2010. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1506, eff. January 1, 1985.
9VAC5-40-2020. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1507, eff. January 1, 1985.
9VAC5-40-2030. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1508, eff. January 1, 1985.
9VAC5-40-2040. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1509, eff. January 1, 1985.
9VAC5-40-2050. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1510, eff. January 1, 1985.
9VAC5-40-2060. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1511, eff. January 1, 1985.
9VAC5-40-2070. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1512, eff. January 1, 1985.
9VAC5-40-2080. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1513, eff. January 1, 1985.
9VAC5-40-2090. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1514, eff. January 1, 1985.
Article 16
Emission Standards for Portland Cement Plants (Rule 4-16)
9VAC5-40-2100. Applicability and designation of affected facility.
Article 16
Emission Standards for Portland Cement Plants (Rule 4-16)
A. The affected facilities in Portland cement plants to which the provisions of this article apply are: kiln, clinker cooler, raw mill system, finish mill system, raw mill dryer, raw material storage, clinker storage, finished product storage, conveyor transfer points, bagging and bulk loading and unloading systems.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1601, eff. January 1, 1985.
9VAC5-40-2110. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Portland cement plant" means any facility manufacturing portland cement by either the wet or dry process.
"Process operation" means any method, form, action, operation or treatment of manufacturing or processing, including any storage or handling of materials or products before, during or after manufacturing or processing.
"Process unit" means any step in a manufacturing or process operation which results in the emission of pollutants to the atmosphere.
"Process weight" means the total weight of all materials introduced into any process unit which may cause any emission of pollutants. Process weight includes solid fuels charged, but does not include liquid and gaseous fuels charged or combustion air for all fuels.
"Process weight rate" means a rate established as follows:
a. For continuous or long-run steady-state process operations, the total process weight for the entire period of continuous operation or for a typical portion of it, divided by the number of hours of such period or portion of it.
b. For cyclical or batch process operations, the total weight for a period that covers a complete operation or an integral number of cycles, divided by the hours of actual process operation during such a period.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1602, eff. January 1, 1985.
9VAC5-40-2120. Standard for particulate matter.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any particulate emissions in excess of the limits in Table 4-16.
TABLE 4-16 | ||
Process Weight | Maximum Allowable Emission Rate | |
Lb/Hr | Tons/Hr | Lb/Hr |
100 or less | 0.05 or less | 0.551 |
200 | 0.10 | 0.877 |
400 | 0.20 | 1.40 |
600 | 0.30 | 1.83 |
800 | 0.40 | 2.22 |
1000 | 0.50 | 2.58 |
1500 | 0.75 | 3.38 |
2000 | 1.00 | 4.10 |
2500 | 1.25 | 4.76 |
3000 | 1.50 | 5.38 |
3500 | 1.75 | 5.96 |
4000 | 2.00 | 6.52 |
5000 | 2.50 | 7.58 |
6000 | 3.00 | 8.56 |
7000 | 3.50 | 9.49 |
8000 | 4.00 | 10.4 |
9000 | 4.50 | 11.2 |
10000 | 5.00 | 12.0 |
12000 | 6.00 | 13.6 |
16000 | 8.00 | 16.5 |
18000 | 9.00 | 17.9 |
20000 | 10.00 | 19.2 |
30000 | 15.00 | 25.2 |
40000 | 20.00 | 30.5 |
50000 | 25.00 | 35.4 |
60000 | 30.00 | 40.0 |
70000 | 35.00 | 41.3 |
80000 | 40.00 | 42.5 |
90000 | 45.00 | 43.6 |
100000 | 50.00 | 44.6 |
120000 | 60.00 | 46.3 |
140000 | 70.00 | 47.8 |
160000 | 80.00 | 49.1 |
200000 | 100.00 | 51.3 |
1000000 | 500.00 | 69.0 |
2000000 | 1000.00 | 77.6 |
6000000 | 3000.00 | 92.7 |
B. Interpretation of the emission standard in subsection A of this section shall be in accordance with 9VAC5-40-22.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1603, eff. January 1, 1985.
9VAC5-40-2130. Standard for sulfur dioxide.
No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any sulfur dioxide emissions in excess of the following limits:
S = 2.64K
where:
S = allowable emission of sulfur dioxide expressed in pounds per hour.
K = actual heat input expressed in Btu X 106 per hour.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1604, eff. January 1, 1985.
9VAC5-40-2140. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1605, eff. January 1, 1985.
9VAC5-40-2150. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1606, eff. January 1, 1985.
9VAC5-40-2160. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1607, eff. January 1, 1985.
9VAC5-40-2170. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1608, eff. January 1, 1985.
9VAC5-40-2180. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1609, eff. January 1, 1985.
9VAC5-40-2190. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1610, eff. January 1, 1985.
9VAC5-40-2200. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1611, eff. January 1, 1985.
9VAC5-40-2210. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1612, eff. January 1, 1985.
9VAC5-40-2220. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1613, eff. January 1, 1985.
9VAC5-40-2230. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1614, eff. January 1, 1985.
9VAC5-40-2240. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1615, eff. January 1, 1985.
Article 17
Emission Standards for Woodworking Operations (Rule 4-17)
9VAC5-40-2250. Applicability and designation of affected facility.
Article 17
Emission Standards for Woodworking Operations (Rule 4-17)
A. The affected facility to which the provisions of this article apply is each woodworking operation.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1701, eff. January 1, 1985.
9VAC5-40-2260. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Woodworking operation" means any operation involving the generation of small wood waste particles (shavings, sanderdust, sawdust, etc.) by any kind of mechanical manipulation of wood, bark, or wood byproducts. Includes, but is not limited to, sawing, planing, chipping, shaping, moulding, hogging, lathing and sanding. Also includes any woodworking waste collection operation.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1702, eff. January 1, 1985.
9VAC5-40-2270. Standard for particulate matter.
A. No owner or other person shall cause or permit to be discharged into the atmosphere any particulate emissions caused by any woodworking operation without providing, as a minimum, for their collection, adequate duct work and properly designed collectors, or such other devices, as approved by the board.
B. Particulate emissions shall not exceed 0.05 grains per standard cubic feet of exhaust gas.
C. The provisions of this section shall not apply to affected facilities identified in subsection A of this section and located in AQCR 7; however, the provisions of 9VAC5-40-270 shall apply to the facilities.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1703, eff. January 1, 1985.
9VAC5-40-2280. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1704, eff. January 1, 1985.
9VAC5-40-2290. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1705, eff. January 1, 1985.
9VAC5-40-2300. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1706, eff. January 1, 1985.
9VAC5-40-2310. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1707, eff. January 1, 1985.
9VAC5-40-2320. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1708, eff. January 1, 1985.
9VAC5-40-2330. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1709, eff. January 1, 1985.
9VAC5-40-2340. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1710, eff. January 1, 1985.
9VAC5-40-2350. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1711, eff. January 1, 1985.
9VAC5-40-2360. Registration.
The provisions of 9VAC5-40-60 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1712, eff. January 1, 1985.
9VAC5-40-2370. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-40-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1713, eff. January 1, 1985.
9VAC5-40-2380. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1714, eff. January 1, 1985.
Article 18
Emission Standards for Primary and Secondary Metal Operations (Rule 4-18)
9VAC5-40-2390. Applicability and designation of affected facility.
Article 18
Emission Standards for Primary and Secondary Metal Operations (Rule 4-18)
A. The affected facility to which the provisions of this article apply is each primary metal operation and each secondary metal operation.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1801, eff. January 1, 1985.
9VAC5-40-2400. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Aluminum production operation" means the production of aluminum or aluminum alloys from aluminum pigs, foundry returns or scrap material by smelting or melting to the metallic form. Includes fluxing, alloying, degassing, and demagging operations.
"Brass or bronze" means any metal alloy containing copper as its predominant constituent and lesser amounts of zinc, tin, lead or other metals.
"Brass or bronze production" means the production of brass or bronze ingots from scrap material by, or through a combination of, melting, smelting, refining or alloying.
"Ferroalloy production operation" means the production of any ferroalloy by use of a smelting furnace.
"Gray iron foundry operation" means the production of gray iron castings by use of a melting furnace.
"Lead" means elemental lead or alloys in which the predominant component is lead.
"Magnesium production operation" means the production of magnesium from scrap material by use of a furnace.
"Melt time" means the time in which the metal is melting and available at the spout or tap hole, excluding any time the equipment is idle, preheating or preparing for shutdown.
"Primary copper smelter" means any installation or any intermediate process engaged in the production of copper from copper sulfide ore concentrates through the use of pyrometallurgical techniques.
"Primary lead smelter" means any installation or any intermediate process engaged in the production of lead from lead sulfide ore concentrates through the use of pyrometallurgical techniques.
"Primary metal operation" means any operation which involves the production of a metal from metal ore concentrates through the use of pyrometallurgical techniques.
"Primary zinc smelter" means any installation or any intermediate process engaged in the production of zinc or zinc oxide from zinc sulfide ore concentrates through the use of pyrometallurgical techniques.
"Process operation" means any method, form, action, operation or treatment of manufacturing or processing, including any storage or handling of materials or products before, during or after manufacturing or processing.
"Process unit" means any step in a manufacturing or process operation which results in the emission of pollutants to the atmosphere.
"Process weight" means the total weight of all materials introduced into any process unit which may cause any emission of pollutants. Process weight includes solid fuels charged, but does not include liquid and gaseous fuels charged or combustion air for all fuels.
"Process weight rate" means a rate established as follows:
a. For continuous or long-run steady-state process operations, the total process weight for the entire period of continuous operation or for a typical portion of it, divided by the number of hours of such period or portion of it.
b. For cyclical or batch process operations, the total weight for a period that covers a complete operation or an integral number of cycles, divided by the hours of actual process operation during such a period.
"Secondary lead production operation" means the production of lead from lead bearing scrap material by smelting to the metallic form.
"Secondary metal operation" means any aluminum production operation, brass or bronze production operation, ferroalloy production operation, gray iron foundry operation, secondary lead production operation, magnesium production operation, steel foundry operation or zinc process operation.
"Steel foundry operation" means the production of steel castings by use of a melting furnace.
"Zinc process operation" means zinc reclaiming, zinc oxide manufacturing and zinc galvanizing.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1802, eff. January 1, 1985.
9VAC5-40-2410. Standard for particulate matter.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any secondary metal operation any particulate emissions in excess of the limits in Table 4-18.
TABLE 4-18 | |
Process Weight Rate | Maximum Allowable Emission Rate |
1,000 or less | 3.05 |
2,000 | 4.70 |
3,000 | 6.35 |
4,000 | 8.00 |
5,000 | 9.05 |
6,000 | 11.30 |
7,000 | 12.90 |
8,000 | 14.30 |
9,000 | 15.50 |
10,000 | 16.65 |
12,000 | 18.70 |
16,000 | 21.60 |
18,000 | 22.80 |
20,000 | 24.00 |
30,000 | 30.00 |
40,000 | 36.00 |
50,000 or more | 42.00 |
B. Interpretation of the emission standard in subsection A of this section shall be in accordance with 9VAC5-40-22.
C. The permissible emission rates as shown in Table 4-18 shall apply during the melt time but shall not apply during the time of preheat or preparing for shutdown. The exemption for preheating and shutdown shall be limited to two 20-minute periods in a given eight-hour period for each furnace unit.
D. The provisions of this section shall not apply to affected facilities identified in subsection A of this section and located in AQCR 7; however, the provisions of 9VAC5-40-270 shall apply to the facilities.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1803, eff. January 1, 1985.
9VAC5-40-2420. Standard for sulfur oxides.
No owner or other person shall cause or permit to be discharged into the atmosphere from any primary metal operation any sulfur oxide emissions in excess of the following limits:
Copper Smelters: Y = 0.2X
Zinc Smelters: Y = 0.564X0.85
Lead Smelters: Y = 0.98X0.77
where:
X = total sulfur fed to the smelter in lb/hr.
Y = allowable sulfur oxide emissions in lb/hr.
Note: This provision in effect requires removal of about 90% of the input-sulfur to the smelter.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1804, eff. January 1, 1985.
9VAC5-40-2430. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1805, eff. January 1, 1985.
9VAC5-40-2440. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1806, eff. January 1, 1985.
9VAC5-40-2450. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1807, eff. January 1, 1985.
9VAC5-40-2460. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1808, eff. January 1, 1985.
9VAC5-40-2470. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1809, eff. January 1, 1985.
9VAC5-40-2480. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1810, eff. January 1, 1985.
9VAC5-40-2490. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1811, eff. January 1, 1985.
9VAC5-40-2500. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1812, eff. January 1, 1985.
9VAC5-40-2510. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1813, eff. January 1, 1985.
9VAC5-40-2520. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1814, eff. January 1, 1985.
9VAC5-40-2530. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1815, eff. January 1, 1985.
Article 19
Emission Standards for Lightweight Aggregate Process Operations (Rule 4-19)
9VAC5-40-2540. Applicability and designation of affected facility.
Article 19
Emission Standards for Lightweight Aggregate Process Operations (Rule 4-19)
A. The affected facility to which the provisions of this article apply is each lightweight aggregate process operation.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1901, eff. January 1, 1985.
9VAC5-40-2550. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Process operation" means any method, form, action, operation or treatment of manufacturing or processing, including any storage or handling of materials or products before, during or after manufacturing or processing.
"Process unit" means any step in a manufacturing or process operation which results in the emission of pollutants to the atmosphere.
"Process weight" means total weight of all materials introduced into any process unit which may cause any emission of pollutants. Process weight includes solid fuels charged, but does not include liquid and gaseous fuels charged or combustion air for all fuels.
"Process weight rate" means a rate established as follows:
a. For continuous or long-run steady-state process operations, the total process weight for the entire period of continuous operation or for a typical portion of it, divided by the number of hours of such period or portion of it.
b. For cyclical or batch process operations, the total weight for a period that covers a complete operation or an integral number of cycles, divided by the hours of actual process operation during such a period.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1902, eff. January 1, 1985.
9VAC5-40-2560. Standard for particulate matter.
A. No owner or other person shall cause, or permit to be discharged into the atmosphere from any lightweight aggregate process operation any particulate emissions in excess of the limits in Table 4-19.
TABLE 4-19 | |
Process Weight Rate | Maximum Allowable Emission Rate |
.05 or less | .176 |
.10 | .351 |
.20 | .702 |
.30 | 1.053 |
.40 | 1.404 |
.50 | 1.76 |
.75 | 2.64 |
1.0 | 3.51 |
1.25 | 5.27 |
1.75 | 6.15 |
2.0 | 7.02 |
4.0 | 14.0 |
6.0 | 21.1 |
8.0 | 28.1 |
10.0 | 35.1 |
15.0 | 52.7 |
20.0 | 70.2 |
25.0 | 87.8 |
30.0 | 105.0 |
35.0 | 123.0 |
40.0 | 140.0 |
45.0 | 158.0 |
50.0 | 176.0 |
B. Except as provided in subsection C of this section, interpretation of the emission standard in subsection A of this section shall be in accordance with 9VAC5-40-22.
C. For a process weight rate between any two consecutive rates in Table 4-19, or for rates over 50 tons per hour, the maximum allowable emission rate may be calculated by the following equation:
E = 3.51 P
where:
E = emission rate in lb/hr.
P = process weight rate in tons/hr.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1903, eff. January 1, 1985.
9VAC5-40-2570. Standard for sulfur oxides.
No owner or other person shall cause, or permit fuel with a sulfur content in excess of three pounds per million Btu to be used in the processing of lightweight aggregate.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1904, eff. January 1, 1985.
9VAC5-40-2580. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1905, eff. January 1, 1985.
9VAC5-40-2590. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1906, eff. January 1, 1985.
9VAC5-40-2600. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1907, eff. January 1, 1985.
9VAC5-40-2610. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1908, eff. January 1, 1985.
9VAC5-40-2620. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1909, eff. January 1, 1985.
9VAC5-40-2630. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1910, eff. January 1, 1985.
9VAC5-40-2640. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1911, eff. January 1, 1985.
9VAC5-40-2650. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1912, eff. January 1, 1985.
9VAC5-40-2660. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1913, eff. January 1, 1985.
9VAC5-40-2670. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1914, eff. January 1, 1985.
9VAC5-40-2680. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-1915, eff. January 1, 1985.
Article 20
Emission Standards for Feed Manufacturing Operations (Rule 4-20)
9VAC5-40-2690. Applicability and designation of affected facility.
Article 20
Emission Standards for Feed Manufacturing Operations (Rule 4-20)
A. The affected facility to which the provisions of this article apply is each feed manufacturing operation.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2001, eff. January 1, 1985.
9VAC5-40-2700. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Feed manufacturing" means receiving, conditioning (drying, sizing, cleaning), blending and pelleting of grains, and their subsequent bagging or bulk loading.
"Manufacturing operation" means any process operation or combination of physically connected dissimilar process operations which is operated to effect physical or chemical changes, or both, in an article.
"Materials handling equipment" means any equipment used as a part of a process operation or combination of process operations which does not effect a physical or chemical change in the material or in an article, such as, but not limited to, conveyors, elevators, feeders or weighters.
"Physically connected" means any combination of process operations connected by materials handling equipment and designed for simultaneous complementary operation.
"Process operation" means any method, form, action, operation or treatment of manufacturing or processing, including any storage or handling of materials or products before, during or after manufacturing or processing.
"Process unit" means any step in a manufacturing or processing operation which results in the emission of pollutants to the atmosphere.
"Process weight" means total weight of all materials introduced into any process unit which may cause any emission of pollutants. Process weight includes solid fuels charged, but does not include liquid and gaseous fuels charged or combustion air for all fuels.
"Process weight rate" means a rate established as follows:
a. For continuous or long-run steady-state process operations, the total process weight for the entire period of continuous operation or for a typical portion of it, divided by the number of hours of such period or portion of it.
b. For cyclical or batch process operations, the total weight for a period that covers a complete operation or an integral number of cycles, divided by the hours of actual process operation during such a period.
"Production rate" means the weight of final product obtained per hour of operation. If the rate of product going to storage can vary, the production rate shall be determined by calculation from the feed rates of raw material.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2002, eff. January 1, 1985.
9VAC5-40-2710. Standard for particulate matter.
A. No owner or other person shall cause, or permit to be discharged into the atmosphere from any feed manufacturing operation any particulate emissions in excess of the limits in Table 4-20.
TABLE 4-20 | ||
Process Weight | Maximum Allowable Emission Rate | |
Lb/Hr | Tons/Hr | Lb/Hr |
100 or less | 0.05 or less | 0.551 |
200 | 0.10 | 0.877 |
400 | 0.20 | 1.40 |
600 | 0.30 | 1.83 |
800 | 0.40 | 2.22 |
1000 | 0.50 | 2.58 |
1500 | 0.75 | 3.38 |
2000 | 1.00 | 4.10 |
2500 | 1.25 | 4.76 |
3000 | 1.50 | 5.38 |
3500 | 1.75 | 5.96 |
4000 | 2.00 | 6.52 |
5000 | 2.50 | 7.58 |
6000 | 3.00 | 8.56 |
7000 | 3.50 | 9.49 |
8000 | 4.00 | 10.4 |
9000 | 4.50 | 11.2 |
10000 | 5.00 | 12.0 |
12000 | 6.00 | 13.6 |
16000 | 8.00 | 16.5 |
18000 | 9.00 | 17.9 |
20000 | 10.00 | 19.2 |
30000 | 15.00 | 25.2 |
40000 | 20.00 | 30.5 |
50000 | 25.00 | 35.4 |
60000 | 30.00 | 40.0 |
70000 | 35.00 | 41.3 |
80000 | 40.00 | 42.5 |
90000 | 45.00 | 43.6 |
100000 | 50.00 | 44.6 |
120000 | 60.00 | 46.3 |
140000 | 70.00 | 47.8 |
160000 | 80.00 | 49.1 |
200000 | 100.00 | 51.3 |
1000000 | 500.00 | 69.0 |
2000000 | 1000.00 | 77.6 |
6000000 | 3000.00 | 92.7 |
B. Except as provided in subsections C and D of this section, interpretation of the emission standard in subsection A of this section shall be in accordance with 9VAC5-40-22.
C. The process weight rate entry to be used in Table 4-20 for feed manufacturing process units shall be considered as the production rate.
D. The process weight rate entry to be used in Table 4-20 for feed manufacturing operations involving physically connected dissimilar process operations shall be the sum of the process weight rates of each of the dissimilar process operations. The materials handling equipment shall not be considered as a part of the process operation for determination of process weight rate.
E. The provisions of this section shall not apply to affected facilities identified in subsection A of this section and located in AQCR 7; however, the provisions of 9VAC5-40-270 shall apply to the facilities.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2003, eff. January 1, 1985.
9VAC5-40-2720. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2004, eff. January 1, 1985.
9VAC5-40-2730. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2005, eff. January 1, 1985.
9VAC5-40-2740. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2006, eff. January 1, 1985.
9VAC5-40-2750. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2007, eff. January 1, 1985.
9VAC5-40-2760. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2008, eff. January 1, 1985.
9VAC5-40-2770. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2009, eff. January 1, 1985.
9VAC5-40-2780. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2010, eff. January 1, 1985.
9VAC5-40-2790. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2011, eff. January 1, 1985.
9VAC5-40-2800. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2012, eff. January 1, 1985.
9VAC5-40-2810. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2013, eff. January 1, 1985.
9VAC5-40-2820. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2014, eff. January 1, 1985.
Article 21
Emissions Standards for Sulfuric Acid Production Units (Rule 4-21)
9VAC5-40-2830. Applicability and designation of affected facility.
Article 21
Emissions Standards for Sulfuric Acid Production Units (Rule 4-21)
A. The affected facility to which the provisions of this article apply is each sulfuric acid production unit.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2101, eff. January 1, 1985.
9VAC5-40-2840. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Sulfuric acid mist" means sulfuric acid mist, as measured by Reference Method 8 or an equivalent or alternative method.
"Sulfuric acid production unit" means any facility producing sulfuric acid by the contact process by burning elemental sulfur, alkylation acid, hydrogen sulfide, organic sulfides and mercaptans, or acid sludge; but does not include facilities where conversion to sulfuric acid is utilized primarily as a means of preventing emissions to the atmosphere of sulfur dioxide or other sulfur compounds.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2102, eff. January 1, 1985.
9VAC5-40-2850. Standard for sulfur dioxide.
No owner or other person shall cause or permit to be discharged into the atmosphere from any sulfuric acid production unit any sulfur dioxide emissions in excess of a concentration of 2000 parts per million by volume and a mass emission rate of 27 pounds per ton of 100% acid produced when elemental sulfur is used for feed material, or 3500 ppm by volume and a mass emission rate of 45 pounds per ton of 100% acid produced when other raw materials such as recycled spent acid and ores are used as feed. These emissions levels may be exceeded for a period not longer than 24 hours during start-up.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2103, eff. January 1, 1985.
9VAC5-40-2860. Standard for sulfuric acid mist.
No owner or other person shall cause or permit to be discharged into the atmosphere from any sulfuric acid production unit any sulfuric acid mist emissions in excess of 0.5 pound per ton of sulfuric acid produced, the production being expressed as 100% H2SO4.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2104, eff. January 1, 1985.
9VAC5-40-2870. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2105, eff. January 1, 1985.
9VAC5-40-2880. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2106, eff. January 1, 1985.
9VAC5-40-2890. Standard for odor.
The provision of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standard for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2107, eff. January 1, 1985.
9VAC5-40-2900. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2108, eff. January 1, 1985.
9VAC5-40-2910. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2109, eff. January 1, 1985.
9VAC5-40-2920. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2110, eff. January 1, 1985.
9VAC5-40-2930. Monitoring.
A. The provisions of 9VAC5-40-40 (Monitoring) apply.
B. Unless otherwise approved by the board, owners of sulfuric acid production units specified in subsection C of this section shall install, calibrate, maintain and operate systems for continuously monitoring and recording specified emissions in accordance with 9VAC5-40-40 and 9VAC5-40-41.
C. Sulfuric acid production units of greater than 300 tons per day production capacity (the production being expressed as 100% acid) shall be monitored for sulfur dioxide emissions.
D. The pollutant gas used to prepare calibration gas mixtures under paragraph 2.1, Performance Specifications 2 of Appendix B of 40 CFR 60 and for calibration checks under 9VAC5-40-41 shall be sulfur dioxide (SO2). Reference Method 8 shall be used for conducting monitoring system performance evaluations under of 9VAC5-40-41 except that only the sulfur dioxide portion of the Reference Method 8 results shall be used. The span shall be set at 1,000 ppm of sulfur dioxide.
E. The owner shall establish a conversion factor for the purpose of converting monitoring data into units of the applicable standard (lb/short ton). The conversion factor shall be determined, as a minimum, three times daily by measuring the concentration of sulfur dioxide entering the converter using suitable methods (e.g., the Reich Test, "Atmospheric Emissions from Sulfuric Acid Manufacturing Processes," see 9VAC5-20-21) and calculating the appropriate conversion factor for each eight-hour period as follows:
| CF = k | (1.000 - 0.15r) |
| (r - s) |
where:
CF = conversion factor (lb/short ton per ppm).
k = constant derived from material balance. For determining CF in English units, k = 0.1306.
r = percentage of sulfur dioxide by volume entering the gas converter. Appropriate corrections must be made for air injection plants subject to the approval of the board.
s = percentage of sulfur dioxide by volume in the emission to the atmosphere determined by the continuous monitoring system.
F. The average sulfur dioxide concentration in the flue gases shall be multiplied by the conversion factor to obtain the average sulfur dioxide emissions in units of the applicable standard. The owner shall record all conversion factors and values under subsection E of this section from which they were computed (i.e., CF, r, and s).
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2111, eff. January 1, 1985; amended, Virginia Register Volume 18, Issue 7, eff. February 1, 2002.
9VAC5-40-2940. Notification, records and reporting.
A. The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
B. For the purpose of reports under 9VAC5-40-50 C, periods of excess emissions that shall be reported are defined as any three-hour period (or the arithmetic average of three consecutive one-hour periods) during which the integrated average sulfur dioxide emissions exceeds the applicable standard under 9VAC5-40-2850.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2112, eff. January 1, 1985.
9VAC5-40-2950. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2113, eff. January 1, 1985.
9VAC5-40-2960. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2114, eff. January 1, 1985.
9VAC5-40-2970. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2115, eff. January 1, 1985.
Article 22
Emission Standards for Sulfur Recovery Operations (Rule 4-22)
9VAC5-40-2980. Applicability and designation of affected facility.
Article 22
Emission Standards for Sulfur Recovery Operations (Rule 4-22)
A. The affected facility to which the provisions of this article apply is each sulfur recovery operation.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2201, eff. January 1, 1985.
9VAC5-40-2990. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Production rate" means the weight of final product obtained per hour of operation. If the rate or product going to storage can vary, the production rate shall be determined by calculation from the feed rates of raw material.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2202, eff. January 1, 1985.
9VAC5-40-3000. Standard for sulfur dioxide.
No owner or other person shall cause or permit to be discharged into the atmosphere from any sulfur recovery operation any sulfur dioxide emissions in excess of a concentration of 8000 parts per million by volume and in excess of the mass emission rate specified in Table 4-22.
TABLE 4-22 | |
Sulfur Production Rate | Maximum Allowable S02 Mass Emission Rate |
50 or less | 415 |
100 | 830 |
200 | 1660 |
300 | 2490 |
400 | 3320 |
500 or more | 4150 |
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2203, eff. January 1, 1985.
9VAC5-40-3010. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2204, eff. January 1, 1985.
9VAC5-40-3020. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2205, eff. January 1, 1985.
9VAC5-40-3030. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2206, eff. January 1, 1985.
9VAC5-40-3040. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2207, eff. January 1, 1985.
9VAC5-40-3050. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2208, eff. January 1, 1985.
9VAC5-40-3060. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2209, eff. January 1, 1985.
9VAC5-40-3070. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2210, eff. January 1, 1985.
9VAC5-40-3080. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2211, eff. January 1, 1985.
9VAC5-40-3090. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2212, eff. January 1, 1985.
9VAC5-40-3100. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2213, eff. January 1, 1985.
9VAC5-40-3110. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2214, eff. January 1, 1985.
Article 23
Emission Standards for Nitric Acid Production Units (Rule 4-23)
9VAC5-40-3120. Applicability and designation of affected facility.
Article 23
Emission Standards for Nitric Acid Production Units (Rule 4-23)
A. The affected facility to which the provisions of this article apply is each nitric acid production unit.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2301, eff. January 1, 1985.
9VAC5-40-3130. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Nitric acid production unit" means any facility producing nitric acid 30 to 70% in strength by either the pressure or atmospheric pressure process.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2302, eff. January 1, 1985.
9VAC5-40-3140. Standard for nitrogen oxides.
No owner or other person shall cause or permit to be discharged into the atmosphere from any nitric acid production unit any emissions of nitrogen oxides (expressed as nitrogen dioxide) in excess of 5.5 pounds per ton of 100% acid produced.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2303, eff. January 1, 1985.
9VAC5-40-3150. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2304, eff. January 1, 1985.
9VAC5-40-3160. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2305, eff. January 1, 1985.
9VAC5-40-3170. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2306, eff. January 1, 1985.
9VAC5-40-3180. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2307, eff. January 1, 1985.
9VAC5-40-3190. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2308, eff. January 1, 1985.
9VAC5-40-3200. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2309, eff. January 1, 1985.
9VAC5-40-3210. Monitoring.
A. The provisions of 9VAC5-40-40 (Monitoring) apply.
B. Unless otherwise approved by the board, owners of existing sources specified in subsection C of this section shall install, calibrate, maintain and operate systems for continuously monitoring and recording emissions of specified pollutants.
C. Nitric acid plants of greater than 300 tons per day production capacity (the production capacity being expressed as 100% acid) shall be monitored for nitrogen oxides emissions.
D. The pollutant gas used to prepare calibration gas mixtures under paragraph 2.1, Performance Specification 2 of Appendix B of 40 CFR 60 and for calibration checks under 9VAC5-40-41 shall be nitrogen dioxide (NO2). The span shall be set at 500 ppm of nitrogen dioxide. Reference Method 7 shall be used for conducting monitoring system performance evaluations under 9VAC5-40-41.
E. The owner shall establish a conversion factor for the purpose of converting monitoring data into units of the applicable standard (lb/short ton). The conversion factor shall be established by measuring emissions with the continuous monitoring system concurrent with measuring emissions with the applicable reference method tests. Using only that portion of the continuous monitoring emission data that represents emission measurements concurrent with the reference method test periods, the conversion factor shall be determined by dividing the reference method test data average by the monitoring data averages to obtain a ratio expressed in units of the applicable standard to units of the monitoring data, i.e., lb/short ton per ppm. The conversion factor shall be reestablished during any emission test under 9VAC5-40-30 or any continuous monitoring system performance evaluation under 9VAC5-40-41. The average nitrogen oxides concentration in the flue gases shall be multiplied by the conversion factor to obtain the average nitrogen oxides emissions in the units of the applicable standard.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2310, eff. January 1, 1985.
9VAC5-40-3220. Notification, records and reporting.
A. The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
B. The owner shall record the production rate and hours of operation.
C. For the purpose of reports required under 9VAC5-40-50 C, periods of excess emissions that shall be reported are defined as any three-hour period during which the average nitrogen oxides emissions (arithmetic average of three contiguous one-hour periods) exceed the standard under 9VAC5-40-3140.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2311, eff. January 1, 1985.
9VAC5-40-3230. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2312, eff. January 1, 1985.
9VAC5-40-3240. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2313, eff. January 1, 1985.
9VAC5-40-3250. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2314, eff. January 1, 1985.
Article 24
Emission Standards for Solvent Metal Cleaning Operations Using Nonhalogenated Solvents (Rule 4-24)
9VAC5-40-3260. Applicability and designation of affected facility.
Article 24
Emission Standards for Solvent Metal Cleaning Operations Using Nonhalogenated Solvents (Rule 4-24)
A. The affected facility to which the provisions of this article apply is each solvent metal cleaning operation using nonhalogenated solvents, including, but not limited to, cold or vapor degreasing at service stations; motor vehicle repair shops; automobile dealerships; machine shops; and any other metal refinishing, cleaning, repair, or fabrication facility.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206. They do not apply to sources in the Northern Virginia volatile organic compound emissions control area designated in 9VAC5-20-206. These sources are subject to Article 47 (9VAC5-40-6820 et seq.). of this part.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from VR120-04-2401, eff. July 1, 1991; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996; Volume 13, Issue 10, eff. April 1, 1997; Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-3270. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Cold cleaning" means the batch process of cleaning and removing foreign matter from metal surfaces by spraying, brushing, flushing or immersion while maintaining the solvent below its boiling point. Wipe cleaning is not included in this definition.
"Conveyorized degreasing" means the continuous process of cleaning and removing foreign matter from metal surfaces by operating with either cold or vaporized solvents.
"Freeboard height"
a. For cold cleaners, the distance from the liquid solvent level in the degreaser tank to the lip of the tank.
b. For open top vapor degreasers, the distance from the solvent-to-air interface in the tank to the lip of the tank.
c. For conveyerized degreasers, the distance from the solvent-to-air interface to the bottom of the entrance or exit opening, whichever is lower.
"Freeboard ratio" means the freeboard height divided by the width of the degreaser.
"Lower explosive limit" means the lower limit of flammability of a gas or vapor at ordinary ambient temperatures expressed in percent of the gas or vapor in air by volume.
"Nonhalogenated solvent" means any solvent other than methylene chloride, perchloroethylene, trichloroethylene, 1,1,1- trichloroethane, carbon tetrachloride, or chloroform. Nonhalogenated solvents may include trace quantities of halogenated solvents which are:
a. Unintended residues in recycled solvents, or
b. Unintended impurities resulting from chemical reaction in the manufacturing process.
"Open top vapor degreasing" means the batch process of cleaning and removing foreign matter from metal surfaces by condensing hot solvent vapor on the colder metal parts.
"Solvent" means organic materials which are liquid at standard conditions and which are used as dissolvers, viscosity reducers or cleaning agents.
"Solvent metal cleaning" means the process of cleaning foreign matter from metal surfaces by cold cleaning or open top vapor degreasing or conveyorized degreasing.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2402, eff. January 1, 1985; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-3280. Standard for volatile organic compounds.
A. Conveyorized degreasing.
1. No owner or other person shall use or permit the use of any conveyorized degreaser unless such degreaser is equipped with a control method that will remove, destroy or prevent the discharge into the atmosphere of at least 70% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subdivision A 1 of this section by use of the methods in 9VAC5-40-3290 A and D will be acceptable to the board.
B. Open top vapor degreasing.
1. No owner or other person shall use or permit the use of any open top vapor degreaser unless such degreaser is equipped with a control method that will remove, destroy or prevent the discharge into the atmosphere of at least 75% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subdivision B 1 of this section by use of the methods in 9VAC5-40-3290 B and D will be acceptable to the board.
C. Cold cleaning.
1. No owner or other person shall use or permit the use of any cold cleaner unless such cleaner is equipped with a control method that will remove, destroy or prevent the discharge into the atmosphere of at least 85% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subdivision C 1 of this section by use of the methods in 9VAC5-40-3290 C and D will be acceptable to the board.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2403, eff. July 1, 1991; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-3290. Control technology guidelines.
A. Conveyorized degreasing.
1. Control requirements.
a. The degreaser (if the air/vapor interface is larger than 20 ft2) should be equipped with one of the following vapor control methods:
(1) Refrigerated chiller (a secondary set of condensing coils operating with a coolant of less than 40°F).
(2) Carbon adsorption system, with ventilation of 50 cfm/ft2 or greater of conveyor opening area (when down-time covers are open), and exhausting less than 25 ppm of solvent by volume averaged over a complete adsorption cycle.
(3) Any method of equal or greater control efficiency to the methods in subdivisions A 1 a (1) and (2) of this section, provided such method is approved by the board.
b. The degreaser should be equipped with either a drying tunnel, or other means such as rotating (tumbling) basket, sufficient to prevent cleaned parts from carrying out solvent liquid or vapor.
c. The degreaser should be equipped with all of the following control devices:
(1) A device to prevent heat input unless there is adequate coolant.
(2) The spray shall be equipped with a device that will prevent spraying unless the degreaser is operating normally.
(3) A device to shut off the heat if the vapor level rises above a predetermined level.
d. Entrances and exits should silhouette work loads so that the average clearance (between the largest parts and the edge of the degreaser opening) is either four inches or 10% of the width of the opening, whichever is less.
e. Covers should be provided for closing off the entrance and exit during shutdown, heat-up and cool-down.
2. Operating requirements.
a. Exhausting ventilation should not exceed 65 cfm/ft2 of degreaser open area, unless necessary to meet the requirements of any regulations promulgated by the U.S. Occupational Safety and Health Administration. Fans shall not be used near the degreaser opening.
b. Carry-out vapor losses should be minimized by racking parts to allow full drainage and maintaining vertical conveyor speed at less than 11 ft/min.
c. Waste solvent should not be disposed of or transferred to another party such that greater than 20% of the waste (by weight) can evaporate into the atmosphere. Waste solvent should only be stored in closed containers.
d. Solvent leaks should be repaired immediately or the degreaser should be shutdown.
e. Water should not be visibly detectable in the solvent exiting the water separator.
f. Down-time cover should be placed over entrances and exits of conveyorized degreaser immediately after the conveyor and exhaust are shutdown and removed just before they are started up.
B. Open top vapor degreasing.
1. Control requirements.
a. Covers should be provided that can be opened and closed easily without disturbing the vapor zone.
b. The degreaser should be equipped with all of the following control devices:
(1) A device to prevent heat input unless there is adequate coolant.
(2) The spray should be equipped with a method that will prevent spraying unless the degreaser is operating normally.
c. Degreaser should be equipped with one of the following vapor control methods:
(1) Freeboard ratio equal to or greater than 0.75. If the open area is larger than 10 ft2, the cover should be powered.
(2) Refrigerated chiller (a secondary set of condensing coils operating with a coolant of less than 40°F).
(3) Enclosed design (cover or door opens only when the dry part is actually entering or exiting the degreaser).
(4) Carbon adsorption system, with ventilation of 50 cfm/ft2 or greater of air/vapor area (when cover is open), and exhausting less than 25 ppm solvent by volume averaged over one complete adsorption cycle.
(5) Any method of equal or greater control efficiency to the methods in subdivisions B 1 c (1) through (4) of this section, provided such method is approved by the board.
d. A permanent label, summarizing operating procedures in subdivisions B 2 a through f of this section, should be placed in a conspicuous location on or near the degreaser.
2. Operating requirements.
a. The cover should be kept closed at all times except when processing work loads through the degreaser.
b. Carry-out vapor losses should be minimized by:
(1) Racking parts to allow full drainage;
(2) Moving parts in and out of the degreaser at less than 11 ft/min;
(3) Degreasing the work load in the vapor zone at least 30 seconds or until condensation ceases, whichever is longer;
(4) Tipping out any pools of solvent on the cleaned parts before removal; and
(5) Allowing parts to dry within the degreaser for at least 15 seconds or until visually dry, whichever is longer.
c. Porous or absorbent materials, such as cloth, leather, wood or rope should not be degreased.
d. Work loads should not occupy more than half of the degreaser's open top area.
e. The vapor level should not drop more than four inches when the work load enters the vapor zone. However, for certain specific solvent vapor degreasing operations where of necessity very large masses are required to be degreased at one time, such as large castings and fabricated assemblies, the manufacturers design should accommodate a drop of the vapor-air interface of more than four inches. This introduction of such large masses of necessity causes significant vapor-air interface drop and so the problem must be resolved by engineering of the degreaser in these cases rather than by limiting the amount of air-vapor interface drop.
f. Spraying above the vapor level should not be done.
g. Solvent leaks should be repaired immediately or the degreaser shutdown.
h. Waste solvent, still, and sump bottoms shall be collected and stored in closed containers. The closed containers may contain a device that would allow pressure relief, but would not allow liquid solvent to drain from the container.
i. Exhaust ventilation should not exceed 65 cfm/ft2 of degreaser open area, unless necessary to meet OSHA requirements. Fans should not be used near the degreaser opening.
j. Water should not be visually detectable in solvent exiting the water separator.
C. Cold cleaning.
1. Control requirements.
a. Covers or enclosed remote reservoirs should be provided. Covers should be designed so that they can be easily operated with one hand. (Covers for larger degreasers may require mechanical assistance, by spring loading, counterweighting or powered systems). Enclosed remote reservoirs should be designed such that they provide reduction effectiveness equivalent to that of a cover.
b. External or internal drainage facilities should be provided to collect and return the solvent to a closed container or a solvent cleaning machine. If a solvent volatility is greater than 0.6 psi measured at 100°F, then the drainage facilities should be internal so that parts are enclosed under the cover while draining. Drainage facilities may be external for applications where an internal type cannot fit into the cleaning system.
c. A permanent label, summarizing the operating procedures in subdivisions C 2 a through c of this section, should be placed in a conspicuous location on or near the degreaser.
d. If used, the solvent spray should be a solid, fluid stream (not a fine, atomized or shower type spray) and at a pressure which does not cause excessive splashing.
e. If a solvent volatility is greater than 0.6 psi measured at 100°F, or if solvent is heated above 120°F, then the degreaser (if the open area is greater than 20 ft2) should be equipped with one of the following vapor control methods:
(1) Freeboard ratio that is equal to or greater than 0.7.
(2) Water cover (solvent should be insoluble in and heavier than water).
(3) Refrigerated chiller (a secondary set of condensing coils operating with a coolant of less than 40°F).
(4) Carbon adsorption system, with ventilation of 50 cfm/ft2 or greater of air/vapor area (when down-time covers are open), and exhausting less than 25 ppm of solvent by volume averaged over a complete adsorption cycle.
(5) Any method of equal or greater control efficiency to the methods in subdivisions C 1 e (1) through (4) of this section, provided such method is approved by the board.
2. Operating requirements.
a. Waste solvent should not be disposed of or transferred to another party, such that greater than 20% of the waste (by weight) can evaporate into the atmosphere. Store waste solvent only in closed containers.
b. The degreaser cover should be closed whenever not handling parts in the cleaner.
c. Cleaned parts should drain for at least 15 seconds or until dripping ceases.
D. Disposal of waste solvent from solvent metal cleaning operations should be by one of the following methods:
1. Reclamation (either by outside services or in-house).
2. Incineration.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2404, eff. July 1, 1991; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-3300. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2405, eff. January 1, 1985.
9VAC5-40-3310. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2406, eff. January 1, 1985.
9VAC5-40-3320. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2407, eff. January 1, 1985.
9VAC5-40-3330. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2408, eff. January 1, 1985.
9VAC5-40-3340. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2409, eff. January 1, 1985.
9VAC5-40-3350. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2410, eff. January 1, 1985.
9VAC5-40-3360. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2411, eff. January 1, 1985.
9VAC5-40-3370. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2412, eff. January 1, 1985.
9VAC5-40-3380. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2413, eff. January 1, 1985.
9VAC5-40-3390. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2414, eff. January 1, 1985.
9VAC5-40-3400. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2415, eff. January 1, 1985; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
Article 25
Emission Standards for Volatile Organic Compound Storage and Transfer Operations (Rule 4-25)
9VAC5-40-3410. Applicability and designation of affected facility.
Article 25
Emission Standards for Volatile Organic Compound Storage and Transfer Operations (Rule 4-25)
A. Except as provided in subsection C of this section, the affected facility to which the provisions of this article apply is each operation involving the storage or transfer of volatile organic compounds or both.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206.
C. The provisions of this article do not apply to:
1. Facilities subject to the provisions of the emission standards for storage or transfer of petroleum liquids (Article 37 (9VAC5-40-5200 et seq.) of this chapter); or
2. Facilities using volatile organic compounds with a vapor pressure less than 1.5 pounds per square inch absolute under actual storage conditions or, in the case of filling, under actual filling conditions.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2501, eff. July 1, 1991.
9VAC5-40-3420. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"External floating roof" means a storage vessel cover in an open top tank consisting of a double deck or pontoon single deck which rests upon and is supported by the liquid being contained and is equipped with a closure seal or seals to close the space between the roof edge and tank shell.
"Internal floating roof" means a cover or roof in a fixed roof tank which rests upon or is floated upon the liquid being contained and is equipped with a closure seal or seals to close the space between the roof edge and tank shell.
"Liquid-mounted" means a primary seal mounted so the bottom of the seal covers the liquid surface between the tank shell and the floating roof.
"Submerged fill pipe" means any fill pipe the discharge opening of which is entirely submerged when the liquid level is six inches above the bottom of the tank; or, when applied to a tank which is loaded from the side, any fill pipe the discharge opening of which is entirely submerged when at the minimum operating level.
"Vapor-mounted" means a primary seal mounted so there is an annular vapor space underneath the seal. The annular vapor space is bounded by the bottom of the primary seal, the tank shell, the liquid surface, and the floating roof.
"Vapor tight" means capable of holding a pressure of 18 inH20 and a vacuum of 6 inH20 without sustaining a pressure change of more than 3 inH20 in five minutes.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2502, eff. July 1, 1985.
9VAC5-40-3430. Standard for volatile organic compounds.
A. Filling of storage tanks.
1. No owner or other person shall use or permit the use of any stationary storage tank for storage of any volatile organic compound unless such tank is equipped with a control method that will remove, destroy or prevent the discharge into the atmosphere of at least 60% by weight of volatile organic compound emissions during the filling of such tank.
2. Achievement of the emission standard in subsection A 1 of this section by use of the methods in 9VAC5-40-3440 A will be acceptable to the board.
3. Exempted from the provisions of this subsection are stationary storage tanks with a storage capacity of 2,000 gallons or less.
B. Volatile organic compound storage - fixed roof tanks.
1. No owner or other person shall use or permit the use of any fixed roof tank for storage of volatile organic compounds unless such tank is equipped with a control method which will remove, destroy or prevent the discharge into the atmosphere of at least 90% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subsection B 1 of this section by use of control methods in 9VAC5-40-3440 B will be acceptable to the board.
3. Exempted from the provisions of this subsection are stationary storage tanks with a storage capacity of 40,000 gallons or less.
4. The owner of a fixed roof tank subject to the provisions of subsection B 1 of this section shall:
a. When the fixed roof tank is equipped with an internal floating roof, perform a visual inspection annually of the floating cover through the roof hatches, to ascertain compliance with the specifications in subsection B 4 (1) and (2).
(1) The cover should be uniformly floating on or above the liquid and there should be no visible defects in the surface of the cover or liquid accumulated on the cover.
(2) The seal must be intact and uniformly in place around the circumference of the cover between the cover and tank wall.
b. Perform a complete inspection of the cover and seal and record the condition of the cover and seal when the tank is emptied for nonoperational reasons such as maintenance, an emergency, or other similar purposes.
c. Maintain records of the average monthly storage temperature and true vapor pressure of the liquid as stored, and the results of the inspection performed under the provisions of subsection B 4 a and b of this section.
C. Volatile organic compound storage - floating roof tanks.
1. No owner or other person shall use or permit the use of any floating roof tank for storage of volatile organic compounds, unless such tank is equipped with a control method which will remove, destroy or prevent the discharge into the atmosphere of at least 90% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subsection C 1 of this section by use of methods in 9VAC5-40-3440 C will be acceptable to the board.
3. Exempted from the provisions of this subsection are stationary storage tanks with a storage capacity of 40,000 gallons or less.
4. The owner of a floating roof tank subject to the provisions of subsection C 1 of this section shall:
a. Perform routine inspections annually which shall include a visual inspection of the secondary seal gap.
b. When the floating roof is equipped with a vapor-mounted primary seal, measure the secondary seal gap annually in accordance with subsections C 4 b (1) and (2) of this section.
(1) Physically measuring the length and width of all gaps around the entire circumference of the secondary seal in each place where a 1/8 inch uniform diameter probe passes freely (without forcing or binding against the seal) between the seal and tank wall; and
(2) Summing the area of the individual gaps.
c. Maintain records of the types of volatile organic compounds stored, the maximum true vapor pressure of the liquid as stored, and the results of the inspections performed under the provisions of subsection C 4 a and b of this section.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2503, eff. July 1, 1991.
9VAC5-40-3440. Control technology guidelines.
A. Filling of storage tanks. The tank should be a pressure tank maintaining working pressure sufficient at all times to prevent vapor loss to the atmosphere, or be designed and equipped with one of the following vapor control systems:
1. Filling of the tank through the use of a submerged fill pipe.
2. Any system of equal or greater control efficiency to the system in subsection A 1 of this section, provided such system is approved by the board.
B. Volatile organic compound storage - fixed roof tanks.
1. The tank should be a pressure tank maintaining working pressure sufficient at all times to prevent vapor loss to the atmosphere, or be designed and equipped with one of the following vapor control systems:
a. An internal floating roof resting on the surface of the liquid contents and equipped with a closure seal, or seals, to close the space between the roof edge and tank shell. All tank gauging and sampling devices should be vapor tight except when gauging or sampling is taking place.
b. Any system of equal or greater control efficiency to the system in subsection B 1 a of this section, provided such system is approved by the board.
2. There should be no visible holes, tears or other openings in the seal or any seal fabric.
3. All openings, except stub drains, should be equipped with a cover, seal or lid. The cover, seal or lid should be in a closed position at all times except when the device is in actual use. Automatic bleeder vents should be closed at all times except when the roof is floated off or landed on the roof leg supports. Rim vents, if provided should be set to open when the roof is being floated off the roof leg supports or at the manufacturer's recommended setting.
4. The exterior aboveground surfaces (exposed to sunlight) should be painted white, light pastels or light metallic and such exterior paint should be periodically maintained in good condition. Repainting may be performed during normal maintenance periods.
C. Volatile organic compound storage - floating roof tanks.
1. The tank should be designed and equipped with one of the following vapor control systems:
a. An external floating roof resting on the surface of the liquid contents and equipped with a seal closure device (meeting the specifications set forth in subsection C 2 and 3 of this section) to close the space between the roof edge and tank shell. All tank gauging and sampling devices should be vapor tight except when gauging or sampling is taking place.
b. Any system of equal or greater control efficiency to the system in subsection C 1 a of the section, provided such system is approved by the board.
2. Unless the tank is a welded tank fitted with a metallic-type shoe seal which has a secondary seal from the top of the shoe seal to the tank wall (a shoe-mounted secondary), the tank should be fitted with a continuous secondary seal extending from the floating roof to the tank wall (a rim-mounted secondary) if:
a. The tank is a welded tank, the true vapor pressure of the contained liquid is 4.0 psi or greater, and the primary seal is one of the following:
(1) A metallic-type shoe seal.
(2) A liquid-mounted foam seal.
(3) A liquid-mounted liquid-filled type seal.
(4) Any other seal closure device which can be demonstrated equivalent to the primary seals specified in subsection C 2 a (1) through (3) of this section.
b. The tank is a riveted tank, the true vapor pressure of the contained liquid is 1.5 psi, or greater, and the seal closure device is as described in subsection C 2 a of this section.
c. The tank is a welded or riveted tank, the true vapor pressure of the contained liquid is 1.5 psi, or greater, and the primary seal is vapor mounted. When such primary seal closure device can be demonstrated equivalent to the primary seals described in subsection C 2 a of this section the provisions of that subsection apply.
3. The seal closure devices should meet the following requirements:
a. There should be no visible holes, tears or other openings in the seal or any seal fabric.
b. The seal should be intact and uniformly in place around the circumference of the floating roof between the floating roof and the tank wall.
c. The areas where the gap between the secondary seal, installed pursuant to subsection C 2 c of this section, and the tank wall exceeds 1/8 inch in width shall be calculated in square inches. The sum of all such areas shall not exceed 1.0 square inch per foot of tank diameter.
4. All openings, except for automatic bleeder vents, rim space vents and leg sleeves, should provide a projection below the liquid surface. All openings, except stub drains, should be equipped with a cover, seal or lid. The cover, seal or lid should be in a closed position at all times except when the device is in actual use. Automatic bleeder vents should be closed at all times except when the roof is floated off or landed on the roof leg supports. Rim vents, if provided, should be set to open when the roof is being floated off the roof leg supports or at the manufacturer's recommended setting. Any emergency roof drain should be provided with a slotted membrane fabric cover or equivalent cover that covers at least 90% of the area of the opening.
5. The exterior above ground surfaces (exposed to sunlight) should be painted white, light pastels, or light metallic and such exterior paint should be periodically maintained in good condition. Repainting may be performed during normal maintenance periods.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2504, eff. July 1, 1991.
9VAC5-40-3450. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2505, eff. January 1, 1985.
9VAC5-40-3460. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2506, eff. January 1, 1985.
9VAC5-40-3470. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2507, eff. January 1, 1985.
9VAC5-40-3480. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2508, eff. January 1, 1985.
9VAC5-40-3490. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2509, eff. January 1, 1985.
9VAC5-40-3500. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2510, eff. January 1, 1985.
9VAC5-40-3510. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2511, eff. January 1, 1985.
9VAC5-40-3520. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2512, eff. January 1, 1985.
9VAC5-40-3530. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2513, eff. January 1, 1985.
9VAC5-40-3540. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2514, eff. January 1, 1985.
9VAC5-40-3550. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate Regional Office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2515, eff. January 1, 1985.
Article 26
Emission Standards for Large Appliance Coating Application Systems (Rule 4-26) [Repealed]
9VAC5-40-3560. (Repealed.)
Historical Notes
Derived from VR120-04-2601, eff. July 1, 1991; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-3570. (Repealed.)
Historical Notes
Derived from VR120-04-2602, eff. July 1, 1991; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-3580. (Repealed.)
Historical Notes
Derived from VR120-04-2603, eff. July 1, 1991; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-3590. (Repealed.)
Historical Notes
Derived from VR120-04-2604, eff. July 1, 1991; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-3600. (Repealed.)
Historical Notes
Derived from VR120-04-2605, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-3610. (Repealed.)
Historical Notes
Derived from VR120-04-2606, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-3620. (Repealed.)
Historical Notes
Derived from VR120-04-2607, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-3630. (Repealed.)
Historical Notes
Derived from VR120-04-2608, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-3640. (Repealed.)
Historical Notes
Derived from VR120-04-2609, eff. July 1, 1991; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-3650. (Repealed.)
Historical Notes
Derived from VR120-04-2610, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-3660. (Repealed.)
Historical Notes
Derived from VR120-04-2611, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-3670. (Repealed.)
Historical Notes
Derived from VR120-04-2612, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-3680. (Repealed.)
Historical Notes
Derived from VR120-04-2613, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-3690. (Repealed.)
Historical Notes
Derived from VR120-04-2614, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
9VAC5-40-3700. (Repealed.)
Historical Notes
Derived from VR120-04-2615, eff. January 1, 1985; repealed, Virginia Register Volume 40, Issue 14, April 11, 2024.
Article 27
Emission Standards for Magnet Wire Coating Application Systems (Rule 4-27)
9VAC5-40-3710. Applicability and designation of affected facility.
Article 27
Emission Standards for Magnet Wire Coating Application Systems (Rule 4-27)
A. Except as provided in subsection C of this section, the affected facility to which the provisions of this article apply is each magnet wire coating application system.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206.
C. The provisions of this article do not apply to coating application systems used exclusively for determination of product quality and commercial acceptance provided:
1. The operation is not an integral part of the production process;
2. The emissions from all product quality coating application systems do not exceed 400 pounds in any 30 day period; and
3. The exemption is approved by the board.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2701, eff. July 1, 1991.
9VAC5-40-3720. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Application area" means the area where the coating is applied by spraying, dipping or flow coating techniques.
"Coating applicator" means an apparatus used to apply a surface coating.
"Coating application system" means any operation or system where a surface coating of one type or function is applied, dried or cured and which is subject to the same emission standard. May include any equipment which applies, conveys, dries or cures a surface coating, including, but not limited to, spray booths, flow coaters, flashoff areas, air dryers, drying areas and ovens. It is not necessary for a coating application system to have an oven, flashoff area or drying area to be included in this definition.
"Flashoff area" means the space between the application area and the oven.
"Magnet wire coating" means the process of applying a coating, electrically insulating varnish or enamel to aluminum or copper wire for use in electrical machinery.
"Oven" means a chamber within which heat is used to bake, cure, polymerize or dry a surface coating or any combination of those.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2702, eff. July 1, 1991.
9VAC5-40-3730. Standard for volatile organic compounds.
A. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 1.7 pounds per gallon of coating, excluding water, as delivered by the coating applicator.
B. Achievement of the emission standard in subsection A of this section by use of methods in 9VAC5-40-3740 will be acceptable to the board.
C. No owner or other person shall use any coating system or equipment unless reasonable precautions are taken to minimize the discharge of emissions from cleaning or purging operations. Reasonable precautions may include the following:
1. The use of capture or control devices or both.
2. The use of detergents, high pressure water, or other nonvolatile cleaning methods.
3. The minimization of the quantity of volatile organic compounds used to clean lines of equipment.
4. The adjustment of production schedules to minimize coating changes thereby reducing the need for frequent cleaning or purging of a system.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2703, eff. July 1, 1991.
9VAC5-40-3740. Control technology guidelines.
The control technology should consist of one or more of the following:
1. Use of waterborne coatings.
2. Use of powder coatings.
3. Incineration.
4. Any technology of equal or greater control efficiency when compared to the use of coating complying with 9VAC5-40-3730 A, provided such technology is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2704, eff. July 1, 1991.
9VAC5-40-3750. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2705, eff. January 1, 1985.
9VAC5-40-3760. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2706, eff. January 1, 1985.
9VAC5-40-3770. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2707, eff. January 1, 1985.
9VAC5-40-3780. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2708, eff. January 1, 1985.
9VAC5-40-3790. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. The emission standards in 9VAC5-40-3730 apply coating by coating or to the volume weighted average of coatings where the coatings are used on a single coating application system and the coatings are the same type or perform the same function. Such averaging shall not exceed 24 hours.
C. Compliance determinations for control technologies not based on compliant coatings (i.e., coating formulation alone) shall be based on the applicable standard in terms of pounds of volatile organic compounds per gallon solids or pounds of volatile organic compounds per gallon solids applied according to the applicable procedure in 9VAC5-20-121.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2709, eff. July 1, 1991.
9VAC5-40-3800. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2710, eff. January 1, 1985.
9VAC5-40-3810. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2711, eff. January 1, 1985.
9VAC5-40-3820. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2712, eff. January 1, 1985.
9VAC5-40-3830. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2713, eff. January 1, 1985.
9VAC5-40-3840. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2714, eff. January 1, 1985.
9VAC5-40-3850. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2715, eff. January 1, 1985.
Article 28
Emission Standards for Automobile and Light Duty Truck Coating Application Systems (Rule 4-28)
9VAC5-40-3860. Applicability and designation of affected facility.
Article 28
Emission Standards for Automobile and Light Duty Truck Coating Application Systems (Rule 4-28)
A. Except as provided in subsection C of this section, the affected facility to which the provisions of this article apply is each automobile or light duty truck coating application system.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206.
C. The provisions of this article do not apply to the following:
1. Coating application systems used exclusively for determination of product quality and commercial acceptance provided:
a. The operation is not an integral part of the production process;
b. The emissions from all product quality coating application systems do not exceed 400 pounds in any 30 day period; and
c. The exemption is approved by the board.
2. Vehicle refinishing operations.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2801, eff. July 1, 1991.
9VAC5-40-3870. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Anti-chip coating" means a resilient coating applied over the prime coat and beneath the topcoat to body parts prone to chip damage for the purpose of protecting the topcoat from chipping.
"Application area" means the area where the coating is applied by spraying, dipping or flow coating techniques.
"Automobile" means any passenger car or passenger car derivative capable of seating 12 or fewer passengers.
"Carbon adsorption system" means a device containing activated carbon as the adsorbent material, an inlet and outlet for exhaust gases, and a system to regenerate the saturated adsorbent. The carbon adsorption system must provide for the proper disposal or reuse of all volatile organic compounds in the adsorbate.
"Clear coating" means a coating which lacks color and opacity or is transparent and uses the undercoat or basecoat as a reflectant base or undertone color.
"Coating applicator" means an apparatus used to apply a surface coating.
"Coating application system" means any operation or system in which a surface coating of one type or function is applied, dried or cured and which is subject to the same emission standard. May include any equipment which applies, conveys, dries or cures a surface coating, including, but not limited to, spray booths, flow coaters, flashoff areas, air dryers, drying areas and ovens. It is not necessary for a coating application system to have an oven, flashoff area or drying area to be included in this definition.
"Electrocoat primer" means the initial coating on components of automobile or light-duty truck bodies that is applied by electrode position.
"Extreme environmental conditions" means exposure to any one of the following: weather all of the time, temperatures consistently above 95°C, detergents, scouring, solvents, corrosive atmospheres or similar environmental conditions.
"Extreme performance coatings" means coatings which are required to be used by design specification on products designed for harsh exposure or extreme environmental conditions.
"Flashoff area" means the space between the application area and the oven.
"Guidecoat" means the surface coating applied over the electrocoat primer and beneath the topcoat.
"Light-duty truck" means any motor vehicle rated at 8,500 pounds gross vehicle weight or less which is designed primarily for purposes of transportation of property or is a derivative of such a vehicle; includes pickups, vans and window vans.
"Oven" means a chamber within which heat is used to bake, cure, polymerize or dry a surface coating or any combination of these.
"Topcoat" means the final coating applied to components of automobile or light-duty truck bodies.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2802, eff. July 1, 1991.
9VAC5-40-3880. Standard for volatile organic compounds.
A. Prime application.
1. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 1.2 pounds per gallon of coating, excluding water, as delivered by the coating applicator.
2. Achievement of the emission standard in subsection A 1 of this section by use of methods in 9VAC5-40-3890 A will be acceptable to the board.
B. Guidecoat application.
1. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 2.8 pounds per gallon of coating, excluding water, as delivered by the coating applicator.
2. Achievement of the emission standard in subsection B 1 of this section by use of methods in 9VAC5-40-3890 B will be acceptable to the board.
C. Topcoat application.
1. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 15.1 pounds per gallon of solids applied to the automobile or light-duty truck components or 2.8 pounds per gallon of coating, excluding water, as delivered by the coating applicator.
2. Achievement of the emission standard in subsection C 1 of this section by use of methods in 9VAC5-40-3890 C will be acceptable to the board.
D. Final repair application.
1. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 4.8 pounds per gallon of coating, excluding water, as delivered by the coating applicator.
2. Achievement of the emission standard in subsection D 1 of this section by use of methods in 9VAC5-40-3890 D will be acceptable to the board.
E. Anti-chip coating application.
1. Except as provided in subsection E 2 of this section, no owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of:
a. 3.5 pounds per gallon of coating, excluding water, delivered to a coating applicator that applies extreme performance coatings; or
b. 3.0 pounds per gallon of coating, excluding water, delivered to a coating applicator for all other coatings and coating application systems.
2. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 2.8 pounds per gallon of coating, excluding water, delivered to a coating applicator that applies anti-chip coatings to the visible surface of main body parts.
3. Achievement of the emission standard in subsections E 1 and 2 of this section by use of methods in 9VAC5-40-3890 E will be acceptable to the board.
F. The provisions of subsections A, B, and C of this section shall not be applicable to the use of wheel enamels, anti-rust coatings, and sealers or other coating operations not associated with prime, guidecoat, or topcoat application to the vehicle body.
G. No owner or other person shall use any coating application system or equipment unless reasonable precautions are taken to minimize the discharge of emissions from cleaning or purging operations. Reasonable precautions may include the following:
1. The use of capture or control devices or both;
2. The use of detergents, high pressure water, or other non-volatile cleaning methods;
3. The minimization of the quantity of volatile organic compounds used to clean lines of equipment; or
4. The adjustment of production schedules to minimize coating changes thereby reducing the need for frequent cleaning or purging of a system.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2803, eff. July 1, 1991.
9VAC5-40-3890. Control technology guidelines.
A. Prime application. The control technology should consist of one or more of the following:
1. Use of electrodeposited waterborne coatings.
2. Use of other waterborne coatings.
3. Use of lower solvent (higher solids) organic solvent-borne systems.
4. Carbon adsorption.
5. Incineration.
6. Any technology of equal or greater control efficiency when compared to the use of a coating complying with 9VAC5-40-3880 A 1, provided such technology is approved by the board.
B. Guidecoat application. The control technology should consist of one or more of the following:
1. Use of waterborne coatings;
2. Use of lower solvent (higher solids) organic solvent-borne systems;
3. Carbon adsorption; and
4. Incineration; or
5. Any technology of equal or greater control efficiency when compared to the use of a coating complying with 9VAC5-40-3880 B 1, provided such technology is approved by the board.
C. Topcoat application. The control technology should consist of one or more of the following:
1. Use of waterborne coatings;
2. Use of lower solvent (higher solids) organic solvent-borne systems;
3. Carbon adsorption; and
4. Incineration; or
5. Any technology of equal or greater control efficiency when compared to the use of a coating complying with 9VAC5-40-3880 C 1, provided such technology is approved by the board.
D. Final repair application. The control technology should consist of one or more of the following:
1. Use of lower solvent (higher solids) organic solvent borne systems;
2. Carbon adsorption; and
3. Incineration; or
4. Any technology of equal or greater control efficiency when compared to the use of a coating complying with 9VAC5-40-3880 D 1, provided such technology is approved by the board.
E. Anti-chip coating application. The control technology should consist of one or more of the following:
1. Use of electrodeposited waterborne coatings;
2. Use of other waterborne coatings;
3. Use of high solids coatings;
4. Use of powder coatings;
5. Carbon adsorption; and
6. Incineration; or
7. Any technology of equal or greater control efficiency when compared to the use of a coating complying with 9VAC5-40-3880 E 1, provided such technology is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2804, eff. July 1, 1991.
9VAC5-40-3900. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2805, eff. January 1, 1985.
9VAC5-40-3910. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2806, eff. January 1, 1985.
9VAC5-40-3920. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2807, eff. January 1, 1985.
9VAC5-40-3930. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2808, eff. January 1, 1985.
9VAC5-40-3940. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. The emission standards in 9VAC5-40-3880 apply coating by coating or to the volume weighted average of coatings where the coatings are used on a single coating application system and the coatings are the same type or perform the same function. Such averaging shall not exceed 24 hours.
C. Compliance determinations for control technologies not based on compliant coatings (i.e., coating formulation alone) shall be based on the applicable standard in terms of pounds of volatile organic compounds per gallon solids or pounds of volatile organic compounds per gallon solids applied according to the applicable procedure in 9VAC5-20-121. Compliance may also be based on transfer efficiency greater than the board accepted baseline transfer efficiency if demonstrated by methods acceptable to the board according to the applicable procedure in 9VAC5-20-121.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2809, eff. January 1, 1985.
9VAC5-40-3950. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2810, eff. January 1, 1985.
9VAC5-40-3960. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2811, eff. January 1, 1985.
9VAC5-40-3970. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2812, eff. January 1, 1985.
9VAC5-40-3980. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2813, eff. January 1, 1985.
9VAC5-40-3990. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2814, eff. January 1, 1985.
9VAC5-40-4000. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2815, eff. January 1, 1985.
Article 29
Emission Standards for Can Coating Application Systems (Rule 4-29)
9VAC5-40-4010. Applicability and designation of affected facility.
Article 29
Emission Standards for Can Coating Application Systems (Rule 4-29)
A. Except as provided in subsection C of this section, the affected facility to which the provisions of this article apply is each can coating application system.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206.
C. The provisions of this article do not apply to coating application systems used exclusively for determination of product quality and commercial acceptance provided:
1. The operation is not an integral part of the production process;
2. The emissions from all product quality coating application systems do not exceed 400 pounds in any 30 day period; and
3. The exemption is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2901, eff. July 1, 1991.
9VAC5-40-4020. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Application area" means the area where the coating is applied by spraying, dipping or flow coating techniques.
"Carbon adsorption system" means a device containing activated carbon as the adsorbent material, an inlet and outlet for exhaust gases, and a system to regenerate the saturated adsorbent. The carbon adsorption system must provide for the proper disposal or reuse of all volatile organic compounds in the adsorbate.
"Coating applicator" means an apparatus used to apply a surface coating.
"Coating application system" means any operation or system where a surface coating of one type or function is applied, dried or cured and which is subject to the same emission standard. May include any equipment which applies, conveys, dries or cures a surface coating, including, but not limited to, spray booths, flow coaters, flashoff areas, air dryers, drying areas and flashoff area or drying area to be included in this definition.
"Flashoff area" means the space between the application area and the oven.
"Oven" means a chamber within which heat is used to bake, cure, polymerize or dry a surface coating or any combination of those.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2902, eff. July 1, 1991.
9VAC5-40-4030. Standard for volatile organic compounds.
A. Sheet basecoat (exterior and interior) and overvarnish; two-piece can exterior (basecoat and overvarnish).
1. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 2.8 pounds per gallon of coating, excluding water, as delivered by the coating applicator.
2. Achievement of the emission standard in subsection A 1 of this section by use of methods in 9VAC5-40-4040 A will be acceptable to the board.
B. Two-piece and three-piece can interior body spray; two-piece can exterior end (spray or roll coat).
1. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 4.2 pounds per gallon of coating, excluding water, as delivered by the coating applicator.
2. Achievement of the emission standard in subsection B 1 of this section by use of methods in 9VAC5-40-4040 B will be acceptable to the board.
C. Three-piece can side-seam spray.
1. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 5.5 pounds per gallon of coating, excluding water, as delivered by the coating applicator.
2. Achievement of the emission standard in subsection C 1 of this section by use of methods in 9VAC5-40-4040 C will be acceptable to the board.
D. End sealing compound coating.
1. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 3.7 pounds per gallon of coating, excluding water, as delivered by the coating applicator.
2. Achievement of the emission standard in subsection D 1 of this section by use of methods in 9VAC5-40-4040 D will be acceptable to the board.
E. No owner or other person shall use any coating system or equipment unless reasonable precautions are taken to minimize the discharge of emissions from cleaning or purging operations. Reasonable precautions may include the following:
1. The use of capture or control devices or both;
2. The use of detergents, high pressure water, or other non-volatile cleaning methods;
3. The minimization of the quantity of volatile organic compounds used to clean lines of equipment; and
4. The adjustment of production schedules to minimize coating changes thereby reducing the need for frequent cleaning or purging of a system.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2903, eff. July 1, 1991.
9VAC5-40-4040. Control technology guidelines.
A. Sheet basecoat (exterior and interior) and overvarnish; two-piece can exterior (basecoat and overvarnish). The control technology should consist of one or more of the following:
1. Use of electrodeposited waterborne coatings;
2. Use of ultraviolet coatings;
3. Use of high solids coatings;
4. Carbon adsorption; and
5. Incineration; or
6. Any technology of equal or greater control efficiency when compared to the use of coating complying with 9VAC5-40-4030 A 1, provided such technology is approved by the board.
B. Two-piece and three-piece can interior body spray; two-piece can exterior end (spray or roll coat). The control technology should consist of one or more of the following:
1. Use of waterborne coatings;
2. Use of powder coatings;
3. Use of high-solids coatings;
4. Carbon adsorption; and
5. Incineration; or
6. Any technology of equal or greater control efficiency when compared to the use of coating complying with 9VAC5-40-4030 B 1, provided such technology is approved by the board.
C. Three-piece can side-seam spray. The control technology should consist of one or more of the following:
1. Use of waterborne coatings;
2. Use of powder coatings; and
3. Use of high solids coatings; or
4. Any technology of equal or greater control efficiency when compared to the use of coating complying with 9VAC5-40-4030 C 1, provided such technology is approved by the board.
D. End sealing compound coating. The control technology should consist of one or more of the following:
1. Use of waterborne coatings;
2. Use of high-solids coatings; or
3. Any technology of equal or greater control efficiency when compared to the use of coating complying with 9VAC5-40-4030 D 1, provided such technology is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2904, eff. July 1, 1991.
9VAC5-40-4050. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2905, eff. January 1, 1985.
9VAC5-40-4060. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2906, eff. January 1, 1985.
9VAC5-40-4070. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2907, eff. January 1, 1985.
9VAC5-40-4080. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2908, eff. January 1, 1985.
9VAC5-40-4090. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. The emission standards in 9VAC5-40-4030 apply coating by coating or to the volume weighted average of coatings where the coatings are used on a single coating application system and the coatings are the same type or perform the same function. Such averaging shall not exceed 24 hours.
C. Compliance determinations for control technologies not based on compliant coatings (i.e., coating formulation alone) shall be based on the applicable standard in terms of pounds of volatile organic compounds per gallon solids or pounds of volatile organic compounds per gallon solids applied according to the applicable procedure in 9VAC5-20-121. Compliance may also be based on transfer efficiency greater than the board accepted baseline transfer efficiency if demonstrated by methods acceptable to the board according to the applicable procedure in 9VAC5-20-121.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2909, eff. July 1, 1991.
9VAC5-40-4100. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2910, eff. January 1, 1985.
9VAC5-40-4110. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2911, eff. January 1, 1985.
9VAC5-40-4120. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2912, eff. January 1, 1985.
9VAC5-40-4130. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2913, eff. January 1, 1985.
9VAC5-40-4140. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2914, eff. January 1, 1985.
9VAC5-40-4150. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-2915, eff. January 1, 1985.
Article 30
Emission Standards for Metal Coil Coating Application Systems (Rule 4-30)
9VAC5-40-4160. Applicability and designation of affected facility.
Article 30
Emission Standards for Metal Coil Coating Application Systems (Rule 4-30)
A. Except as provided in subsection C of this section, the affected facility to which the provisions of this article apply is each metal coil coating application system.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206.
C. The provisions of this article do not apply to coating application systems used exclusively for determination of product quality and commercial acceptance provided:
1. The operation is not an integral part of the production process;
2. The emissions from all product quality coating application systems do not exceed 400 pounds in any 30 day period; and
3. The exemption is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3001, eff. July 1, 1991.
9VAC5-40-4170. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Application area" means the area where the coating is applied by spraying, dipping or flow coating techniques.
"Coating applicator" means an apparatus used to apply a surface coating.
"Coating application system" means any operation or system wherein a surface coating of one type or function is applied, dried or cured and which is subject to the same emission standard. May include any equipment which applies, conveys, dries or cures a surface coating, including, but not limited to, spray booths, flow coaters, flashoff areas, air dryers, drying areas and ovens. It is not necessary for a coating application system to have an oven, flashoff area or drying area to be included in this definition.
"Coil coating" means the coating of any flat metal sheet or strip that comes in rolls or coils.
"Flashoff area" means the space between the application area and the oven.
"Oven" means a chamber within which heat is used to bake, cure, polymerize or dry a surface coating or any combination of those.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3002, eff. July 1, 1991.
9VAC5-40-4180. Standard for volatile organic compounds.
A. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 2.6 pounds per gallon of coating, excluding water, as delivered by the coating applicator.
B. Achievement of the emission standard in subsection A of this section by use of methods in 9VAC5-40-4190 will be acceptable to the board.
C. No owner or other person shall use any coating application system or equipment unless reasonable precautions are taken to minimize the discharge of emissions from cleaning or purging operations. Reasonable precautions may include the following:
1. The use of capture or control devices or both;
2. The use of detergents, high pressure water, or other non-volatile cleaning methods;
3. The minimization of the quantity of volatile organic compounds used to clean lines of equipment; and
4. The adjustment of production schedules to minimize coating changes thereby reducing the need for frequent cleaning or purging of a system.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3003, eff. July 1, 1991.
9VAC5-40-4190. Control technology guidelines.
Control technology should consist of one of the following:
1. Use of electrodeposited waterborne coatings;
2. Use of other waterborne coatings;
3. Use of high-solids coatings;
4. Incineration; or
5. Any technology of equal or greater control efficiency when compared to the use of a coating complying with 9VAC5-40-4180 A, provided such technology is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3004, eff. July 1, 1991.
9VAC5-40-4200. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3005, eff. January 1, 1985.
9VAC5-40-4210. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3006, eff. January 1, 1985.
9VAC5-40-4220. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3007, eff. January 1, 1985.
9VAC5-40-4230. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3008, eff. January 1, 1985.
9VAC5-40-4240. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. The emission standards in 9VAC5-40-4180 apply coating by coating or to the volume weighted average of coatings where the coatings are used on a single coating application system and the coatings are the same type or perform the same function. Such averaging shall not exceed 24 hours.
C. Compliance determinations for control technologies not based on compliant coatings (i.e., coating formulation alone) shall be based on the applicable standard in terms of pounds of volatile organic compounds per gallon solids or pounds of volatile organic compounds per gallon solids applied according to the applicable procedure in 9VAC5-20-121. Compliance may also be based on transfer efficiency greater than the board accepted baseline transfer efficiency if demonstrated by methods acceptable to the board according to the applicable procedure in 9VAC5-20-121.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3009, eff. July 1, 1991.
9VAC5-40-4250. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3010, eff. January 1, 1985.
9VAC5-40-4260. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3011, eff. January 1, 1985.
9VAC5-40-4270. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3012, eff. January 1, 1985.
9VAC5-40-4280. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3013, eff. January 1, 1985.
9VAC5-40-4290. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3014, eff. January 1, 1985.
9VAC5-40-4300. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3015, eff. January 1, 1985.
Article 31
Emission Standards for Paper and Fabric Coating Application Systems (Rule 4-31)
9VAC5-40-4310. Applicability and designation of affected facility.
Article 31
Emission Standards for Paper and Fabric Coating Application Systems (Rule 4-31)
A. Except as provided in subsections C and D of this section, the affected facility to which the provisions of this article apply is each paper or fabric coating application system or both.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206.
C. Exempted from the provisions of this article are coating plants whose emissions of volatile organic compounds are not more than 2.7 tons per year, 15 pounds per day and three pounds per hour, based on the actual emissions rate. All volatile organic compound emissions from purging or washing solvents shall be considered in applying the exemption levels specified in this subsection.
D. The provisions of this article do not apply to coating application systems used exclusively for determination of product quality and commercial acceptance provided:
1. The operation is not an integral part of the production process;
2. The emissions from all product quality coating application systems do not exceed 400 pounds in any 30 day period; and
3. The exemption is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3101, eff. July 1, 1991.
9VAC5-40-4320. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Application area" means the area where the coating is applied by spraying, dipping or flow coating techniques.
"Carbon adsorption system" means a device containing activated carbon as the adsorbent material, an inlet and outlet for exhaust gases, and a system to regenerate the saturated adsorbent. The carbon adsorption system must provide for the proper disposal or reuse of all volatile organic compounds in the adsorbate.
"Coating applicator" means an apparatus used to apply a surface coating.
"Coating application system" means any operation or system wherein a surface coating of one type or function is applied, dried or cured and which is subject to the same emission standard. May include any equipment which applies, conveys, dries or cures a surface coating, including, but not limited to, spray booths, flow coaters, flashoff areas, air dryers, drying areas and ovens. It is not necessary for a coating application system to have an oven, flashoff area or drying area to be included in this definition.
"Fabric coating" means the coating of a textile substrate by knife, roll or rotogravure coating to impart properties that are not initially present, such as strength, stability, water or acid repellency, or appearance.
"Flashoff area" means the space between the application area and the oven.
"Knife coating" means the application of a coating material to a substrate by means of drawing the substrate beneath a knife that spreads the coating evenly over the full width of the substrate.
"Oven" means a chamber within which heat is used to bake, cure, polymerize or dry a surface coating or any combination of those.
"Paper coating" means the coating of paper and pressure sensitive tapes regardless of substrate by knife, roll or rotogravure coating. Related wet coating process on plastic films and decorative coatings on metal foil are included in this definition.
"Roll coating" means the application of a coating material to a substrate by means of hard rubber or metal rolls.
"Rotogravure coating" means the application of a coating material to a substrate by means of a roll coating technique in which the pattern to be applied is etched on the coating roll. The coating material is picked up in these recessed areas and is transferred to the substrate.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3102, eff. July 1, 1991.
9VAC5-40-4330. Standard for volatile organic compounds.
A. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 2.9 pounds per gallon of coating, excluding water, as delivered by the coating applicator.
B. Achievement of the emission standard in subsection A of this section by use of methods in 9VAC5-40-4340 will be acceptable to the board.
C. The provisions of this section shall not be applicable to the production of packaging materials and to printing (graphic arts) operations to the extent provided in subsection D of this section.
D. The production of packaging materials involves two principal operations which emit volatile organic compounds: the coating and laminating of paper, film and foil, and the printing of words, designs and pictures upon webs of paper, film and foil. For the purposes of applicability of the above emission standard, coating is the application of a layer of material across any portion of the web and printing is the formation of words, designs and pictures, usually by a series of application rolls each with only partial coverage. The above emission standard applies to coating and laminating operations in the production of packaging materials, but does not apply to printing operations in the production of packaging materials and to publication rotogravure printing operations (the emission standards in Article 36 (9VAC5-40-5060 et seq.) of this chapter apply to such operations). However, all units in a machine which have both coating and printing units will be considered as performing a printing operation. A typical operation is as follows: the first unit applies a uniform background color, subsequent units print additional colors, the final unit applies a varnish overcoat. Such a machine would not be subject to the above emission standard, but would be subject to the emission standards in Article 36 (9VAC5-40-5060 et seq.) of this chapter.
E. No owner or other person shall use any coating application system or equipment unless reasonable precautions are taken to minimize the discharge or emissions from cleaning or purging operations. Reasonable precautions may include the following:
1. The use of capture or control devices or both;
2. The use of detergents, high pressure water, or other non-volatile cleaning methods;
3. The minimization of the quantity of volatile organic compounds used to clean lines of equipment; and
4. The adjustment of production schedules to minimize coating changes thereby reducing the need for frequent cleaning or purging of a system.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3103, eff. July 1, 1991.
9VAC5-40-4340. Control technology guidelines.
The control technology should consist of one of the following:
1. Use of waterborne coatings;
2. Use of high-solids coatings;
3. Use of other low solvent coatings, provided such coatings are approved by the board;
4. Carbon adsorption;
5. Incineration; or
6. Any technology of equal or greater control efficiency when compared to the use of a coating complying with 9VAC5-40-4330 A, provided such technology is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3104, eff. July 1, 1991.
9VAC5-40-4350. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3105, eff. January 1, 1985.
9VAC5-40-4360. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3106, eff. January 1, 1985.
9VAC5-40-4370. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3107, eff. January 1, 1985.
9VAC5-40-4380. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3108, eff. January 1, 1985.
9VAC5-40-4390. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. The emission standards in 9VAC5-40-4330 apply coating by coating or to the volume weighted average of coatings where the coatings are used on a single coating application system and the coatings are the same type or perform the same function. Such averaging shall not exceed 24 hours.
C. Compliance determinations for control technologies not based on compliant coatings (i.e., coating formulation alone) shall be based on the applicable standard in terms of pounds of volatile organic compounds per gallon solids or pounds of volatile organic compounds per gallon solids applied according to the applicable procedure in 9VAC5-20-121. Compliance may also be based on transfer efficiency greater than the board accepted baseline transfer efficiency if demonstrated by methods acceptable to the board according to the applicable procedure in 9VAC5-20-121.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3109, eff. July 1, 1991.
9VAC5-40-4400. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3110, eff. January 1, 1985.
9VAC5-40-4410. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3111, eff. January 1, 1985.
9VAC5-40-4420. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3112, eff. January 1, 1985.
9VAC5-40-4430. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3113, eff. January 1, 1985.
9VAC5-40-4440. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3114, eff. January 1, 1985.
9VAC5-40-4450. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3115, eff. January 1, 1985.
Article 32
Emission Standards for Vinyl Coating Application Systems (Rule 4-32)
9VAC5-40-4460. Applicability and designation of affected facility.
Article 32
Emission Standards for Vinyl Coating Application Systems (Rule 4-32)
A. Except as provided in subsection C of this section, the affected facility to which the provisions of this article apply is each vinyl coating application system.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206.
C. The provisions of this article do not apply to coating application systems used exclusively for determination of product quality and commercial acceptance provided:
1. The operation is not an integral part of the production process;
2. The emissions from all product quality application systems do not exceed 400 pounds in any 30 day period; and
3. The exemption is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3201, eff. July 1, 1991.
9VAC5-40-4470. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Application area" means the area where the coating is applied by spraying, dipping or flow coating techniques.
"Carbon adsorption system" means a device containing activated carbon as the adsorbent material, an inlet and outlet for exhaust gases, and a system to regenerate the saturated adsorbent. The carbon adsorption system must provide for the proper disposal or reuse of all volatile organic compounds in the adsorbate.
"Coating applicator" means an apparatus used to apply a surface coating.
"Coating application system" means any operation or system wherein a surface coating of one type or function is applied, dried or cured and which is subject to the same emission standard. May include any equipment which applies, conveys, dries or cures a surface coating, including, but not limited to, spray booths, flow coaters, flashoff areas, air dryers, drying areas and ovens. It is not necessary for a coating application system to have an oven, flashoff area or drying area to be included in this definition.
"Flashoff area" means the space between the application area and the oven.
"Oven" means a chamber within which heat is used to bake, cure, polymerize or dry a surface coating or any combination of those.
"Vinyl coating" means applying a decorative or protective topcoat, or printing on vinyl coated fabric or vinyl sheets.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3202, eff. July 1, 1991.
9VAC5-40-4480. Standard for volatile organic compounds.
A. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 3.8 pounds per gallon of coating, excluding water, as delivered by the coating applicator.
B. Achievement of the emission standard in subsection A of this section by use of methods in 9VAC5-40-4490 will be acceptable to the board.
C. No owner or other person shall use any coating system or equipment unless reasonable precautions are taken to minimize the discharge of emissions from cleaning or purging operations. Reasonable precautions may include the following:
1. The use of capture or control devices or both;
2. The use of detergents, high pressure water, or other nonvolatile cleaning methods;
3. The minimization of the quantity of volatile organic compounds used to clean lines of equipment; and
4. The adjustment of production schedules to minimize coating changes thereby reducing the need for frequent cleaning or purging of a system.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3203, eff. July 1, 1991.
9VAC5-40-4490. Control technology guidelines.
The control technology should consist of one of the following:
1. Use of waterborne coatings;
2. Use of high-solids coatings;
3. Carbon adsorption;
4. Incineration; or
5. Any technology of equal or greater control efficiency when compared to the use of a coating complying with 9VAC5-40-4480 A, provided such technology is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3204, eff. July 1, 1991.
9VAC5-40-4500. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3205, eff. January 1, 1985.
9VAC5-40-4510. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3206, eff. January 1, 1985.
9VAC5-40-4520. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3207, eff. January 1, 1985.
9VAC5-40-4530. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3208, eff. January 1, 1985.
9VAC5-40-4540. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. The emission standards in 9VAC5-40-4480 apply coating by coating or to the volume weighted average of coatings where the coatings are used on a single coating application system and the coatings are the same type or perform the same function. Such averaging shall not exceed 24 hours.
C. Compliance determinations for control technologies not based on compliant coatings (i.e., coating formulation alone) shall be based on the applicable standard in terms of pounds of volatile organic compounds per gallon solids or pounds of volatile organic compounds per gallon solids applied according to the applicable procedure in 9VAC5-20-121. Compliance may also be based on transfer efficiency greater than the board accepted baseline transfer efficiency if demonstrated by methods acceptable to the board according to the applicable procedure in 9VAC5-20-121.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3209, eff. July 1, 1991.
9VAC5-40-4550. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3210, eff. January 1, 1985.
9VAC5-40-4560. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3211, eff. January 1, 1985.
9VAC5-40-4570. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3212, eff. January 1, 1985.
9VAC5-40-4580. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3213, eff. January 1, 1985.
9VAC5-40-4590. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3214, eff. January 1, 1985.
9VAC5-40-4600. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3215, eff. January 1, 1985.
Article 33
Emission Standards for Metal Furniture Coating Application Systems (Rule 4-33)
9VAC5-40-4610. Applicability and designation of affected facility.
Article 33
Emission Standards for Metal Furniture Coating Application Systems (Rule 4-33)
A. Except as provided in subsection C of this section, the affected facility to which the provisions of this article apply is each metal furniture coating application system.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206.
C. The provisions of this article do not apply to coating application systems used exclusively for determination of product quality and commercial acceptance provided:
1. The operation is not an integral part of the production process;
2. The emissions from all product quality coating application systems do not exceed 400 pounds in any 30 day period; and
3. The exemption is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3301, eff. July 1, 1991.
9VAC5-40-4620. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Application area" means the area where the coating is applied by spraying, dipping or flow coating techniques.
"Carbon adsorption system" means a device containing activated carbon as the adsorbent material, an inlet and outlet for exhaust gases, and a system to regenerate the saturated adsorbent. The carbon adsorption system must provide for the proper disposal or reuse of all volatile organic compounds in the adsorbate.
"Coating applicator" means an apparatus used to apply a surface coating.
"Coating application system" means any operation or system where a surface coating of one type or function is applied, dried or cured and which is subject to the same emission standard. May include any equipment which applies, conveys, dries or cures a surface coating, including, but not limited to, spray booths, flow coaters, flashoff areas, air dryers, drying areas and ovens. It is not necessary for a coating application system to have an oven, flashoff area or drying area to be included in this definition.
"Flashoff area" means the space between the application area and the oven.
"Metal furniture coating" means the surface coating of any furniture made of metal or any metal part which will be assembled with other metal, wood, fabric, plastic or glass parts to form a furniture piece.
"Oven" means a chamber within which heat is used to bake, cure, polymerize or dry a surface coating or any combination of those.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3302, eff. July 1, 1991.
9VAC5-40-4630. Standard for volatile organic compounds.
A. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 3.0 pounds per gallon of coating, excluding water, as delivered by the coating applicator.
B. Achievement of the emission standard in subsection A of this section by use of methods in 9VAC5-40-4640 will be acceptable to the board.
C. No owner or other person shall use any coating system or equipment unless reasonable precautions are taken to minimize the discharge of emissions from cleaning or purging operations. Reasonable precautions may include the following:
1. The use of capture or control devices or both;
2. The use of detergents, high pressure water, or other nonvolatile cleaning methods;
3. The minimization of the quantity of volatile organic compounds used to clean lines of equipment; and
4. The adjustment of production schedules to minimize coating changes thereby reducing the need for frequent cleaning or purging of a system.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3303, eff. July 1, 1991.
9VAC5-40-4640. Control technology guidelines.
The control technology should consist of one or more of the following:
1. Use of electrodeposited waterborne coatings.
2. Use of other waterborne coatings.
3. Use of powder coatings.
4. Use of high-solids coatings.
5. Carbon adsorption.
6. Incineration.
7. Any technology of equal or greater control efficiency when compared to the use of a coating complying with 9VAC5-40-4630 A, provided such technology is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3304, eff. July 1, 1991.
9VAC5-40-4650. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3305, eff. January 1, 1985.
9VAC5-40-4660. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3306, eff. January 1, 1985.
9VAC5-40-4670. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3307, eff. January 1, 1985.
9VAC5-40-4680. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3308, eff. January 1, 1985.
9VAC5-40-4690. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. The emission standards in 9VAC5-40-4630 apply coating by coating or to the volume weighted average of coatings where the coatings are used on a single coating application system and the coatings are the same type or perform the same function. Such averaging shall not exceed 24 hours.
C. Compliance determinations for control technologies not based on compliant coatings (i.e., coating formulation alone) shall be based on the applicable standard in terms of pounds of volatile organic compounds per gallon solids or pounds of volatile organic compounds per gallon solids applied according to the applicable procedure in 9VAC5-20-121. Compliance may also be based on transfer efficiency greater than the board accepted baseline transfer efficiency if demonstrated by methods acceptable to the board according to the applicable procedure in 9VAC5-20-121.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3309, eff. July 1, 1991.
9VAC5-40-4700. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3310, eff. January 1, 1985.
9VAC5-40-4710. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3311, eff. January 1, 1985.
9VAC5-40-4720. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3312, eff. January 1, 1985.
9VAC5-40-4730. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3313, eff. January 1, 1985.
9VAC5-40-4740. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3314, eff. January 1, 1985.
9VAC5-40-4750. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3315, eff. January 1, 1985.
Article 34
Emission Standards for Miscellaneous Metal Parts and Products Coating Application Systems (Rule 4-34)
9VAC5-40-4760. Applicability and designation of affected facility.
Article 34
Emission Standards for Miscellaneous Metal Parts and Products Coating Application Systems (Rule 4-34)
A. Except as provided in subsections C and D of this section, the affected facility to which the provisions of this article apply is each miscellaneous metal parts and products coating application system.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206. On and after February 1, 2017, this article does not apply to sources in the Northern Virginia Volatile Organic Compound Emissions Control Area designated in 9VAC5-20-206. These sources are subject to Article 59 (9VAC5-40-8810 et seq.) of this part.
C. Exempted from the provisions of this article are coating plants whose emissions of volatile organic compounds are not more than 2.7 tons per year, 15 pounds per day and three pounds per hour, based on the actual emission rate. All volatile organic compound emissions from purging or washing solvents shall be considered in applying the exemption levels specified in this subsection.
D. The provisions of this article do not apply to the following:
1. Coating application systems used exclusively for determination of product quality and commercial acceptance provided:
a. The operation is not an integral part of the production process;
b. The emissions from all product quality coating application systems do not exceed 400 pounds in any 30 day period; and
c. The exemption is approved by the board.
2. Vehicle refinishing operations.
3. Vehicle customized coating operations, if production is less than 20 vehicles per day.
4. Fully assembled aircraft and marine vessel exterior coating operations.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from VR120-04-3401, eff. July 1, 1991; amended, Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-4770. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Application area" means the area where the coating is applied by spraying, dipping or flow coating techniques.
"Carbon adsorption system" means a device containing activated carbon as the adsorbent material, an inlet and outlet for exhaust gases, and a system to regenerate the saturated adsorbent. The carbon adsorption system must provide for the proper disposal or reuse of all volatile organic compounds in the adsorbate.
"Clear coating" means a coating which lacks color and opacity or is transparent and uses the undercoat as a reflectant base or undertone color.
"Coating application system" means any operation or system where a surface coating of one type or function is applied, dried or cured and which is subject to the same emission standard. May include any equipment which applies, conveys, dries or cures a surface coating, including, but not limited to, spray booths, flow coaters, flashoff areas, air dryers, drying areas and ovens. It is not necessary for a coating application system to have an oven, flashoff area or drying area to be included in this definition.
"Coating applicator" means an apparatus used to apply a surface coating.
"Extreme environmental conditions" means exposure to any one of the following: the weather all of the time, temperatures consistently above 95°C, detergents, scouring, solvents, corrosive atmospheres or similar environmental conditions.
"Extreme performance coatings" means coatings which are required to be used by design specification on products designed for harsh exposure or extreme environmental conditions.
"Flashoff area" means the space between the application area and the oven.
"Miscellaneous metal parts and products" means any part or product from the following industrial categories:
a. Large farm machinery (harvesting, fertilizing and planting machines, tractors, combines, etc.);
b. Small farm machinery (lawn and garden tractors, lawn mowers, rototillers, etc.);
c. Small appliances (fans, mixers, blenders, crock pots, dehumidifiers, vacuum cleaners, etc.);
d. Commercial machinery (computers and auxiliary equipment, typewriters, calculators, vending machines, etc.);
e. Industrial machinery (pumps, compressors, conveyor components, fans, blowers, transformers, etc.);
f. Fabricated metal products (i.e., metal covered doors, frames); and
g. Any other industrial category which coats metal parts or products under the Standard Industrial Classification Code of Major Group 33 (primary metal industries), Major Group 34 (fabricated metal products), Major Group 35 (nonelectrical machinery), Major Group 36 (electrical machinery), Major Group 37 (transportation equipment), Major Group 38 (miscellaneous instruments), Major Group 39 (miscellaneous manufacturing industries), Major Group 40 (railroad transportation), and Major Group 41 (transit passenger transportation). "Major groups" (i.e., which have the same two-digit code) shall be described in the Standard Industrial Classification Manual (see 9VAC5-20-21).
"Oven" means a chamber within which heat is used to bake, cure, polymerize or dry a surface coating or any combination of those.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3402, eff. July 1, 1991.
9VAC5-40-4780. Standard for volatile organic compounds.
A. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of:
1. 4.3 pounds per gallon of coating, excluding water, delivered to the coating applicator that applies clear coatings;
2. 3.5 pounds per gallon of coating, excluding water, delivered to a coating applicator in a coating application system that utilizes air or forced air driers;
3. 3.5 pounds per gallon of coating, excluding water, delivered to a coating applicator that applies extreme performance coatings, or
4. 3.0 pounds per gallon of coating, excluding water, delivered to a coating applicator for all other coatings and coating application systems.
B. If more than one emission limitation in subsection A of this section applies to a specific coating, then the least stringent emission limitation shall be applied.
C. Achievement of the emission standard in subsection A of this section by use of methods in 9VAC5-40-4790 will be acceptable to the board.
D. No owner or other person shall use any coating application system or equipment unless reasonable precautions are taken to minimize the discharge or emissions from cleaning or purging operations. Reasonable precautions may include the following:
1. The use of capture or control devices or both;
2. The use of detergents, high pressure water, or other non-volatile cleaning methods;
3. The minimization of the quantity of volatile organic compounds used to clean lines of equipment; and
4. The adjustment of production schedules to minimize coating changes thereby reducing the need for frequent cleaning or purging of a system.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3403, eff. July 1, 1991.
9VAC5-40-4790. Control technology guidelines.
The control technology should consist of one of the following:
1. Use of electrodeposited waterborne coatings;
2. Use of waterborne coatings;
3. Use of high-solids coatings;
4. Use of powder coatings;
5. Carbon adsorption;
6. Incineration; or
7. Any technology of equal or greater control efficiency when compared to the use of a coating complying with 9VAC5-40-4780 A, provided such technology is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3404, eff. July 1, 1991.
9VAC5-40-4800. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3405, eff. January 1, 1985.
9VAC5-40-4810. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3406, eff. January 1, 1985.
9VAC5-40-4820. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3407, eff. January 1, 1985.
9VAC5-40-4830. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3408, eff. January 1, 1985.
9VAC5-40-4840. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. The emission standards in 9VAC5-40-4780 apply coating by coating or to the volume weighted average of coatings where the coatings are used on a single coating application system and the coatings are the same type or perform the same function. Such averaging shall not exceed 24 hours.
C. Compliance determinations for control technologies not based on compliant coatings (i.e., coating formulation alone) shall be based on the applicable standard in terms of pounds of volatile organic compounds per gallon solids or pounds of volatile organic compounds per gallon solids applied according to the applicable procedure in 9VAC5-20-121. Compliance may also be based on transfer efficiency greater than the board accepted baseline transfer efficiency if demonstrated by methods acceptable to the board according to the applicable procedure in 9VAC5-20-121.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3409, eff. July 1, 1991.
9VAC5-40-4850. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3410, eff. January 1, 1985.
9VAC5-40-4860. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3411, eff. January 1, 1985.
9VAC5-40-4870. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3412, eff. January 1, 1985.
9VAC5-40-4880. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3413, eff. January 1, 1985.
9VAC5-40-4890. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3414, eff. January 1, 1985.
9VAC5-40-4900. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3415, eff. January 1, 1985.
Article 35
Emission Standards for Flatwood Paneling Coating Application Systems (Rule 4-35)
9VAC5-40-4910. Applicability and designation of affected facility.
Article 35
Emission Standards for Flatwood Paneling Coating Application Systems (Rule 4-35)
A. Except as provided in subsection C of this section, the affected facility to which the provisions of this article apply is each flatwood paneling coating application system.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206.
C. The provisions of this article do not apply to the following:
1. Coating application systems used exclusively for determination of product quality and commercial acceptance provided:
a. The operation is not an integral part of the production process;
b. The emissions from all product quality coating application systems do not exceed 400 pounds in any 30 day period; and
c. The exemption is approved by the board.
2. Coating application systems involved in the manufacture of exterior siding, tileboard or particleboard used as a furniture component.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3501, eff. July 1, 1991.
9VAC5-40-4920. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Application area" means the area where the coating is applied by spraying, dipping or flow coating techniques.
"Carbon adsorption system" means a device containing activated carbon as the adsorbent material, an inlet and outlet for exhaust gases, and a system to regenerate the saturated adsorbent. The carbon adsorption system must provide for the proper disposal or reuse of all volatile organic compounds in the adsorbate.
"Class II Hardboard paneling finishes" means finishes which meet the specifications of Voluntary Product Standard PS-59-73 as approved by the American National Standards Institute.
"Coating application system" means any operation or system where a surface coating of one type or function is applied, dried or cured and which is subject to the same emission standard. May include any equipment which applies, conveys, dries or cures a surface coating, including, but not limited to, spray booths, flow coaters, flashoff areas, air dryers, drying areas and ovens. It is not necessary for a coating application system to have an oven, flashoff area or drying area to be included in this definition.
"Flashoff area" means the space between the application area and the oven.
"Hardboard" means a panel manufactured primarily from inter-felted lignocellulosic fibers which are consolidated under heat and pressure in hot-press.
"Hardwood plywood" means plywood whose surface layer is a veneer of hardwood.
"Natural finish hardwood plywood panels" means panels whose original grain pattern is enhanced by essentially transparent finishes frequently supplemented by fillers and toners.
"Oven" means a chamber within which heat is used to bake, cure, polymerize or dry a surface coating or any combination of these.
"Particleboard" means a manufactured board made of individual wood particles which have been coated with a binder and formed into flat sheets by pressure. Thin particleboard has a thickness of ¼ inch or less.
"Printed interior panels" means panels whose grain or natural surface is obscured by fillers and basecoats upon which a simulated grain or decorative pattern is printed.
"Tileboard" means paneling that has a colored waterproof surface coating.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3502, eff. July 1, 1991.
9VAC5-40-4930. Standard for volatile organic compounds.
A. Printed interior panels made of hardwood plywood and thin particleboard.
1. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 6.0 pounds per 1,000 ft2 of coating surface, regardless of the number of coats applied.
2. Achievement of the emission standard in subsection A 1 of this section by use of methods in 9VAC5-40-4940 will be acceptable to the board.
B. Natural finish hardwood plywood panels.
1. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 12.0 pounds per 1,000 ft2 of coated surface, regardless of the number of coats applied.
2. Achievement of the emission standard in subsection B 1 of this section by use of methods in 9VAC5-40-4940 will be acceptable to the board.
C. Class II hardboard paneling finishes.
1. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of 10.0 pounds per 1,000 ft2 of coated surface, regardless of the number of coats applied.
2. Achievement of the emission standard in subsection C 1 of this section by use of methods in 9VAC5-40-4940 will be acceptable to the board.
D. No owner or other person shall use any coating application system or equipment unless reasonable precautions are taken to minimize the discharge of emissions from cleaning or purging operations. Reasonable precautions may include the following:
1. The use of capture or control devices or both;
2. The use of detergents, high pressure water, or other nonvolatile cleaning methods;
3. The minimization of the quantity of volatile organic compounds used to clean lines of equipment; and
4. The adjustment of production schedules to minimize coating changes thereby reducing the need for frequent cleaning or purging of a system.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3503, eff. July 1, 1991.
9VAC5-40-4940. Control technology guidelines.
The control technology should consist of one or more of the following:
1. Use of waterborne coatings.
2. Use of high-solids coatings.
3. Use of ultraviolet curing systems.
4. Use of electron beam curing systems.
5. Carbon adsorption.
6. Incineration.
7. Any technology of equal or greater control efficiency when compared to the use of a coating complying with 9VAC5-40-4930 A, B, or C as applicable, provided such technology is approved by the board.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3504, eff. July 1, 1991.
9VAC5-40-4950. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3505, eff. January 1, 1985.
9VAC5-40-4960. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3506, eff. January 1, 1985.
9VAC5-40-4970. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3507, eff. January 1, 1985.
9VAC5-40-4980. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3508, eff. January 1, 1985.
9VAC5-40-4990. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. The emission standards in 9VAC5-40-4930 apply coating by coating or to the volume weighted average of coatings where the coatings are used on a single coating application system and the coatings are the same type or perform the same function. Such averaging shall not exceed 24 hours.
C. Compliance determinations for control technologies not based on compliant coatings (i.e., coating formulation alone) shall be based on the applicable standard in terms of pounds of volatile organic compounds per gallon solids or pounds of volatile organic compounds per gallon solids applied according to the applicable procedure in 9VAC5-20-121. Compliance may also be based on transfer efficiency greater than the board accepted baseline transfer efficiency if demonstrated by methods acceptable to the board according to the applicable procedure in 9VAC5-20-121.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3509, eff. July 1, 1991.
9VAC5-40-5000. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3510, eff. January 1, 1985.
9VAC5-40-5010. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3511, eff. January 1, 1985.
9VAC5-40-5020. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3512, eff. January 1, 1985.
9VAC5-40-5030. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3513, eff. January 1, 1985.
9VAC5-40-5040. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3514, eff. January 1, 1985.
9VAC5-40-5050. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3515, eff. January 1, 1985.
Article 36
Emission Standards for Flexographic, Packaging Rotogravure, and Publication Rotogravure Printing Lines (Rule 4-36)
9VAC5-40-5060. Applicability and designation of affected facility.
Article 36
Emission Standards for Flexographic, Packaging Rotogravure, and Publication Rotogravure Printing Lines (Rule 4-36)
A. Except as provided in subsections C, D, and E of this section, the affected facility to which the provisions of this article apply is each flexographic, packaging rotogravure, or publication rotogravure printing line which uses a substrate other than a textile.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206.
C. Exempted from the provisions of this article are flexographic, packaging rotogravure, and publication rotogravure facilities in the Northern Virginia Volatile Organic Compound Emissions Control Area whose potential to emit is less than 25 tons per year of volatile organic compounds, provided the emission rates are determined in a manner acceptable to the board. All volatile organic compound emissions from printing inks and cleaning solutions shall be considered in applying the exemption levels specified in this subsection.
D. Exempted from the provisions of this article are flexographic, packaging rotogravure, and publication rotogravure facilities in all volatile organic compound emissions control areas, other than the Northern Virginia Volatile Organic Compound Emissions Control Area, whose potential to emit is less than 100 tons per year of volatile organic compounds, provided the emission rates are determined in a manner acceptable to the board. All volatile organic compound emissions from printing inks and cleaning solutions shall be considered in applying the exemption levels specified in this subsection.
E. The provisions of this article do not apply to the following:
1. Printing processes used exclusively for determination of product quality and commercial acceptance provided:
a. The operation is not an integral part of the production process;
b. The emissions from all product quality printing processes do not exceed 400 pounds in any 30 day period; and
c. The exemption is approved by the board.
2. Lithography or letterpress printing.
3. Electrostatic duplication.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110 and 182 of the Clean Air Act; 40 CFR Part 51.
Historical Notes
Derived from VR120-04-3601, eff. July 1, 1991; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996; Volume 22, Issue 26, eff. October 4, 2006.
9VAC5-40-5070. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Carbon adsorption system" means a device containing activated carbon as the adsorbent material, an inlet and outlet for exhaust gases, and a system to regenerate the saturated adsorbent. The carbon adsorption system must provide for the proper disposal or reuse of all volatile organic compounds in the adsorbate.
"Compliant ink or surface coating" means an ink or surface coating conforming to the definition of a high-solids, low-volatile organic compound or a waterborne ink or surface coating.
"Cleaning solutions" means any liquid used to remove ink and debris from the operating surface of a printing press and its parts.
"Electrostatic duplication" means a process using a plate or takeoff sheet that is electrically charged to attract developer to the image area only.
"Flexographic printing" means the application of words, designs or pictures by a rubber or elastomeric image carrier in which the image area is raised above the nonimage area.
"High-solids ink or surface coating" means an ink or surface coating which contains 60% or more nonvolatile compounds by volume.
"Letterpress printing" means a printing process which uses raised image transfer elements fixed upon a metal backing.
"Lithographic printing" means a planographic printing process in which the image and nonimage areas are chemically differentiated with the image area being oil receptive and the nonimage area being water receptive.
"Low-solvent ink or surface coating" means an ink or surface coating which contains not more than 0.5 pounds of volatile organic compounds per pound of nonvolatile compounds and is used on a packaging rotogravure printing or flexographic printing press.
"Noncompliant ink or surface coating" means an ink or surface coating which does not conform to the definition of a high-solids, low-volatile organic compound or waterborne ink or surface coating.
"Packaging rotogravure printing" means an intaglio printing process in which the ink is transferred from minute etched wells on an image carrier, typically a cylinder, to paper, paper board, metal foil, plastic film and other substrates, which are, in subsequent operations, formed into containers and labels for articles to be sold.
"Printing" means a photomechanical process in which a transfer of text, designs, and images occurs through contact of an image carrier with a substrate.
"Printing line" means all of the equipment between a web feed input and the finished rolled or cut and stacked product wherein printing ink or a combination of printing inks and surface coatings are applied, dried, or cured and which is subject to the same emission standard. Such equipment may include decks, stations, press units, devices, ink stations, and any other equipment which applies, conveys, dries, or cures surface inks or surface coatings. Such equipment may include but is not limited to flow coaters, flashoff areas, air dryers, drying areas, and ovens. It is not necessary for a printing line to have an oven, flashoff area, or drying area to be included in this definition.
"Printing process" means any operation or system wherein printing ink or a combination of printing ink and surface coating is applied, dried or cured and which is subject to the same emission standard. May include any equipment which applies, conveys, dries or cures inks or surface coatings, including, but not limited to, flow coaters, flashoff areas, air dryers, drying areas and ovens. It is not necessary for a printing process to have an oven, flashoff area or drying area to be included in this definition.
"Publication rotogravure printing" means an intaglio printing process in which the ink is transferred from minute etched wells on an image carrier, typically a cylinder, to paper which is subsequently formed into books, magazines, catalogues, brochures, directories, newspaper supplements or any other types of printed materials not included under the definition of packaging rotogravure printing.
"Surface coating" means all nonink liquids and liquid-solid mixtures containing volatile organic compounds which are applied to the substrate by printing units.
"Waterborne ink" or "surface coating" means an ink or surface coating whose volatile portion consists of 75% or more by volume of water and 25% or less by volume of volatile organic compounds.
"Web" means a continuous roll of printing substrate.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3602, eff. July 1, 1991; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-5080. Standard for volatile organic compounds.
A. No owner or other person shall use or permit the use of any packaging rotogravure, publication rotogravure or flexographic printing line employing an ink or surface coating containing volatile organic compounds unless:
1. The ink or surface coating, as it is applied to the substrate, is a waterborne ink or surface coating;
2. The ink or surface coating, as it is applied to the substrate, is a high-solids ink or surface coating;
3. The ink or surface coating, as it is applied to the substrate, is a low-solvent ink or surface coating; or
4. The owner installs and operates an emission control system which achieves the emission reductions specified below in subdivision A 4 a through c of this section. The reduction in volatile organic compound emissions from each printing line shall be at least:
a. 75% by weight of volatile organic compounds of all noncompliant inks and surface coatings where a publication rotogravure printing process is employed;
b. 65% by weight of volatile organic compounds of all noncompliant inks and surface coatings where a packaging rotogravure printing process is employed; or
c. 60% by weight of volatile organic compounds of all noncompliant inks and surface coatings where a flexographic printing process is employed.
B. All units in a machine which has printing units and coating or laminating units shall be subject to this article and exempt from Article 31 (9VAC5-40-4310 et seq.) of this chapter.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3603, eff. July 1, 1991; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-5090. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3605, eff. January 1, 1985.
9VAC5-40-5100. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3606, eff. January 1, 1985.
9VAC5-40-5110. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3607, eff. January 1, 1985.
9VAC5-40-5120. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3608, eff. January 1, 1985.
9VAC5-40-5130. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. The emission standards in 9VAC5-40-5080 A apply ink by ink and coating by coating or to the volume weighted average of inks or surface coatings where the inks and surface coatings are used on a single printing line and the inks and surface coatings are of the same type or perform the same function.
C. Inks and surface coatings meeting the criteria in 9VAC5-40-5080 A 1 through 3 (compliant inks and coatings) may be used on the same printing line with inks and surface coatings subject to the control requirements in 9VAC5-40-5080 (noncompliant inks and coatings) to meet the control requirements of 9VAC5-40-5080 without the installation of an add-on control system. When this is the case, compliance is determined by credits generated by the weight of volatile organic compounds by which the compliant inks or coatings are less than the applicable criteria in 9VAC5-40-5080 A 1 through 3. Compliance is demonstrated if the total credits in pounds of volatile organic compounds is equal to or greater than the total weight of volatile organic compound reduction required of the noncompliant inks over a time period not exceeding 24 hours.
D. Compliance with the requirements of 9VAC5-40-5130 B and C and the emission standards in 9VAC5-40-5080 A shall apply as follows:
1. To each printing line, and to parts of a printing line individually designated by the owner; or
2. To multiple printing lines controlled by a single solvent recovery system. For this option, the most stringent standard applicable to any of the printing lines is applied to all the lines controlled by the same solvent recovery system.
E. The emission standards in 9VAC5-40-5080 A shall apply to each successive compliance averaging period. This compliance averaging period shall not exceed:
1. 24 hours; or
2. The minimum compliance averaging period acceptable to the board, provided that:
a. The owner demonstrates to the satisfaction of the board that an averaging period of 24 hours or less does not adequately represent the reduction of volatile organic compound emissions over the same time period because of the physical or operational characteristics of an add-on control system;
b. The owner demonstrates to the satisfaction of the board the minimum compliance averaging period which adequately represents the reduction of volatile organic compound emissions; and
c. The owner determines compliance for each day or partial day of operation using the minimum compliance averaging period acceptable to the board.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3609, eff. July 1, 1991; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-5140. Test methods and procedures.
A. The provisions of 9VAC5-40-30 (Emission Testing) apply.
B. Testing for compliance with the emission standards in 9VAC5-40-5080 A 4 shall be performed using the applicable methods and procedures specified in 9VAC5-20-121.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3610, eff. January 1, 1985; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-5150. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3611, eff. January 1, 1985.
9VAC5-40-5160. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3612, eff. January 1, 1985.
9VAC5-40-5170. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3613, eff. January 1, 1985.
9VAC5-40-5180. Facility and control equipment maintenance of malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3614, eff. January 1, 1985.
9VAC5-40-5190. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3615, eff. January 1, 1985; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
Article 37
Emission Standards for Petroleum Liquid Storage and Transfer Operations (Rule 4-37)
9VAC5-40-5200. Applicability and designation of affected facility.
Article 37
Emission Standards for Petroleum Liquid Storage and Transfer Operations (Rule 4-37)
A. Except as provided in subsection C of this section, the affected facility to which the provisions of this article apply is each operation involving the storage or transfer of petroleum liquids or both.
B. Except as provided in subdivisions 1, 2 and 3 of this subsection, the provisions of this article apply to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206.
1. The emission standards in 9VAC5-40-5220 C, D, E, and G shall not apply to affected facilities in the following localities: Botetourt County, Frederick County, and Winchester City.
2. The emission standard in 9VAC5-40-5220 F shall apply only to affected facilities in the Northern Virginia and Richmond Volatile Organic Compound Emissions Control Areas. For the purposes of applicability of 9VAC5-40-5220 F only, the Richmond Emissions Control Area does not include Prince George County and Petersburg City.
3. The emission standard in 9VAC5-40-5220 C shall apply to affected facilities in Bedford County.
C. The provisions of this article do not apply to affected facilities using petroleum liquids with a vapor pressure less than 1.5 pounds per square inch absolute under actual storage conditions or, in the case of loading or processing, under actual loading or processing conditions. (Kerosene and fuel oil have vapor pressures of less than 1.5 pounds per square inch absolute under actual storage conditions; therefore, kerosene and fuel oil are not subject to the provisions of this article when used or stored at ambient temperatures).
D. The burden of proof of eligibility for exemption from this article is on the owner. Owners seeking such an exemption shall maintain adequate records of average monthly throughput and furnish these records to the board upon request.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110 and 182 of the Clean Air Act; 40 CFR Part 51.
Historical Notes
Derived from VR120-04-3701, eff. January 1, 1993; amended, Virginia Register Volume 14, Issue 2, eff. January 1, 1998; Volume 16, Issue 24, eff. October 1, 2000; Volume 20, Issue 12, eff. March 24, 2004; Volume 22, Issue 26, eff. October 4, 2006.
9VAC5-40-5210. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Average monthly throughput" means the average monthly amount of gasoline pumped at a gasoline dispensing facility during the two most recent consecutive calendar years or some other two-year period which is representative of normal source operation. If the board determines that no two-year period is representative of normal source operation, the board shall allow the use of an alternative period of time upon a determination by the board that it is more representative of normal source operation. Downtime, such as a full or significant shutdown of a facility's operation due to construction, shall not be included when calculating average monthly throughput.
"Begin actual construction" means initiation of permanent physical on-site construction of a new gasoline dispensing facility. This includes, but is not limited to, installation of building supports and foundations, laying of underground pipework, and construction of permanent storage structures.
"Bulk gasoline plant" means a secondary distribution point for delivering gasoline to local farms, businesses, service stations and other distribution points, where the total gasoline throughput is 20,000 gallons or less per working day, based on the daily average for the most recent 12-month period.
"Bulk gasoline terminal" means a primary distribution point for delivering gasoline to bulk plants, service stations and other distribution points, where the total gasoline throughput is greater than 20,000 gallons per working day, based on the daily average for the most recent 12-month period.
"Certified Stage II vapor recovery system" means any system certified by California Air Resources Board as having a vapor recovery or removal efficiency of at least 95%, and approved under the provisions of AQP-9, Procedures for Implementation of Regulations Covering Stage II Vapor Recovery Systems for Gasoline Dispensing Facilities (see 9VAC5-20-121).
"Condensate" means a hydrocarbon liquid separated from natural gas which condenses due to changes in the temperature or pressure or both and remains liquid at standard conditions.
"Crude oil" means a naturally occurring mixture which consists of any combination of hydrocarbons, sulfur, nitrogen or oxygen derivatives of hydrocarbons and which is a liquid at standard conditions.
"Custody transfer" means the transfer of produced crude oil or condensate, after processing or treating or both in the producing operations, from storage tanks or automatic transfer facilities to pipelines or any other forms of transportation.
"Defective equipment" means any absence, disconnection, or malfunctioning of a Stage II vapor recovery system component required by this article including, but not limited to, the following:
a. A vapor return line that is crimped, flattened, blocked, or that has any hole or slit that allows vapors to leak out;
b. A nozzle bellows that has any hole large enough to allow a ¼-inch diameter cylindrical rod to pass through it or any slit one inch or more in length;
c. A nozzle faceplate or cone that is torn or missing over 25% of its surface;
d. A nozzle with no automatic overfill control mechanism, or an inoperable overfill control mechanism; and
e. An inoperable or malfunctioning vapor processing unit, vacuum generating device, pressure or vacuum relief valve, vapor check valve or any other equipment normally used to dispense gasoline or is required by this article.
"External floating roof" means a storage vessel cover in an open top consisting of a double deck or pontoon single deck which rests upon and is supported by the liquid being contained and is equipped with a closure seal or seals to close the space between the roof edge and tank shell.
"Gasoline" means any petroleum distillate having a Reid vapor pressure of four pounds per square inch or greater.
"Gasoline dispensing facility" means any site where gasoline is dispensed to motor vehicle tanks from stationary storage tanks.
"Independent small business gasoline marketer" means a person engaged in the marketing of gasoline who owns one or more gasoline dispensing facilities and is required to pay for procurement and installation of vapor recovery equipment, unless such owner:
a. Is a refiner; controls, or is controlled by, or is under common control with, a refiner; or is otherwise directly or indirectly affiliated with a refiner or with a person who controls, is controlled by, or is under a common control with a refiner (unless the sole affiliation is by means of a supply contract or an agreement or contract to use a trademark, tradename, service mark, or other identifying symbol or name owned by such refiner or any such person); or
b. Receives less than 50% of his annual income from refining or marketing of gasoline.
For the purposes of this definition, "control" of a corporation means ownership of more than 50% of its stock and "control" of a partnership, joint venture or other nonstock entity means ownership of more than a 50% interest in such partnership, joint venture or other nonstock entity. The lessee of a gasoline dispensing facility, for which the owner of such outlet does not sell, trade in, or otherwise dispense any product at wholesale or retail at such outlet, shall be considered an independent small business marketer if the lessee by lease agreement with the owner is required to pay for the cost of procurement and installation of vapor recovery equipment over a reasonable period.
"Internal floating roof" means a cover or roof in a fixed roof tank which rests upon or is floated upon the liquid being contained and is equipped with a closure seal or seals to close the space between the roof edge and tank shell.
"Liquid-mounted" means a primary seal mounted so the bottom of the seal covers the liquid surface between the tank shell and the floating roof.
"Major system modification" means the replacement, repair or upgrade of 75% of a facility's Stage II vapor recovery system equipment.
"Owner" means, for the purposes of this article, any person, including bodies politic and corporate, associations, partnerships, personal representatives, trustees and committees, as well as individuals who own, lease, operate, control or supervise an operation involving the storage or transfer of petroleum liquids or both.
"Petroleum liquids" means crude oil, condensate, and any finished or intermediate products manufactured or extracted in a petroleum refinery.
"Petroleum refinery" means any facility engaged in producing gasoline, kerosene, distillate fuel oils, residual fuel oils, lubricants or other products through distillation of petroleum or through redistillation, cracking, rearrangement or reforming of unfinished petroleum derivatives.
"Refiner" means any person or entity that owns or operates a facility engaged in the production of gasoline, kerosene, distillate fuel oils, residual fuel oils, lubricants or similar products through distillation of petroleum or through redistillation, cracking, or reforming of unfinished petroleum derivatives and whose total refinery capacity (including the refinery capacity of any person or entity who controls, is controlled by or is under common control with, such refiner) is greater than 65,000 barrels per day.
"Stage II vapor recovery system" means any equipment designed and used to collect, recover, or destroy, or any combination of those, gasoline vapors displaced during the transfer of gasoline into a motor vehicle fuel tank.
"Submerged fill pipe" means any fill pipe the discharge opening of which is entirely submerged when the liquid level is six inches above the bottom of the tank; or, when applied to a tank which is loaded from the side, any fill pipe the discharge opening of which is entirely submerged when at the minimum operating level.
"Vapor-mounted" means a primary seal mounted so there is an annular vapor space underneath the seal. The annular vapor space is bounded by the bottom of the primary seal, the tank shell, the liquid surface, and the floating roof.
"Vapor tight" means capable of holding a pressure of 18 inH20 and a vacuum of 6 inH2O without sustaining a pressure change of more than 3 inH2O in five minutes.
"Waxy, heavy pour crude oil" means a crude oil with a pour point of 50°F or higher as determined by the American Society for Testing and Materials publication, "Test for Pour Point of Petroleum Oils" (see 9VAC5-20-21).
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3702, eff. January 1, 1993; amended, Virginia Register Volume 18, Issue 7, eff. February 1, 2002.
9VAC5-40-5220. Standard for volatile organic compounds.
A. Petroleum liquid storage-fixed roof tanks.
1. No owner or other person shall use or permit the use of any fixed roof tank of more than 40,000 gallons capacity for storage of petroleum liquids, unless such tank is equipped with a control method that will remove, destroy, or prevent the discharge into the atmosphere of at least 90% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subdivision 1 of this subsection by use of methods in 9VAC5-40-5230 A will be acceptable to the board.
3. The provisions of this subsection shall not be applicable to fixed roof tanks having capacities less than 400,000 gallons for crude oil or condensate stored, processed, or treated at a drilling and production facility prior to custody transfer.
4. The owner of a fixed roof tank subject to the provisions of subdivision 1 of this subsection shall:
a. When the fixed roof tank is equipped with an internal floating roof, perform a visual inspection annually of the floating cover through roof hatches to ascertain compliance with the specifications in subdivisions (1) and (2) of this subdivision A 4 a.
(1) The cover should be uniformly floating on or above the liquid and there should be no visible defects in the surface of the cover or liquid accumulated on the cover.
(2) The seal must be intact and uniformly in place around the circumference of the cover between the cover and tank wall.
b. Perform a complete inspection of the cover and seal and record the condition of the cover and seal when the tank is emptied for nonoperational reasons such as maintenance, an emergency, or other similar purposes.
c. Maintain records of the throughput quantities and types of petroleum liquids stored, the average monthly storage temperature and true vapor pressure of the liquid as stored, and the results of the inspections performed under the provisions of subdivisions 4 a and 4 b of this subsection.
B. Petroleum liquid storage--floating roof tanks.
1. No owner or other person shall use or permit the use of any floating roof tank of more than 40,000 gallons capacity for storage of petroleum liquids, unless such tank is equipped with a control method that will remove, destroy, or prevent the discharge into the atmosphere of at least 90% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subdivision 1 of this subsection by use of methods in 9VAC5-40-5230 B will be acceptable to the board.
3. The provisions of this subsection shall not be applicable to the following:
a. Floating roof tanks having capacities less than 400,000 gallons for crude oil or condensate stored, processed, or treated at a drilling and production facility prior to custody transfer.
b. Floating roof tanks storing waxy, heavy pour crude oil.
4. The owner of a floating roof tank subject to the provisions of subdivision 1 of this subsection shall:
a. Perform routine inspections annually which shall include a visual inspection of the secondary seal gap.
b. When the floating roof is equipped with a vapor-mounted primary seal, measure the secondary seal gap annually in accordance with subdivisions (1) and (2) of this subdivision B 4 b.
(1) Physically measure the length and width of all gaps around the entire circumference of the secondary seal in each place where a 1/8-inch uniform diameter probe passes freely (without forcing or binding against the seal) between the seal and tank wall; and
(2) Sum the area of the individual gaps.
c. Maintain records of the types of petroleum liquids stored, the maximum true vapor pressure of the liquid as stored, and the results of the inspections performed under the provisions of subdivisions a and b of this subdivision B 4.
C. Gasoline bulk loading--bulk terminals.
1. No owner or other person shall cause or permit the discharge into the atmosphere from a bulk gasoline terminal (including any appurtenant equipment necessary to load the tank truck compartments) any volatile organic compound in excess of.67 pounds per 1,000 gallons of gasoline loaded.
2. Achievement of the emission standard in subdivision 1 of this subsection by use of methods in 9VAC5-40-5230 C will be acceptable to the board.
D. Gasoline bulk loading--bulk plants.
1. No owner or other person shall use or permit the use of any bulk gasoline plant (including any appurtenant equipment necessary to load or unload tank trucks and account trucks) unless such plant is equipped with a vapor control system that will remove, destroy, or prevent the discharge into the atmosphere of at least 77% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subdivision 1 of this subsection by use of methods in 9VAC5-40-5230 D will be acceptable to the board.
3. The provisions of this subsection shall not be applicable to facilities whose average daily throughput of gasoline is less than 4,000 gallons per working day when based on a 30-day rolling average. Average daily throughput means the average daily amount of gasoline pumped at a gasoline dispensing facility during the most recent 30-day period. Average daily throughput shall be calculated for the two most recent consecutive calendar years. If during this two-year period or any period thereafter, the average daily throughput exceeds 4,000 gallons per working day, the facility is no longer exempt from the provisions of subdivision 1 of this subsection.
E. Transfer of gasoline--gasoline dispensing facilities--Stage I vapor control systems.
1. No owner or other person shall transfer or permit the transfer of gasoline from any tank truck into any stationary storage tank unless such tank is equipped with a vapor control system that will remove, destroy, or prevent the discharge into the atmosphere of at least 90% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subdivision 1 of this subsection by use of methods in 9VAC5-40-5230 E will be acceptable to the board.
3. The provisions of this subsection shall not apply to the following:
a. Transfers made to storage tanks that are either less than 250 gallons in capacity or located at facilities whose average monthly throughput of gasoline is less than 10,000 gallons.
b. Transfers made to storage tanks equipped with floating roofs or their equivalent.
F. Transfer of gasoline--gasoline dispensing facilities--Stage II vapor recovery systems.
1. No owner or other person shall transfer or permit the transfer of gasoline into the fuel tank of any motor vehicle at any affected gasoline dispensing facility unless the transfer is made using a certified Stage II vapor recovery system that is designed, operated, and maintained such that the vapor recovery system removes, destroys, or prevents the discharge into the atmosphere of at least 95% by weight of volatile organic compound emissions.
2. Achievement of the emission standard in subdivision 1 of this subsection by use of methods in 9VAC5-40-5230 F will be acceptable to the board.
3. The affected gasoline facilities shall be in compliance with the emissions standard in subdivision 1 of this subsection according to the following schedule:
a. Facilities which begin actual construction on or after January 1, 1993, must comply upon startup unless the facility can prove it is exempt under the provisions of subdivision 4 of this subsection.
b. Facilities which begin actual construction after November 15, 1990, and before January 1, 1993, must comply by May 15, 1993.
c. Facilities which begin actual construction on or before November 15, 1990, and dispense an average monthly throughput of 100,000 gallons or more of gasoline must comply by November 15, 1993.
d. All other affected facilities which begin actual construction on or before November 15, 1990, must comply by November 15, 1994.
4. The provisions of this subsection shall not apply to the following facilities:
a. Gasoline dispensing facilities with an average monthly throughput of 10,000 gallons or less.
b. Gasoline dispensing facilities owned by independent small business gasoline marketers with an average monthly throughput of 50,000 gallons or less.
c. Gasoline dispensing devices that are used exclusively for refueling marine vehicles, aircraft, farm equipment, and emergency vehicles.
5. Any gasoline dispensing facility subject to the provisions of this subsection shall also comply with the provisions of subsection E of this section (Stage I vapor controls).
6. In accordance with the provisions of AQP-9, Procedures for Implementation of Regulations Covering Stage II Vapor Recovery Systems for Gasoline Dispensing Facilities (see 9VAC5-20-121), owners of affected gasoline dispensing facilities shall:
a. Register the Stage II system with the board and submit Stage II vapor recovery equipment specifications at least 90 days prior to installation of the Stage II vapor recovery system. Owners of gasoline dispensing facilities in existence as of January 1, 1993, shall contact the board by February 1, 1993, and register the Stage II vapor recovery system according to the schedule outlined in AQP-9. Any repair or modification to an existing Stage II vapor recovery system that changes the approved configuration shall be reported to the board no later than 30 days after completion of such repair or modification.
b. Perform tests, before the equipment is made available for use by the public, on the entire Stage II vapor recovery system to ensure the proper functioning of nozzle automatic shut-off mechanisms and flow prohibiting mechanisms where applicable, and perform a pressure decay/leak test, a vapor space tie test, and a liquid blockage test. In cases where use of one of the test methods in AQP-9 is not feasible for a particular Stage II vapor recovery system, the owner may, upon approval of the board, use an alternative test method.
c. No later than 15 days after system testing is completed, submit to the board documentation showing the results of the tests outlined in subdivision 6 b of this subsection.
d. Ensure that the Stage II vapor recovery system is vapor tight by performing a pressure decay/leak test and a liquid blockage test at least every five years, upon major system replacement or modification, or if requested by the board after evidence of a system malfunction which compromises the efficiency of the system.
e. Notify the board at least two days prior to Stage II vapor recovery system testing as required by subdivisions 6 b and 6 d of this subsection.
f. Conspicuously post operating instructions for the vapor recovery system on each gasoline dispensing pump which includes the following information:
(1) A statement, as described in Part III F 1 of AQP-9 (see 9VAC5-20-121), describing the benefits of the Stage II vapor recovery system.
(2) A clear description of how to correctly dispense gasoline with the vapor recovery nozzles.
(3) A warning that repeated attempts to continue dispensing gasoline after the system has indicated that the vehicle fuel tank is full (by automatically shutting off) may result in spillage or recirculation of gasoline.
(4) A telephone number to report problems experienced with the vapor recovery system to the board.
g. Promptly and conspicuously post "Out Of Order" signs on any nozzle associated with any part of the vapor recovery system that is defective if use of that nozzle would allow escape of gasoline vapors to the atmosphere. "Out of order" signs shall not be removed from affected nozzles until said system has been repaired.
h. Provide adequate training and written instructions for facility personnel to assure proper operation of the vapor recovery system.
i. Perform routine maintenance inspections of the Stage II vapor recovery system on a daily and monthly basis and record the monthly inspection results as specified in Part III E of AQP-9 (see 9VAC5-20-121).
j. Maintain records on site, in a form and manner acceptable to the board, of operator training, system registration and equipment approval, and maintenance, repair and testing of the system. Original documents may be maintained at a centralized location only if copies of these documents are maintained on site according to the requirements set forth in AQP-9. Records shall be retained for a period of at least two years, unless specified otherwise, and shall be made immediately available for inspection by the board upon request.
7. The requirements of this subsection shall apply to the localities specified in 9VAC5-40-5200 B 2 until the following dates, after which the decommissioning or maintenance requirements of subdivision 8 or 9 of this subsection shall be followed.
a. For the Northern Virginia Volatile Organic Compound Control Area: January 1, 2014.
b. For the Richmond Volatile Organic Compound Control Area (which shall not include Prince George County and Petersburg City): January 1, 2017.
8. No owner or other person decommissioning any Stage II equipment shall be relieved from the continuing proper operation and maintenance of Stage I vapor control systems. In order to assure the proper operation and maintenance of Stage I equipment, all of the Stage II decommissioning procedures in this subdivision F 8 shall be completed:
a. Notify the board in writing prior to removing or discontinuing all or part of an existing Stage II system. All notifications shall include:
(1) Name, address, contact name, telephone number, and registration number;
(2) Details and cost of project, and the name of the service provider for the project; and
(3) Start date and projected completion date.
A copy of this notification shall be maintained with on-site records.
b. Decommission the discontinued Stage II system or, in the case of removal and replacement of an existing dispenser system, decommission each dispenser system piping in accordance with all applicable steps provided in the Recommended Practices for Installation and Testing of Vapor-Recovery Systems at Vehicle-Fueling Sites, PEI/RP300-09, Petroleum Equipment Institute (PEI) (see 9VAC5-20-21), or an alternative procedure as approved by the board.
c. Notify the board in writing no more than 30 days after decommissioning all or part of a Stage II system. All notifications shall include:
(1) Name, address, contact name, telephone number, and registration number;
(2) Name and telephone number of the qualified technician or qualified service provider or both who decommissioned the Stage II equipment;
(3) Date decommissioning was complete and type of Stage II system;
(4) Steps used in decommissioning or a completed PEI checklist form (Appendix C of PEI/RP300-09);
(5) Copy of pressure decay test conducted after decommissioning was complete; and
(6) Statement from the service provider verifying the storage system has been left in a condition that will reliably prevent the release of any vapors or liquids from any component of the storage system associated with the Stage II system.
A copy of this notification shall be maintained with on-site records.
9. No owner or other person that continues to operate Stage II equipment in lieu of following the decommissioning procedures in subdivision 8 of this subsection shall be relieved from the continuing proper operation and maintenance of the Stage II equipment in compliance with this article.
G. Tank trucks/account trucks and vapor collection systems.
1. No owner or other person shall use or permit the use of any tank truck or account truck that is loaded or unloaded at facilities subject to the provisions of subsection C, D, or E of this section unless such truck is designed, maintained, and certified to be vapor tight. In addition, there shall be no avoidable visible liquid leaks. Invariably there will be a few drops of liquid from disconnection of dry breaks in liquid lines even when well maintained; these drops are allowed.
2. Vapor-laden tank trucks or account trucks exclusively serving facilities subject to subsection D or E of this section may be refilled only at facilities in compliance with subsection C of this section.
3. Tank truck and account truck hatches shall be closed at all times during loading and unloading operations (periods during which there is liquid flow into or out of the truck) at facilities subject to the provisions of subsection C, D, or E of this section.
4. During loading or unloading operations at facilities subject to the provisions of subsection C, D, or E of this section, there shall be no volatile organic compound concentrations greater than or equal to 100% of the lower explosive limit (LEL, measured as propane) at 2.5 centimeters around the perimeter of a potential leak source as detected by a combustible gas detector. In addition, there shall be no avoidable visible liquid leaks. Invariably there will be a few liquid drops from the disconnection of well-maintained bottom loading dry breaks and the raising of well-maintained top loading vapor heads; these few drops are allowed. The vapor collection system includes all piping, seals, hoses, connection, pressure-vacuum vents, and other possible leak sources between the truck and the vapor disposal unit and between the storage tanks and vapor recovery unit.
5. The vapor collection and vapor disposal equipment must be designed and operated to prevent gauge pressure in the tank truck from exceeding 18 in H20 and prevent vacuum from exceeding 6 in H20.
6. Testing to determine compliance with subdivision 1 of this subsection shall be conducted and reported and data shall be reduced as set forth in procedures approved by the board using test methods specified there. All tests shall be conducted by, or under the direction of, a person qualified by training or experience in the field of air pollution testing, or tank truck maintenance and testing and approved by the board.
7. Monitoring to confirm the continuing existence of leak tight conditions specified in subdivision 4 of this subsection shall be conducted as set forth in procedures approved by the board using test methods specified there.
8. Owners of tank trucks and account trucks subject to the provisions of subdivision 1 of this subsection shall certify each year that the trucks are vapor tight in accordance with test procedures specified in subdivision 6 of this subsection. Trucks that are not vapor tight must be repaired within 15 days of the test and be tested and certified as vapor tight.
9. Each truck subject to the provisions of subdivision 1 of this subsection shall have information displayed on the tank indicating the expiration date of the certification and such other information as may be needed by the board to determine the validity of the certification. The means of display and location of this information shall be in a manner acceptable to the board.
10. An owner of a vapor collection/control system shall repair and retest the system within 15 days of the testing, if it exceeds the limit specified in subdivision 4 of this subsection.
11. The owner of a tank/account truck or vapor collection/control system or both subject to the provisions of this section shall maintain records of all certification testing and repairs. The records must identify the tank/account truck, vapor collection system, or vapor control system; the date of the test or repair; and, if applicable, the type of repair and the date of retest. The records must be maintained in a legible, readily available condition for at least two years after the date testing or repair was completed.
12. The records of certification tests required by subdivision 11 of this subsection shall, as a minimum, contain the following:
a. The tank/account truck tank identification number;
b. The initial test pressure and the time of the reading;
c. The final test pressure and the time of the reading;
d. The initial test vacuum and the time of the reading;
e. The final test vacuum and the time of the reading; and
f. Name and the title of the person conducting the test.
13. Copies of all records and reports required by this section shall immediately be made available to the board, upon verbal or written request, at any reasonable time.
14. The board may, at any time, monitor a tank/account truck, vapor collection system, or vapor control system by the method referenced in subdivision 6 or 7 of this subsection to confirm continuing compliance with subdivision 1 or 4 of this subsection.
15. If, after over one year of monitoring (i.e., at least two complete annual checks), the owner of a truck subject to the provisions of subdivision 6 of this subsection feels that modification of the requirements are in order, the owner may request in writing to the board that a revision be made. The request should include data that have been developed to justify any modifications in the monitoring schedule. On the other hand, if the board finds an excessive number of leaks during an inspection, or if the owner finds an excessive number of leaks during scheduled monitoring, consideration shall be given to increasing the frequency of inspection.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from VR120-04-3703, eff. January 1, 1993; amended, Virginia Register Volume 20, Issue 12, eff. March 24, 2004; Volume 31, Issue 21, eff. July 30, 2015.
9VAC5-40-5230. Control technology guidelines.
A. Petroleum liquid storage-fixed roof tanks.
1. The tank should be a pressure tank maintaining working pressure sufficient at all times to prevent vapor loss to the atmosphere, or be designed and equipped with one of the following vapor control systems:
a. An internal floating roof resting on the surface of the liquid contents and equipped with a closure seal, or seals, to close the space between the roof edge and tank shell. All tank gauging and sampling devices should be vapor tight except when gauging or sampling is taking place.
b. Any system of equal or greater control efficiency to the system in subdivision A 1 a of this section, provided such system is approved by the board.
2. There should be no visible holes, tears or other openings in the seal or any seal fabric.
3. All openings, except stub drains, should be equipped with a cover, seal or lid. The cover, seal or lid should be in a closed position at all times except when the device is in actual use. Automatic bleeder vents should be closed at all times except when the roof is floated off or landed on the roof leg supports. Rim vents, if provided, should be set to open when the roof is being floated off the roof leg supports or at the manufacturer's recommended setting.
4. The exterior above ground surfaces (exposed to sunlight) should be painted white, light pastels, or light metallic and such exterior paint should be periodically maintained in good condition. Repainting may be performed during normal maintenance periods.
B. Petroleum liquid storage-floating roof tanks.
1. The tank should be designed and equipped with one of the following vapor control systems:
a. An external floating roof resting on the surface of the liquid contents and equipped with a seal closure device (meeting the specifications set forth in subdivisions B 2 and 3 of this section) to close the space between the roof edge and tank shell. All tank gauging and sampling devices should be vapor tight except when gauging or sampling is taking place.
b. Any system of equal or greater control efficiency to the system in subdivision B 1 a of this section, provided such system is approved by the board.
2. Unless the tank is a welded tank fitted with a metallic-type shoe seal which has a secondary seal from the top to the shoe seal to the tank wall (a shoe-mounted secondary), the tank should be fitted with a continuous secondary seal extending from the floating roof to the tank wall (a rim-mounted secondary) if:
a. The tank is a welded tank, the true vapor pressure of the contained liquid is 4.0 psi or greater, and the primary seal is one of the following:
(1) A metallic-type shoe seal.
(2) A liquid-mounted foam seal.
(3) A liquid-mounted liquid-filled type seal.
(4) Any other seal closure device which can be demonstrated equivalent to the primary seals specified in subdivisions B 2 a (1) through (3) of this section.
b. The tank is a riveted tank, the true vapor pressure of the contained liquid is 1.5 psi, or greater, and the seal closure device is as described in subdivision B 2 a of this section.
c. The tank is a welded or riveted tank, the true vapor pressure of the contained liquid is 1.5 psi, or greater, and the primary seal is vapor mounted. When such primary seal closure device can be demonstrated equivalent to the primary seals described in subdivision B 2 a of this section, the provisions of that subdivision apply.
3. The seal closure devices should meet the following requirements:
a. There should be no visible holes, tears or other openings in the seal or any seal fabric.
b. The seal should be intact and uniformly in place around the circumference of the floating roof between the floating roof and the tank wall.
c. The areas where the gap between the secondary seal, installed pursuant to subdivision B 2 c of this section, and the tank wall exceeds 1/8 inch in width shall be calculated in square inches. The sum of all such areas shall not exceed 1.0 square inch per foot of tank diameter.
4. All openings, except for automatic bleeder vents, rim space vents and leg sleeves, should provide a projection below the liquid surface. All openings, except stub drains, should be equipped with a cover, seal or lid. The cover, seal or lid should be in a closed position at all times except when the device is in actual use. Automatic bleeder vents should be closed at all times except when the roof is floated off or landed on the roof leg supports. Rim vents, if provided, should be set to open when the roof is being floated off the roof leg supports or at the manufacturer's recommended setting. Any emergency roof drain should be provided with a slotted membrane fabric cover or equivalent cover that covers at least 90% of the area of the opening.
5. The exterior above ground surfaces (exposed to sunlight) should be painted white, light pastels, or light metallic and such exterior paint should be periodically maintained in good condition. Repainting may be performed during normal maintenance periods.
C. Gasoline bulk loading-bulk terminals. The control system should consist of the following:
1. A vapor collection and disposal system with the vapor disposal portion consisting of one of the following:
a. Compression-refrigeration-adsorption system;
b. Refrigeration system;
c. Oxidation system; or
d. Any system of equal or greater control efficiency to the systems in subdivisions C 1 a through c of this section, provided such system is approved by the board.
2. A vapor collection and disposal system with the vapor collection portion meeting the following criteria:
a. Loading should be accomplished in such manner that all displaced vapor and air will be vented only to the vapor disposal system. Measures should be taken to prevent liquid drainage from the loading device when it is not in use or to accomplish substantially complete drainage before the loading device is disconnected;
b. The pressure relief valves on storage containers and tank trucks should be set to release at no less than 0.7 psi or the highest possible pressure in accordance with the following National Fire Prevention Association Standards: "Standard for Tank Vehicles for Flammable and Combustible Liquids," "Flammable and Combustible Liquids Code," "Code for Motor Fuel Dispensing Facilities and Repair Garages" (see 9VAC5-20-21);
c. Pressure in the vapor collection lines should not exceed tank truck pressure relief valve settings; and
d. All loading and vapor lines should be equipped with fittings which make vapor tight connections and which close when disconnected.
D. Gasoline bulk loading-bulk plants.
1. The control system should consist of one of the following:
a. Submerged filling of account trucks and storage tanks (either top-submerged or bottom-fill) plus a vapor balance (displacement) system to control volatile organic compounds displaced by gasoline delivery to the storage tank and account truck;
b. Top loading vapor recovery method of filling account trucks and storage tanks plus a vapor balance (displacement) system to control volatile organic compounds displaced by gasoline delivery to the storage tank and account truck; or
c. Any system of equal or greater control efficiency to the system in subdivision D 1 a or b of this section, provided such system is approved by the board.
2. The control system in subdivisions D 1 a and b of this section should meet the following equipment specifications and operating procedures:
a. For top-submerged and bottom-fill. The fill pipe should extend to within six inches of the bottom of the storage tank and account truck during top-submerged filling operations. Any bottom fill is acceptable if the inlet is flush with the tank bottom; and
b. For the balance system:
(1) There should be no leaks in the account trucks' and tank trucks' pressure vacuum relief valves and hatch covers, nor tank trucks, account trucks, storage tanks or associated vapor return lines during loading or unloading operations.
(2) The pressure relief valves on storage tanks, account trucks and tank trucks should be set to release at no less than 0.7 psi or the highest possible pressure in accordance with the following National Fire Prevention Association Standards: "Standard for Tank Vehicles for Flammable and Combustible Liquids," "Flammable and Combustible Liquids Code," "Code for Motor Fuel Dispensing Facilities and Repair Garages" (see 9VAC5-20-21).
(3) Pressure in the vapor collection lines should not exceed account truck or tank truck pressure relief valve settings.
(4) All loading and vapor lines should be equipped with fittings which make vapor tight connections and which close when disconnected.
E. Transfer of gasoline-gasoline dispensing facilities-stage I vapor control systems. The control system should consist of the following:
1. A submerged fill pipe;
2. A vapor control system with the vapor recovery portion consisting of one of the following:
a. A vapor tight return line from the storage container to the tank truck which shall be connected before gasoline is transferred into the container;
b. Any adsorption system or condensation system; or
c. Any system of equal or greater control efficiency to the systems in subdivision E 2 a or b of this section, provided such system is approved by the board.
3. A vapor control system with the vapor balance portion meeting the following criteria:
a. There should be no leaks in the tank truck's pressure vacuum relief valves and hatch covers, nor truck tanks, storage tanks and associated vapor return lines during loading or unloading operations;
b. The pressure relief valves on storage containers and tank trucks should be set to release at no less than 0.7 psi or the highest possible pressure in accordance with the following National Fire Prevention Association Standards: "Standard for Tank Vehicles for Flammable and Combustible Liquids," "Flammable and Combustible Liquids Code," "Code for Motor Fuel Dispensing Facilities and Repair Garages" (see 9VAC5-20-21);
c. Pressure in the vapor collection lines should not exceed tank truck pressure relief valve settings; and
d. All loading and vapor lines should be equipped with fittings which make vapor tight connections and which close when disconnected.
F. Transfer of gasoline-gasoline dispensing facilities-Stage II vapor recovery systems.
1. Stage II vapor recovery systems shall be limited to those certified systems approved under the provisions of AQP-9, Procedures for Implementation of Regulations Covering Stage II Vapor Recovery Systems for Gasoline Dispensing Facilities (see 9VAC5-20-121), which utilize coaxial hoses and vapor check valves in the nozzle or remote vapor check valves which do not impede the performance of the functional tests required in subdivision F 6 b of 9VAC5-40-5220.
2. Stage II vapor recovery systems installed prior to January 1, 1993, must meet the specifications of a system certified by the California Air Resources Board. Owners of Stage II vapor recovery systems utilizing remote check valves which will impede the performance of the functional tests required in subdivision F 6 b of 9VAC5-40-5220 and dual vapor recovery hoses shall replace these components with check valves in the nozzle and with coaxial hoses by January 1, 1995.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3704, eff. January 1, 1993; amended, Virginia Register Volume 18, Issue 7, eff. February 1, 2002.
9VAC5-40-5240. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3705, eff. January 1, 1985.
9VAC5-40-5250. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3706, eff. January 1, 1985.
9VAC5-40-5260. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3707, eff. January 1, 1985.
9VAC5-40-5270. Standard for toxic pollutants.
The provisions of Article 4, Emission Standards for Toxic Pollutants from Existing Sources, (9VAC5-60-200 et seq.) of Part I of Hazardous Air Pollutant Sources apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from VR120-04-3708, eff. January 1, 1985; amended, Virginia Register Volume 31, Issue 21, eff. July 30, 2015.
9VAC5-40-5280. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3709, eff. January 1, 1985.
9VAC5-40-5290. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3710, eff. January 1, 1985.
9VAC5-40-5300. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3711, eff. January 1, 1985.
9VAC5-40-5310. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3712, eff. January 1, 1985.
9VAC5-40-5320. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3713, eff. January 1, 1985.
9VAC5-40-5330. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3714, eff. January 1, 1985.
9VAC5-40-5340. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3715, eff. January 1, 1985.
Article 38
Emission Standards for Dry Cleaning Systems (Rule 4-38) [Repealed]
9VAC5-40-5350. (Repealed.)
Article 38
Emission Standards for Dry Cleaning Systems (Rule 4-38) [Repealed]
Historical Notes
Derived from VR120-04-3801, eff. July 1, 1991, and from VR120-04-3802 to VR120-04-3814, eff. January 1, 1985; repealed, Virginia Register Volume 15, Issue 12, eff. April 1, 1999.
9VAC5-40-5490. (Repealed.)
Historical Notes
Derived from VR120-04-3901, eff. July 1, 1991; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5500. (Repealed.)
Historical Notes
Derived from VR120-04-3902, eff. January 1, 1985; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5510. (Repealed.)
Historical Notes
Derived from VR120-04-3903, eff. January 1, 1985; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5520. (Repealed.)
Historical Notes
Derived from VR120-04-3904, eff. January 1, 1985; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5530. (Repealed.)
Historical Notes
Derived from VR120-04-3905, eff. January 1, 1985; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5540. (Repealed.)
Historical Notes
Derived from VR120-04-3906, eff. January 1, 1985; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5550. (Repealed.)
Historical Notes
Derived from VR120-04-3907, eff. January 1, 1985; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5560. (Repealed.)
Historical Notes
Derived from VR120-04-3908, eff. January 1, 1985; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5570. (Repealed.)
Historical Notes
Derived from VR120-04-3909, eff. January 1, 1985; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5580. (Repealed.)
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-3910, eff. January 1, 1985; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5590. (Repealed.)
Historical Notes
Derived from VR120-04-3911, eff. January 1, 1985; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
Article 40
Emission Standards for Open Burning (Rule 4-40) (Repealed)
9VAC5-40-5600. (Repealed.)
Article 40
Emission Standards for Open Burning (Rule 4-40) (Repealed)
Historical Notes
Derived from VR120-04-4001, eff. January 1, 1988; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996; Volume 23, Issue 1, eff. October 18, 2006; repealed, Virginia Register Volume 25, Issue 12, eff. March 18, 2009.
9VAC5-40-5610. (Repealed.)
Historical Notes
Derived from VR120-04-4002, eff. January 1, 1988; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996; Volume 23, Issue 1, eff. October 18, 2006; repealed, Virginia Register Volume 25, Issue 12, eff. March 18, 2009.
9VAC5-40-5620. (Repealed.)
Historical Notes
Derived from VR120-04-4003, eff. January 1, 1988; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996; Volume 23, Issue 1, eff. October 18, 2006; repealed, Virginia Register Volume 25, Issue 12, eff. March 18, 2009.
9VAC5-40-5630. (Repealed.)
Historical Notes
Derived from VR120-04-4004, eff. January 1, 1988; amended, Virginia Register Volume 12, Issue 11, eff. April 1, 1996; Volume 23, Issue 1, eff. October 18, 2006; repealed, Virginia Register Volume 25, Issue 12, eff. March 18, 2009.
9VAC5-40-5631. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 13, Issue 18, eff. July 1, 1997; amended, Virginia Register Volume 23, Issue 1, eff. October 18, 2006; repealed, Virginia Register Volume 25, Issue 12, eff. March 18, 2009.
9VAC5-40-5640. (Repealed.)
Historical Notes
Derived from VR120-04-4005, eff. January 1, 1988; repealed, Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-5641. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 13, Issue 18, eff. July 1, 1997; amended, Virginia Register Volume 23, Issue 1, eff. October 18, 2006; Errata, 23:5 VA.R. 791 November 13, 2006; repealed, Virginia Register Volume 25, Issue 12, eff. March 18, 2009.
9VAC5-40-5645. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996; repealed, Virginia Register Volume 25, Issue 12, eff. March 18, 2009.
Article 41
Emission Standards for Mobile Sources (Rule 4-41)
9VAC5-40-5650. Applicability and designation of affected facility.
Article 41
Emission Standards for Mobile Sources (Rule 4-41)
A. Except as provided in subsection C of this section, the affected facility to which the provisions of this article apply is each mobile source.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
C. The provisions of this article do not apply to mobile sources used solely for ceremonial purposes, antiques and others of historical significance.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-4101, eff. January 1, 1985.
9VAC5-40-5660. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Mobile sources" means any vehicle, including, but not limited to, any motor vehicle (automobile, truck, bus, etc.) or other landcraft; airplane or other aircraft; locomotive or other rail vehicle; ship, boat or other watercraft, which emits or may emit any air pollutant.
"Motor vehicle" means any powered conveyance of a type normally licensed by the Virginia Department of Motor Vehicles.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-4102, eff. January 1, 1985.
9VAC5-40-5670. Motor vehicles.
A. Emission control systems.
1. No owner or other person shall cause or permit the removal, disconnection or disabling of a crankcase emission control system or device, exhaust emission control system or device, fuel evaporative emission control system or device, or other air pollution control system or device which has been installed on a motor vehicle in accordance with federal laws and regulations while such motor vehicle is operating in the Commonwealth of Virginia.
2. No owner or other person shall attempt to defeat the purpose of any such motor vehicle pollution control system or device by installing any part or component which is not a standard factory replacement part or component of the device.
3. No motor vehicle or engine shall be operated with the motor vehicle pollution control system or device removed or otherwise rendered inoperable.
4. The provisions of this section shall not prohibit or prevent shop adjustments or replacement of equipment for maintenance or repair, or the conversion of engines to low polluting fuels such as, but not limited to, natural gas or propane.
B. Visible emissions.
1. No owner or other person shall cause or permit the emission of visible air pollutants from gasoline-powered motor vehicles for longer than five consecutive seconds after the engine has been brought up to operating temperature.
2. No owner or other person shall cause or permit the emission of visible air pollutants from diesel-powered motor vehicles of a density equal to or greater than 20% opacity for longer than 10 consecutive seconds after the engine has been brought up to operating temperature.
C. In commercial or residential urban areas, propulsion engines of motor vehicles licensed for commercial or public service use shall not be left running for more than three minutes when the vehicle is parked, unless the propulsion engine is providing auxiliary power for other than heating or air conditioning; except that:
1. Tour buses may idle for up to 10 minutes during hot weather in order to maintain power to the air conditioning system; and
2. Diesel powered vehicles may idle for up to 10 minutes to minimize restart problems.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-4103, eff. January 1, 1985.
9VAC5-40-5680. Other mobile sources.
A. General. All mobile sources operating within Virginia, including the air space over this Commonwealth, shall control their emissions in strict accordance with the applicable federal laws and regulations.
B. Visible emissions. The provisions of 9VAC5-40-80 shall apply to the discharge of visible emissions from all mobile sources, unless specified otherwise in subsection C of this section.
C. Exceptions.
1. Aircraft. Subsection B of this section shall not apply to aircraft.
2. Diesel locomotives. Visible emissions from operating diesel-powered locomotives shall not exceed a density greater than 30% opacity unless the locomotive is operating under any of the following conditions:
a. Accelerating under load, and then only for a maximum of 40 consecutive seconds for stabilization of the new operating condition;
b. Being loaded after a period of idle, and then only for a maximum period of four consecutive minutes after the changed condition;
c. Started cold, and then only for a maximum of 30 consecutive minutes after such a start; or
d. Being tested, adjusted, or broken in after rebuilding or repair, and then only for maximum periods of 3 consecutive minutes for an aggregate of no more than 10 minutes in any 60-minute period.
3. Ships and other watercraft. Visible emissions in excess of subsection B of this section are authorized when not at dock and for brief periods when at dock under the following conditions:
a. During dock trials as required to test and calibrate the ship's machinery control systems;
b. When lighting off a cold machinery plant and getting under way;
c. When used on shore to simulate dock or sea trials; or
d. When soot blowing. Soot blowing shall be limited to once in each 24-hour period and shall be allowed only when wind conditions and direction are such as to prevent a public nuisance or hazard to the health and safety of persons and property both ashore and afloat.
4. Other diesel-powered mobile sources. Visible emissions from diesel-powered mobile sources which are not otherwise governed by these regulations shall not exceed 20% opacity for longer than 10 consecutive seconds after the engine has been brought up to operating temperature.
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-4104, eff. January 1, 1985.
9VAC5-40-5690. Export/import of motor vehicles.
A. Any person may remove the catalyst and restrictive filler inlet from used motor vehicles scheduled for shipment overseas provided that:
1. The export/import of the motor vehicle meets the provisions of subsection B of this section; and
2. The removal of the emission control devices does not take place prior to 10 days before the vehicle is turned in to the port authorities and the reinstallation of the emission control devices takes place within 10 days after receipt of the vehicle by the owner from the port authorities.
B. To be exempted under the provisions of subsection A of this section, the motor vehicle must:
1. Be exported/imported under a U.S. Environmental Protection Agency (EPA) approved catalyst control program; or
2. If not under an EPA program, upon reimportation to the United States must be entered through U.S. Customs under cash bond and formal entry procedures (19 CFR 12 - Special classes of merchandise) and must be modified to bring it into conformity with applicable federal motor vehicle emission standards (40 CFR 86 - Control of air pollution from new motor vehicle engines: Certification and test procedures).
Statutory Authority
§§ 10.1-1307 and 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from VR120-04-4105, eff. October 1, 1986.
9VAC5-40-5700. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5710. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; repealed, Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5720. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; repealed, Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5730. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; repealed, Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5740. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; repealed, Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5750. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; repealed, Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5760. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; repealed, Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-5770. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; repealed, Volume 28, Issue 25, eff. September 27, 2012.
Article 43
Emission Standards for Municipal Solid Waste Landfills (Rule 4-43)
9VAC5-40-5800. Applicability and designation of affected facility.
Article 43
Emission Standards for Municipal Solid Waste Landfills (Rule 4-43)
A. The affected facility to which the provisions of this article apply is each municipal solid waste (MSW) landfill which commenced construction, reconstruction, or modification before May 30, 1991.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
C. For purposes of obtaining a federal operating permit, the owner of an MSW landfill subject to this article with a design capacity less than 2.5 million megagrams or 2.5 million cubic meters is not subject to the requirement to obtain a federal operating permit for the landfill, unless the landfill is otherwise subject to federal operating permit requirements. For purposes of submitting a timely application for a federal operating permit, the owner of an MSW landfill subject to this article with a design capacity greater than or equal to 2.5 million megagrams and 2.5 million cubic meters on the effective date of EPA approval of the board's program under § 111(d) of the federal Clean Air Act, and otherwise not subject to federal operating permit requirements, shall submit an operating permit application as provided in 9VAC5-80-80 C, even if the design capacity report is submitted earlier.
D. When an MSW landfill subject to this article becomes closed, the owner is no longer subject to the requirement to maintain a federal operating permit for the landfill if the landfill is not otherwise subject to federal operating permit requirements and if either of the following conditions is met:
1. The landfill was never subject to the requirement for a control system under 9VAC5-40-5820 C 2; or
2. The owner meets the conditions for control system removal specified in 9VAC5-40-5820 C 2 e.
E. Activities required by or conducted pursuant to a CERCLA, RCRA, or board remedial action are not considered construction, reconstruction, or modification for the purposes of this article.
F. Each affected facility with a design capacity greater than 2.5 million megagrams or 2.5 million cubic meters shall demonstrate compliance with this article by demonstrating compliance with the provisions of Article 43.1 (9VAC5-40-5925 et seq.) of this chapter.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999; Volume 20, Issue 8, eff. January 29, 2004; Volume 33, Issue 10, eff. February 22, 2017.
9VAC5-40-5810. Definitions.
A. For the purpose of applying this article in the context of the Regulations for the Control and Abatement of Air Pollution and related uses, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10), unless otherwise required by context.
C. Terms defined.
"Active collection system" means a gas collection system that uses gas mover equipment.
"Active landfill" means a landfill in which solid waste is being placed or a landfill that is planned to accept waste in the future.
"CERCLA" means the federal Comprehensive Environmental Response, Compensation and Liability Act (42 USC § 9601 et seq.).
"Closed landfill" means a landfill in which solid waste is no longer being placed, and in which no additional solid wastes will be placed without first filing a notification of modification, as prescribed under 40 CFR 60.7(a)(4), with the board. Once a notification of modification has been filed, and additional solid waste is placed in the landfill, the landfill is no longer closed.
"Closure" means that point in time when a landfill becomes a closed landfill.
"Commenced" means that an owner has undertaken a continuous program of construction or modification or that an owner has entered into a contractual obligation to undertake and complete, within a reasonable time, a continuous program of construction or modification.
"Commercial waste" means all types of solid waste generated by stores, offices, restaurants, warehouses, and other nonmanufacturing activities, excluding construction, household, and industrial wastes.
"Construction" means fabrication, erection, or installation of an affected facility.
"Controlled landfill" means any landfill at which collection and control systems are required under this article as a result of the nonmethane organic compounds emission rate. The landfill is considered controlled at the time a collection and control system design plan is submitted in compliance with 9VAC5-40-5820 C 2 a.
"Design capacity" means the maximum amount of solid waste a landfill can accept, as indicated in terms of volume or mass in the most recent permit issued by the department under Part V (9VAC20-81-400 et seq.) of the Solid Waste Management Regulations, plus any in-place waste not accounted for in the most recent permit, or as calculated using good engineering practices acceptable to the board. If the owner chooses to convert the design capacity from volume to mass or from mass to volume to demonstrate that its design capacity is less than (i) 1.0 million megagrams or 1.0 million cubic meters in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 2.5 million megagrams or 2.5 million cubic meters in the remaining areas of the Commonwealth, the calculation must include a site-specific density, which must be recalculated annually.
"Disposal facility" means all contiguous land and structures, other appurtenances, and improvements on the land used for the disposal of solid waste.
"Emission rate cutoff" means the threshold annual emission rate to which a landfill compares its estimated emission rate to determine if control under the regulation is required.
"Enclosed combustor" means an enclosed firebox which maintains a relatively constant limited peak temperature generally using a limited supply of combustion air. An enclosed flare is considered an enclosed combustor.
"Federal operating permit" means a permit issued under Article 1 (9VAC5-80-50 et seq.) of Part II of 9VAC5 Chapter 80.
"Flare" means an open combustor without enclosure or shroud.
"Gas mover equipment" means the equipment (i.e., fan, blower, compressor) used to transport landfill gas through the header system.
"Household waste" mean any solid waste, including garbage, trash and refuse, derived from households (including, but not limited to, single and multiple residences, hotels and motels, bunkhouses, ranger stations, crew quarters, campgrounds, picnic grounds and day-use recreational areas). For the purposes of determining capacity as required by 9VAC5-40-5820 and NMOC emission rates as required by 9VAC5-40-5860, household waste includes sanitary waste (septage) in septic tanks.
"Industrial solid waste" means any solid waste generated by manufacturing or industrial processes that is not a hazardous waste regulated under Subtitle C (42 USC § 6921 et seq.) of RCRA (as reflected in 40 CFR Parts 264 and 265) and implemented by the department in 9VAC20 Chapter 60 (9VAC20-60, Virginia Hazardous Waste Management Regulations). Such waste may include, but is not limited to, waste resulting from the following manufacturing processes: electric power generation; fertilizer and agricultural chemicals; food and related products and byproducts; inorganic chemicals; iron and steel manufacturing; leather and leather products; nonferrous metals manufacturing and foundries; organic chemicals; plastics and resins manufacturing; pulp and paper industry; rubber and miscellaneous plastic products; stone, glass, clay, and concrete products; textile manufacturing; transportation equipment; and water treatment. This term does not include mining waste or oil and gas waste.
"Interior well" means any well or similar collection component located inside the perimeter of the landfill waste. A perimeter well located outside the landfilled waste is not an interior well.
"Landfill" means an area of land or an excavation in which wastes are placed for permanent disposal, and that is not a land application unit, surface impoundment, injection well, or waste pile as those terms are defined under 9VAC20-81.
"Landfill gas" means any gas derived from the decomposition of organic waste deposited in an MSW landfill or from the evolution of volatile organic species in the waste. Emissions from MSW landfills is equivalent to landfill gas emissions.
"Lateral expansion" means a horizontal expansion of the waste boundaries of an existing MSW landfill. A lateral expansion is not a modification unless it results in an increase in the design capacity of the landfill.
"Modification" means an increase in the permitted volume design capacity of the landfill by either horizontal or vertical expansion based on its permitted design capacity as of May 30, 1991. Modification does not occur until the owner commences construction on the horizontal or vertical expansion.
"Municipal solid waste landfill" or "MSW landfill" means an entire disposal facility in a contiguous geographical space where household waste is placed in or on land. An MSW landfill may also receive other types of solid wastes regulated under Subtitle D (42 USC § 6941 et seq.) of RCRA (as reflected in 40 CFR 257.2) and implemented by the department in 9VAC20-81 (Solid Waste Management Regulations) such as commercial solid waste, nonhazardous sludge, conditionally exempt small quantity generator waste, and nonhazardous industrial solid waste. Portions of an MSW landfill may be separated by access roads. An MSW landfill may be publicly or privately owned. An MSW landfill may be a new MSW landfill, an existing MSW landfill, or a lateral expansion.
"Municipal solid waste landfill emissions" or "MSW landfill emissions" means gas generated by the decomposition of organic waste deposited in an MSW landfill or derived from the evolution of organic compounds in the waste.
"NMOC" means nonmethane organic compounds, as measured according to the provisions of 9VAC5-40-5860 B through E.
"Nondegradable waste" means any waste that does not decompose through chemical breakdown or microbiological activity. Examples include, but are not limited to, concrete, municipal waste combustor ash, and metals.
"Passive collection system" means a gas collection system that solely uses positive pressure within the landfill to move the gas rather than using gas mover equipment.
"RCRA" means the federal Resource Conservation and Recovery Act (42 USC § 6901 et seq.).
"Refuse" means trash, rubbish, garbage, and other forms of solid or liquid waste, including, but not limited to, wastes resulting from residential, agricultural, commercial, industrial, institutional, trade, construction, land clearing, forest management, and emergency operations.
"Sludge" means any solid, semi-solid, or liquid waste generated from a municipal, commercial, or industrial wastewater treatment plant, water supply treatment plant, or air pollution control facility exclusive of the treated effluent from a wastewater treatment plant.
"Solid waste" means any garbage, sludge from a wastewater treatment plant, water supply treatment plant, or air pollution control facility and other discarded material, including solid, liquid, semi-solid, or contained gaseous material resulting from industrial, commercial, mining, and agricultural operations, and from community activities, but does not include solid or dissolved material in domestic sewage, or solid or dissolved materials in irrigation return flows or industrial discharges that are point sources subject to permits under 33 USC § 1342, or source, special nuclear, or byproduct material as defined by the Atomic Energy Act of 1954 (42 USC § 2011 et seq.). For more detail, see 9VAC20-81-95 of the Solid Waste Management Regulations.
"Sufficient density" means any number, spacing, and combination of collection system components, including vertical wells, horizontal collectors, and surface collectors, necessary to maintain emission and migration control as determined by measures of performance set forth in this part.
"Sufficient extraction rate" means a rate sufficient to maintain a negative pressure at all wellheads in the collection system without causing air infiltration, including any wellheads connected to the system as a result of expansion or excess surface emissions, for the life of the blower.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999; Volume 20, Issue 8, eff. January 29, 2004; Volume 27, Issue 23, eff. August 17, 2011.
9VAC5-40-5820. Standard for air emissions.
A. This section shall apply to affected facilities that have accepted waste any time since November 8, 1987, or have additional design capacity available for future waste deposition, and meet the design capacity and emission rate applicability criteria in subdivisions A 1 or A 2 of this section.
1. For affected facilities located in the Northern Virginia Volatile Organic Compound Emissions Control Area as designated in 9VAC5-20-206:
a. A design capacity greater than or equal to 1.0 million megagrams and 1.0 million cubic meters; and
b. A nonmethane organic compound emission rate of 23 megagrams per year or more as determined using test procedures under 9VAC5-40-5860.
2. For affected facilities located in the remaining areas of the Commonwealth:
a. A design capacity greater than or equal to 2.5 million megagrams or 2.5 million cubic meters; and
b. A nonmethane organic compound emission rate of 50 megagrams per year or more as determined using test procedures under 9VAC5-40-5860.
B. Each owner of an MSW landfill having a design capacity less than (i) 1.0 million megagrams or 1.0 million cubic meters in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 2.5 million megagrams or 2.5 million cubic meters in the remaining areas of the Commonwealth shall submit an initial design capacity report to the board as provided in 9VAC5-40-5880 C no later than June 30, 1999. The landfill may calculate design capacity in either megagrams or cubic meters for comparison with the design capacity applicability criteria in subsection A of this section. Any density conversions shall be documented and submitted with the report. Submittal of the initial design capacity report shall fulfill the requirements of this article except as provided for in subdivisions B 1 and B 2 of this section.
1. The owner shall submit to the board an amended design capacity report, as provided for in 9VAC5-40-5880 C 3. If the design capacity increase is the result of a modification, as defined in 9VAC5-40-5810 C, that was commenced on or after May 30, 1991, the landfill is subject to the new source performance standard in Article 5 of 9VAC5 Chapter 50 (9VAC5-50-410) instead of this article. If the design capacity increase is the result of a change in operating practices, density, or some other change that is not a modification, the landfill remains subject to this article.
2. When an increase in the maximum design capacity of a landfill exempted from the provisions of 9VAC5-40-5820 C, 9VAC5-40-5822, 9VAC5-40-5824, 9VAC5-40-5850, 9VAC5-40-5860, 9VAC5-40-5870, 9VAC5-40-5880, and 9VAC5-40-5890 on the basis of the design capacity applicability criteria in subsection A of this section results in a revised maximum design capacity equal to or greater than (i) 1.0 million megagrams or 1.0 million cubic meters in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 2.5 million megagrams or 2.5 million cubic meters in the remaining areas of the Commonwealth, the owner shall comply with the provisions of subsection C of this section.
C. Each owner of an MSW landfill having a design capacity greater than or equal to (i) 1.0 million megagrams and 1.0 million cubic meters in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 2.5 million megagrams and 2.5 million cubic meters in the remaining areas of the Commonwealth shall either install a collection and control system as provided in subdivision C 2 of this section or calculate an initial NMOC emission rate for the landfill using the procedures specified in 9VAC5-40-5860. The NMOC emission rate shall be recalculated annually, except as provided in 9VAC5-40-5880 D 1 b.
1. If the calculated NMOC emission rate is less than (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, the owner shall:
a. Submit an annual emission report to the board, except as provided for in 9VAC5-40-5880 D 1 b; and
b. Recalculate the NMOC emission rate annually using the procedures specified in 9VAC5-40-5860 B 1 until such time as the calculated NMOC emission rate is greater than or equal to (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, or the landfill is closed.
(1) If the NMOC emission rate, upon initial calculation or annual recalculation required in subdivision C 1 b of this section, is greater than or equal to (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, the owner shall install a collection and control system in compliance with subdivision C 2 of this section.
(2) If the landfill is permanently closed, a closure notification shall be submitted to the board as provided for in 9VAC5-40-5880 F.
2. If the calculated NMOC emission rate is greater than or equal to (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, the owner shall:
a. Submit a collection and control system design plan prepared by a professional engineer to the board within one year:
(1) The collection and control system as described in the plan shall meet the design requirements of subdivision C 2 b of this section.
(2) The collection and control system design plan shall include any alternatives to the operational standards, test methods, procedures, compliance measures, monitoring, recordkeeping or reporting provisions of 9VAC5-40-5822, 9VAC5-40-5850, 9VAC5-40-5860, 9VAC5-40-5870, 9VAC5-40-5880, and 9VAC5-40-5890 proposed by the owner.
(3) The collection and control system design plan shall either conform with specifications for active collection systems in 9VAC5-40-5824 or include a demonstration to the board's satisfaction of the sufficiency of the alternative provisions to 9VAC5-40-5824.
(4) The board will review the information submitted under subdivisions C 2 a (1), (2) and (3) of this section and either approve it, disapprove it, or request that additional information be submitted. Because of the many site-specific factors involved with landfill gas system design, alternative systems may be necessary. A wide variety of system designs are possible, such as vertical wells, combination horizontal and vertical collection systems, or horizontal trenches only, leachate collection components, and passive systems. All design plan changes shall be submitted to the board and may be implemented only upon approval of the board.
b. Install a collection and control system that captures the gas generated within the landfill as required by subdivision C 2 b (1) or (2) of this section within 30 months after the first annual report in which the emission rate equals or exceeds (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, unless Tier 2 or Tier 3 sampling demonstrates that the emission rate is less than (a) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (b) 50 megagrams per year in the remaining areas of the Commonwealth, as specified in 9VAC5-40-5880 E 1 or E 2.
(1) An active collection system shall:
(a) Be designed to handle the maximum expected gas flow rate from the entire area of the landfill that warrants control over the intended use period of the gas control or treatment system equipment;
(b) Collect gas from each area, cell, or group of cells in the landfill in which the initial solid waste has been placed for a period of:
(i) Five years or more if active; or
(ii) Two years or more if closed or at final grade;
(c) Collect gas at a sufficient extraction rate;
(d) Be designed to minimize off-site migration of subsurface gas.
(2) A passive collection system shall:
(a) Comply with the provisions specified in subdivisions C 2 b (1) (a), (b), and (d) of this section.
(b) Be installed with liners on the bottom and all sides in all areas in which gas is to be collected. The liners shall be installed as required under 9VAC20-81-130.
c. Route all the collected gas to a control system that complies with the requirements in either subdivision C 2 c (1), (2) or (3) of this section.
(1) An open flare designed and operated in accordance with 40 CFR 60.18.
(2) A control system designed and operated to reduce NMOC by 98 weight-percent, or, when an enclosed combustion device is used for control, to either reduce NMOC by 98 weight-percent or reduce the outlet NMOC concentration to less than 20 parts per million by volume, dry basis as hexane at 3.0% oxygen. The reduction efficiency or parts per million by volume shall be established by an initial compliance test to be completed no later than 180 days after the initial startup of the approved control system using the test methods specified in 9VAC5-40-5860 E.
(a) If a boiler or process heater is used as the control device, the landfill gas stream shall be introduced into the flame zone.
(b) The control device shall be operated within the parameter ranges established during the initial or most recent compliance test. The operating parameters to be monitored are specified in 9VAC5-40-5870.
(3) Route the collected gas to a treatment system that processes the collected gas for subsequent sale or use. All emissions from any atmospheric vent from the gas treatment system shall be subject to the requirements of subdivision C 2 c (1) or (2) of this section.
d. Operate the collection and control device installed to comply with this article in accordance with the provisions of 9VAC5-40-5822, 9VAC5-40-5850, and 9VAC5-40-5870.
e. The collection and control system may be capped or removed provided that all the conditions of subdivisions C 2 e (1), (2), and (3) of this section are met:
(1) The landfill shall be a closed landfill as defined in 9VAC5-40-5810 and under the requirements of 9VAC20-81-160. A closure report shall be submitted to the board as provided in 9VAC5-40-5880 F;
(2) The collection and control system shall have been in operation a minimum of 15 years; and
(3) Following the procedures specified in 9VAC5-40-5860 C, the calculated NMOC gas produced by the landfill shall be less than (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth on three successive test dates. The test dates shall be no less than 90 days apart and no more than 180 days apart.
D. When an MSW landfill subject to this article is closed, the owner is no longer subject to the requirement to maintain a federal operating permit for the landfill if the landfill is not otherwise subject to federal operating permit requirements if either of the following conditions are met:
1. The landfill was never subject to the requirement for a control system under 9VAC5-40-5820 C 2; or
2. The owner meets the conditions for control system removal specified in 9VAC5-40-5820 C 2 e.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999; Volume 20, Issue 8, eff. January 29, 2004; Volume 27, Issue 23, eff. August 17, 2011.
9VAC5-40-5822. Operational standards for collection and control systems.
A. Each owner of an MSW landfill with a gas collection and control system used to comply with the provisions of 9VAC5-40-5820 C 2 b shall comply with the following requirements:
1. Operate the collection system such that gas is collected from each area, cell, or group of cells in the MSW landfill in which solid waste has been in place for:
a. Five years or more if active; or
b. Two years or more if closed or at final grade.
2. Operate the collection system with negative pressure at each wellhead except under the following conditions:
a. A fire or increased well temperature. The owner shall record instances when positive pressure occurs in efforts to avoid a fire. These records shall be submitted with the annual reports as provided in 9VAC5-40-5880 H 1;
b. Use of a geomembrane or synthetic cover. The owner shall develop acceptable pressure limits in the design plan; and
c. A decommissioned well. A well may experience a static positive pressure after shut down to accommodate for declining flows. All design changes shall be approved by the board.
3. Operate each interior wellhead in the collection system with a landfill gas temperature less than 55 degrees Celsius and with either a nitrogen level less than 20% or an oxygen level less than 5.0%. The owner may establish a higher operating temperature, nitrogen, or oxygen value at a particular well. A higher operating value demonstration shall show supporting data that the elevated parameter does not cause fires or significantly inhibit anaerobic decomposition by killing methanogens.
a. The nitrogen level shall be determined using Reference Method 3C in Appendix A of 40 CFR Part 60, unless an alternative method is established as allowed by 9VAC5-40-5820 C 2 a.
b. Unless an alternative method is established as allowed by 9VAC5-40-5820 C 2 a, the oxygen shall be determined by an oxygen meter using Reference Method 3A in Appendix A of 40 CFR Part 60 except that:
(1) The span shall be set so that the regulatory limit is between 20 and 50% of the span;
(2) A data recorder is not required;
(3) Only two calibration gases are required, a zero and span, and ambient air may be used as the span;
(4) A calibration error check is not required; and
(5) The allowable sample bias, zero drift, and calibration drift are ±10%.
4. Operate the collection system so that the methane concentration is less than 500 parts per million above background at the surface of the landfill. To determine if this level is exceeded, the owner shall conduct surface testing around the perimeter of the collection area and along a pattern that traverses the landfill at 30-meter intervals and where visual observations indicate elevated concentrations of landfill gas, such as distressed vegetation and cracks or seeps in the cover. The owner may establish an alternative traversing pattern that ensures equivalent coverage. A surface monitoring design plan shall be developed that includes a topographical map with the monitoring route and the rationale for any site-specific deviations from the 30-meter intervals. Areas with steep slopes or other dangerous areas may be excluded from the surface testing.
5. Operate the system such that all collected gases are vented to a control system designed and operated in compliance with 9VAC5-40-5820 C 2 c. In the event the collection or control system is inoperable, the gas mover system shall be shut down and all valves in the collection and control system contributing to venting of the gas to the atmosphere shall be closed within one hour.
6. Operate the control or treatment system at all times when the collected gas is routed to the system.
B. If monitoring demonstrates that the operational requirement in subdivision A 2, 3 or 4 of this section are not met, corrective action shall be taken as specified in 9VAC5-40-5850 C 3 through 5 or 9VAC5-40-5850 E. If corrective actions are taken as specified in 9VAC5-40-5850, the monitored exceedance is not a violation of the operational requirements in this section.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 15, Issue 12, eff. April 1, 1999; amended, Virginia Register Volume 20, Issue 8, eff. January 29, 2004.
9VAC5-40-5824. Specifications for active collection systems.
A. Each owner seeking to comply with 9VAC5-40-5820 C 2 a shall site active collection wells, horizontal collectors, surface collectors, or other extraction devices at a sufficient density throughout all gas producing areas using the following procedures unless alternative procedures have been approved by the board as provided in 9VAC5-40-5820 C 2 a (3) and (4):
1. The collection devices within the interior and along the perimeter areas shall be certified to achieve comprehensive control of surface gas emissions by a professional engineer. The following issues shall be addressed in the design: depths of refuse, refuse gas generation rates and flow characteristics, cover properties, gas system expandability, leachate and condensate management, accessibility, compatibility with filling operations, integration with closure end use, air intrusion control, corrosion resistance, fill settlement, and resistance to the refuse decomposition heat.
2. The sufficient density of gas collection devices determined in subdivision A 1 of this section shall address landfill gas migration issues and augmentation of the collection system through the use of active or passive systems at the landfill perimeter or exterior.
3. The placement of gas collection devices determined in subdivision A 1 of this section shall control all gas producing areas, except as provided by subdivisions A 3 a and A 3 b of this section.
a. Any segregated area of asbestos or nondegradable material may be excluded from collection if documented as provided under 9VAC5-40-5890 F. The documentation shall provide the nature, date of deposition, location and amount of asbestos or nondegradable material deposited in the area, and shall be provided to the board upon request.
b. Any nonproductive area of the landfill may be excluded from control, provided that the total of all excluded areas can be shown to contribute less than 1.0% of the total amount of NMOC emissions from the landfill. The amount, location, and age of the material shall be documented and provided to the board upon request. A separate NMOC emissions estimate shall be made for each section proposed for exclusion, and the sum of all such sections shall be compared to the NMOC emissions estimate for the entire landfill. Emissions from each section shall be computed using the following equation:
Qi = 2kL0Mi(e-kti)(CNMOC)(3.6 X 10-9)
where
Qi = NMOC emission rate from the ith section, megagrams per year
k = methane generation rate constant, year-1
L0 = methane generation potential, cubic meters per megagram solid waste
Mi = mass of the degradable solid waste in the ith section, megagrams
ti = age of the solid waste in the ith section, years
CNMOC = concentration of nonmethane organic compounds, parts per million by volume
3.6 X 10-9 = conversion factor
The values for k and CNMOC determined in field testing shall be used, if field testing has been performed in determining the NMOC emission rate or the radii of influence (this is distance from the well center to a point in the landfill where the pressure gradient applied by the blower or compressor approaches zero). If field testing has not been performed, the default values for k, L0 and CNMOC provided in 9VAC5-40-5860 B 1 or the alternative values from 9VAC5-40-5860 B 5 shall be used. The mass of nondegradable solid waste contained within the given section may be subtracted from the total mass of the section when estimating emissions provided the nature, location, age, and amount of the nondegradable material is documented as provided in subdivision A 3 a of this section.
B. Each owner seeking to comply with 9VAC5-40-5820 C 2 a (1) shall construct the gas collection devices using the following equipment or procedures:
1. The landfill gas extraction components shall be constructed of polyvinyl chloride (PVC), high density polyethylene (HDPE) pipe, fiberglass, stainless steel, or other nonporous, corrosion-resistant material of suitable dimensions to: convey projected amounts of gases; withstand installation, static, and settlement forces; and withstand planned overburden or traffic loads. The collection system shall extend as necessary to comply with emission and migration standards. Collection devices such as wells and horizontal collectors shall be perforated to allow gas entry without head loss sufficient to impair performance across the intended extent of control. Perforations shall be situated with regard to the need to prevent excessive air infiltration.
2. Vertical wells shall be placed so as not to endanger underlying liners and shall address the occurrence of water within the landfill. Holes and trenches constructed for piped wells and horizontal collectors shall be of sufficient cross section so as to allow for their proper construction and completion including, for example, centering of pipes and placement of gravel backfill. Collection devices shall be designed so as not to allow indirect short circuiting of air into the cover or refuse into the collection system or gas into the air. Any gravel used around pipe perforations should be of a dimension so as not to penetrate or block perforations.
3. Collection devices may be connected to the collection header pipes below or above the landfill surface. The connector assembly shall include a positive closing throttle valve, any necessary seals and couplings, access couplings and at least one sampling port. The collection devices shall be constructed of PVC, HDPE, fiberglass, stainless steel, or other nonporous material of suitable thickness.
C. Each owner seeking to comply with 9VAC5-40-5820 C 2 a (1) shall convey the landfill gas to a control system in compliance with 9VAC5-40-5820 C 2 c through the collection header pipe(s). The gas mover equipment shall be sized to handle the maximum gas generation flow rate expected over the intended use period of the gas moving equipment using the following procedures:
1. For existing collection systems, the flow data shall be used to project the maximum flow rate. If no flow data exists, the procedures in subdivision C 2 of this section shall be used.
2. For new collection systems, the maximum flow rate shall be in accordance with 9VAC5-40-5850 C 1.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 15, Issue 12, eff. April 1, 1999; amended, Virginia Register Volume 20, Issue 8, eff. January 29, 2004.
9VAC5-40-5830. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-5840. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-5850. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. Owners subject to 9VAC5-40-5820 shall comply with the provisions of Part III (9VAC20-81-100 et seq.) of 9VAC20 Chapter 81 (Solid Waste Management Regulations) pertaining to the control of landfill gases.
C. Except as provided in 9VAC5-40-5820 C 2 a (2), the specified methods in subdivisions C 1 through C 6 of this section shall be used to determine whether the gas collection system is in compliance with 9VAC5-40-5820 C 2 b.
1. For the purposes of calculating the maximum expected gas generation flow rate from the landfill to determine compliance with 9VAC5-40-5820 C 2 b (1) (a), one of the following equations shall be used. The k and L sub0 kinetic factors should be those published in the "Compilation of Air Pollutant Emission Factors (AP-42)" (see 9VAC5-20-21) or other site-specific values demonstrated to be appropriate and approved by the board. If k has been determined as specified in 9VAC5-40-5860 B 4, the value of k determined from the test shall be used. A value of no more than 15 years shall be used for the intended use period of the gas mover equipment. The active life of the landfill is the age of the landfill plus the estimated number of years until closure.
a. For sites with unknown year-to-year solid waste acceptance rate:
QM = 2L0R(e-kc - e-kt)
where
QM = maximum expected gas generation flow rate, cubic meters per year
L0 = methane generation potential, cubic meters per megagram solid waste
R = average annual acceptance rate, megagrams per year
k = methane generation rate constant, year-1
t = age of the landfill at equipment installation plus the time the owner or operator intends to use the gas mover equipment or active life of the landfill, whichever is less. If the equipment is installed after closure, t is the age of the landfill at installation, years
c = time since closure, years (for an active landfill c = 0 and e-kc = 1)
b. For sites with known year-to-year solid waste acceptance rate:
where
QM = maximum expected gas generation flow rate, cubic meters per year
k = methane generation rate constant, year-1
L0 = methane generation potential, cubic meters per megagram solid waste
Mi = mass of solid waste in the ith section, megagrams
ti = age of the ith section, years
c. If a collection and control system has been installed, actual flow data may be used to project the maximum expected gas generation flow rate instead of, or in conjunction with, the equations in subdivisions C 1 a and b of this section. If the landfill is still accepting waste, the actual measured flow data will not equal the maximum expected gas generation rate, so calculations using the equations in subdivisions C 1 a or b of this section or other methods acceptable to the board shall be used to predict the maximum expected gas generation rate over the intended period of use of the gas control system equipment.
2. For the purposes of determining sufficient density of gas collectors for compliance with 9VAC5-40-5820 C 2 b (1) (b), the owner shall design a system of vertical wells, horizontal collectors, or other collection devices, acceptable to the board, capable of controlling and extracting gas from all portions of the landfill sufficient to meet all operational and performance standards.
3. For the purpose of demonstrating whether the gas collection system flow rate is sufficient to determine compliance with 9VAC5-40-5820 C 2 b (1) (c), the owner shall measure gauge pressure in the gas collection header at each individual well, monthly. If a positive pressure exists, action shall be initiated to correct the exceedance within five calendar days, except for the three conditions allowed under 9VAC5-40-5822 A 2. If negative pressure cannot be achieved without excess air infiltration within 15 calendar days of the first measurement, the gas collection system shall be expanded to correct the exceedance within 120 days of the initial measurement of positive pressure. Any attempted corrective measure shall not cause exceedances of other operational or performance standards. An alternative timeline for correcting the exceedance may be submitted to the board for approval.
4. Owners are not required to expand the system as required in subdivision C 3 of this section during the first 180 days after gas collection system startup.
5. For the purpose of identifying whether excess air infiltration into the landfill is occurring, the owner shall monitor each well monthly for temperature and nitrogen or oxygen as provided in 9VAC5-40-5822 A 3. If a well exceeds one of these operating parameters, action shall be initiated to correct the exceedance within five calendar days. If correction of the exceedance cannot be achieved within 15 calendar days of the first measurement, the gas collection system shall be expanded to correct the exceedance within 120 days of the initial exceedance. Any attempted corrective measure shall not cause exceedances of other operational or performance standards. An alternative timeline for correcting the exceedance may be submitted to the board for approval.
6. An owner seeking to demonstrate compliance with 9VAC5-40-5820 C 2 b (1) (d) through the use of a collection system not conforming to the specifications provided in 9VAC5-40-5824 shall provide information acceptable to the board as specified in 9VAC5-40-5820 C 2 a (3) demonstrating that off-site migration is being controlled.
D. For purposes of compliance with 9VAC5-40-5822 A 1, each owner of a controlled landfill shall place each well or design component as specified in the approved design plan as provided in 9VAC5-40-5820 C 2 a. Each well shall be installed no later than 60 days after the date on which the initial solid waste has been in place for a period of:
1. Five years or more if active; or
2. Two years or more if closed or at final grade.
E. The following procedures shall be used for compliance with the surface methane operational standard as provided in 9VAC5-40-5822 A 4.
1. After installation of the collection system, the owner shall monitor surface concentrations of methane along the entire perimeter of the collection area and along a pattern that traverses the landfill at 30-meter intervals (or a site-specific established spacing) for each collection area on a quarterly basis using an organic vapor analyzer, flame ionization detector, or other portable monitor meeting the specifications provided in subsection F of this section.
2. The background concentration shall be determined by moving the probe inlet upwind and downwind outside the boundary of the landfill at a distance of at least 30 meters from the perimeter wells.
3. Surface emission monitoring shall be performed in accordance with § 4.3.1 of Reference Method 21 of Appendix A of 40 CFR Part 60, except that the probe inlet shall be placed within 5 to 10 centimeters of the ground. Monitoring shall be performed during typical meteorological conditions.
4. Any reading of 500 parts per million or more above background at any location shall be recorded as a monitored exceedance and the actions specified in subdivisions E 4 a through e of this section shall be taken. As long as the specified actions are taken, the exceedance is not a violation of the operational requirements of 9VAC5-40-5822 A 4.
a. The location of each monitored exceedance shall be marked and the location recorded.
b. Cover maintenance or adjustments to the vacuum of the adjacent wells to increase the gas collection in the vicinity of each exceedance shall be made and the location shall be remonitored within 10 calendar days of detecting the exceedance.
c. If the remonitoring of the location shows a second exceedance, additional corrective action shall be taken and the location shall be monitored again within 10 days of the second exceedance. If the remonitoring shows a third exceedance for the same location, the action specified in subdivision E 4 e of this section shall be taken, and no further monitoring of that location is required until the action specified in subdivision E 4 e of this section has been taken.
d. Any location that initially showed an exceedance but has a methane concentration less than 500 parts per million methane above background at the 10-day remonitoring specified in subdivision E 4 b or c of this section shall be remonitored one month from the initial exceedance. If the one-month remonitoring shows a concentration less than 500 parts per million above background, no further monitoring of that location is required until the next quarterly monitoring period. If the 1-month remonitoring shows an exceedance, the actions specified in subdivision E 4 c or e of this section shall be taken.
e. For any location where monitored methane concentration equals or exceeds 500 parts per million above background three times within a quarterly period, a new well or other collection device shall be installed within 120 calendar days of the initial exceedance. An alternative remedy to the exceedance, such as upgrading the blower, header pipes or control device, and a corresponding timeline for installation may be submitted to the board for approval.
5. The owner shall implement a program to monitor for cover integrity and implement cover repairs as necessary on a monthly basis.
F. Each owner seeking to comply with the provisions in subsection E of this section shall comply with the following instrumentation specifications and procedures for surface emission monitoring devices:
1. The portable analyzer shall meet the instrument specifications provided in § 3 of Reference Method 21 of Appendix A of 40 CFR Part 60, except that "methane" shall replace all references to VOC.
2. The calibration gas shall be methane, diluted to a nominal concentration of 500 parts per million in air.
3. To meet the performance evaluation requirements in § 3.1.3 of Reference Method 21 of Appendix A of 40 CFR Part 60, the instrument evaluation procedures of § 4.4 of Reference Method 21 of Appendix A of 40 CFR Part 60 shall be used.
4. The calibration procedures provided in § 4.2 of Reference Method 21 of Appendix A of 40 CFR Part 60 shall be followed immediately before commencing a surface monitoring survey.
G. The provisions of this article apply at all times, except during periods of startup, shutdown, or malfunction, provided that the duration of startup, shutdown, or malfunction shall not exceed five days for collection systems and shall not exceed one hour for treatment or control devices. This subsection shall not apply to the emission standards set forth in 9VAC5-40-5830 and 9VAC5-40-5840.
H. With regard to startup, shutdown, and malfunction, the provisions of 9VAC5-40-5850 A and 9VAC5-40-5910 shall apply to the emission standards set forth in 9VAC5-40-5830 and 9VAC5-40-5840.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999; Volume 20, Issue 8, eff. January 29, 2004; Volume 27, Issue 23, eff. August 17, 2011.
9VAC5-40-5855. Compliance schedule.
A. Except as provided for under subsection B of this section, the owner of a municipal solid waste landfill subject to this article located outside the Northern Virginia Volatile Organic Compound Emissions Control Area and with a design capacity greater than or equal to 2.5 million megagrams and 2.5 million cubic meters shall plan, award contracts, and install emission collection and control equipment capable of meeting the standards established under 9VAC5-40-5820 within specific periods after the date the initial NMOC emission rate report under 9VAC5-40-5880 D 1 a shows NMOC emissions equal or exceed 50 megagrams per year, as follows:
1. The collection and control design plan shall be submitted to the board within 12 months.
2. Construction contracts shall be awarded within 18 months.
3. Construction shall be initiated within 20 months.
4. Construction shall be completed within 28 months.
5. Final compliance shall be achieved within 30 months after the date the initial annual emission rate report shows NMOC emissions greater than or equal to 50 megagrams per year.
B. For each MSW landfill located outside of the Northern Virginia Volatile Organic Compound Emissions Control Area with a design capacity of 2.5 million megagrams and 2.5 million cubic meters and with an NMOC rate less than 50 megagrams per year on April 1, 1999, installation of collection and control systems capable of meeting the standards established under 9VAC5-40-5820 shall be accomplished within 30 months of the date when the condition in 9VAC5-40-5820 C is met (i.e., the date of the first annual NMOC emission rate which equals or exceeds 50 megagrams per year), as follows:
1. The collection and control design plan shall be submitted to the board within 12 months.
2. Construction contracts shall be awarded within 18 months.
3. Construction shall be initiated within 20 months.
4. Construction shall be completed within 28 months.
5. Final compliance shall be achieved within 30 months after the date the initial annual emission rate report shows NMOC emissions greater than or equal to 50 megagrams per year.
C. Except as provided for under subsection D of this section, the owner of a municipal solid waste landfill subject to this article in the Northern Virginia Volatile Organic Compound Emissions Control Area, with a design capacity greater than or equal to 1.0 million megagrams and 1.0 million cubic meters shall plan, award contracts, and install emission collection and control equipment capable of meeting the standards established under 9VAC5-40-5820 by December 30, 1999, provided the initial NMOC emission rate report shows NMOC emissions equal or exceed 23 megagrams per year.
D. For each MSW landfill in the Northern Virginia Volatile Organic Compound Emissions Control Area, with a design capacity greater than or equal to 1.0 million megagrams and 1.0 million cubic meters and with an NMOC rate less than 23 megagrams per year on April 1, 1999, installation of collection and control systems capable of meeting the standards established under 9VAC5-40-5820 shall be accomplished within 30 months of the date when the condition in 9VAC5-40-5820 C is met (i.e., the date of the first annual NMOC emission rate which equals or exceeds 23 megagrams per year), as follows:
1. The collection and control design plan shall be submitted to the board within 12 months.
2. Construction contracts shall be awarded within 18 months.
3. Construction shall be initiated within 20 months.
4. Construction shall be completed within 28 months.
5. Final compliance shall be achieved within 30 months after the date the initial annual emission rate report shows NMOC emissions greater than or equal to 23 megagrams per year.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 15, Issue 12, eff. April 1, 1999; amended, Virginia Register Volume 20, Issue 8, eff. January 29, 2004.
9VAC5-40-5860. Test methods and procedures.
A. The provisions of 9VAC5-40-30 (Emission testing) or 40 CFR 60.8, whichever is more restrictive, apply.
B. 1. The owner shall calculate the NMOC emission rate using either the equation provided in subdivision B 1 a of this section or the equation provided in subdivision B 1 b of this section. Both equations may be used if the actual year-to-year solid waste acceptance rate is known, as specified in subdivision B 1 a of this section, for part of the life of the landfill and the actual year-to-year solid waste acceptance rate is unknown, as specified in subdivision B 1 b of this section, for part of the life of the landfill. The values to be used in both equations are 0.05 per year for k, 170 cubic meters per megagram for L0, and 4,000 parts per million by volume as hexane for the CNMOC. For landfills located in geographical areas with a 30-year average annual precipitation of less than 25 inches, as measured at the nearest representative official meteorological site, the k value to be used is 0.02 per year.
a. The following equation shall be used if the actual year-to-year solid waste acceptance rate is known.
MNMOC = 2kL0Mi (e-kti) (CNMOC) (3.6 X 10-9)
where
MNMOC = Total NMOC emission rate from the landfill, megagrams per year
k = methane generation rate constant, year-1
L0 = methane generation potential, cubic meters per megagram solid waste
Mi = mass of solid waste in the ith section, megagrams
ti = age of the ith section, years
CNMOC = concentration of NMOC, parts per million by volume as hexane
3.6 X 10-9 = conversion factor
The mass of nondegradable solid waste may be subtracted from the total mass of solid waste in a particular section of the landfill when calculating the value for Mi if documentation of the nature and amounts of such wastes is obtained.
b. The following equation shall be used if the actual year-to-year solid waste acceptance rate is unknown.
MNMOC = 2L0 R(e-kc -e-kt)(CNMOC)(3.6 X 10-9)
where
MNMOC = mass emission rate of NMOC, megagrams per year
L0 = methane generation potential, cubic meters per megagram solid waste
R = average annual acceptance rate, megagrams per year
k = methane generation rate constant, year-1
t = age of landfill, years
CNMOC = concentration of NMOC, parts per million by volume as hexane
c = time since closure, years. For active landfill c = 0 and e-kc = 1
3.6 X 10-9 = conversion factor
The mass of nondegradable solid waste may be subtracted from the total mass of solid waste in a particular section of the landfill when calculating the value of R if documentation of the nature and amounts of such waste is maintained.
2. Tier 1. The owner shall compare the calculated NMOC mass emission rate to the following emission rate applicability criteria: (i) in the Northern Virginia Volatile Organic Compound Emissions Control Area, 23 megagrams per year or (ii) in the remaining areas of the Commonwealth, 50 megagrams per year.
a. If the NMOC emission rate calculated in subdivision B 1 of this section is (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, then the owner shall submit an emission rate report as provided in 9VAC5-40-5880 D 1, and shall recalculate the NMOC mass emission rate annually as required under 9VAC5-40-5820 C 1.
b. If the calculated NMOC emission rate is greater than or equal to (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, then the owner shall either comply with 9VAC5-40-5820 C 2, or determine a site-specific NMOC concentration and recalculate the NMOC emission rate using the procedures provided in subdivision B 3 of this section.
3. Tier 2. The owner shall determine the NMOC concentration using the following sampling procedure. The owner shall install at least two sample probes per hectare of landfill surface that has retained waste for at least two years. If the landfill is larger than 25 hectares in area, only 50 samples are required. The sample probes should be located to avoid known areas of nondegradable solid waste. The owner shall collect and analyze one sample of landfill gas from each probe to determine the NMOC concentration using Reference Method 25C of Appendix A of 40 CFR Part 60 or Reference Method 18 of Appendix A of 40 CFR Part 60. If using Reference Method 18 of Appendix A of 40 CFR Part 60, the minimum list of compounds to be tested shall be those published in the "Compilation of Air Pollutant Emission Factors (AP-42)" (see 9VAC5-20-21). If composite sampling is used, equal volumes shall be taken from each sample probe. If more than the required number of samples are taken, all samples shall be used in the analysis. The owner shall divide the NMOC concentration from Reference Method 25C of Appendix A of 40 CFR Part 60 by six to convert from CNMOC as carbon to CNMOC as hexane.
a. The owner shall recalculate the NMOC mass emission rate using the equations provided in subdivision B 1 a or B 1 b of this section and using the average NMOC concentration from the collected samples instead of the default value in the equation provided in subdivision B 1 of this section.
b. If the resulting mass emission rate calculated using the site-specific NMOC concentration is greater than or equal to (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, then the owner shall either comply with 9VAC5-40-5820 C 2, or determine the site-specific methane generation rate constant and recalculate the NMOC emission rate using the site-specific methane generation rate using the procedure specified in subdivision B 4 of this section.
c. If the resulting NMOC mass emission rate is less than (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, the owner shall submit a periodic estimate of the emission rate report as provided in 9VAC5-40-5880 D 1 and retest the site-specific NMOC concentration every five years using the methods specified in this section.
4. Tier 3. The site-specific methane generation rate constant shall be determined using the procedures provided in Reference Method 2E of Appendix A of 40 CFR Part 60. The owner shall estimate the NMOC mass emission rate using equations in subdivision B 1 a or B 1 b of this section and using a site-specific methane generation rate constant k, and the site-specific NMOC concentration as determined in subdivision B 3 of this section instead of the default values provided in subdivision B 1 of this section. The owner shall compare the resulting NMOC mass emission rate to the following emission rate applicability criteria: (i) in the Northern Virginia Volatile Organic Compound Emissions Control Area, 23 megagrams per year or (ii) in the remaining areas of the Commonwealth, 50 megagrams per year.
a. If the NMOC mass emission rate as calculated using the site-specific methane generation rate and concentration of NMOC is greater than or equal to (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, the owner shall comply with 9VAC5-40-5820 C 2.
b. If the NMOC mass emission rate is less than (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, then the owner shall submit a periodic emission rate report as provided in 9VAC5-40-5880 D 1 and shall recalculate the NMOC mass emission rate annually, as provided in 9VAC5-40-5880 D 1 using the equations in subdivision B 1 of this section and using the site-specific methane generation rate constant and NMOC concentration obtained in subdivision B 3 of this section. The calculation of the methane generation rate constant is performed only once, and the value obtained from this test shall be used in all subsequent annual NMOC emission rate calculations.
5. The owner may use other methods to determine the NMOC concentration or a site-specific k as an alternative method required in subdivisions B 3 and B 4 of this section if the method has been approved by the board.
C. After the installation of a collection and control system in compliance with 9VAC5-40-5850, the owner shall calculate the NMOC emission rate for purposes of determining when the system can be removed as provided in 9VAC5-40-5820 C 2 e, using the following equation:
MNMOC = 1.89 X 10-3 QLFG CNMOC
where
MNMOC = mass emission rate of NMOC, megagrams per year
QLFG = flow rate of landfill gas, cubic meters per minute
CNMOC = NMOC concentration, parts per million by volume as hexane
1. The flow rate of landfill gas, QLFG, shall be determined by measuring the total landfill gas flow rate at the common header pipe that leads to the control device using a gas flow measuring device calibrated according to the provisions of § 4 of Reference Method 2E of Appendix A of 40 CFR Part 60.
2. The average NMOC concentration, CNMOC, shall be determined by collecting and analyzing landfill gas sampled from the common header pipe before the gas moving or condensate removal equipment using the procedures in Reference Method 25C or Reference Method 18 of Appendix A of 40 CFR Part 60. If using Reference Method 18 of Appendix A of 40 CFR Part 60, the minimum list of compounds to be tested shall be those published in the "Compilation of Air Pollutant Emission Factors (AP-42)" (see 9VAC5-20-21). The sample location on the common header pipe shall be before any condensate removal or other gas refining units. The owner shall divide the NMOC concentration from Reference Method 25C of Appendix A of 40 CFR Part 60 by six to convert from CNMOC as carbon to CNMOC as hexane.
3. The owner may use an alternative method to determine landfill gas flow rate and NMOC concentration if the method has been approved by the board.
D. When calculating emissions for prevention of significant deterioration purposes, the owner of each MSW landfill subject to the provisions of this article shall estimate the NMOC emission rate for comparison to the prevention of significant deterioration major source and significance levels in Article 8 (9VAC5-80-1700 et seq.) of Part II of 9VAC5 Chapter 80 using the "Compilation of Air Pollutant Emission Factors (AP-42)" (see 9VAC5-20-21) or other measurement procedures acceptable to the board. If a collection system, which complies with the provisions in 9VAC5-40-5820 C 2 is already installed, the owner shall estimate the NMOC emission rate using the procedures provided in subsection C of this section.
E. For the compliance test required in 9VAC5-40-5820 C 2 c (2), Reference Method 25 or Reference Method 18 of Appendix A of 40 CFR Part 60 shall be used to determine compliance with 98 weight-percent efficiency or the 20 ppmv outlet concentration level, unless an alternative method to demonstrate compliance has been approved by the board as provided by 9VAC5-40-5820 C 2 a (2). If using Reference Method 18 of Appendix A of 40 CFR Part 60, the minimum list of compounds to be tested shall be those published in the "Compilation of Air Pollutant Emission Factors (AP-42)" (see 9VAC5-20-21). The following equation shall be used to calculate efficiency:
Control Efficiency = (NMOCin - NMOCout)/(NMOCin)
where
NMOCin = mass of NMOC entering control device
NMOCout = mass of NMOC exiting control device
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999; Volume 20, Issue 8, eff. January 29, 2004.
9VAC5-40-5870. Monitoring.
A. The provisions of 9VAC5-40-40 (Monitoring) apply.
B. Except as provided in 9VAC5-40-5820 C 2 a (2), the provisions of subsections C through H of this section apply.
C. Each owner seeking to comply with 9VAC5-40-5820 C 2 b (1) for an active gas collection system shall install a sampling port and a thermometer, other temperature measuring device, or an access port for temperature measurements at each wellhead and:
1. Measure the gauge pressure in the gas collection header on a monthly basis as provided in 9VAC5-40-5850 C 3; and
2. Monitor nitrogen or oxygen concentration in the landfill gas on a monthly basis as provided in 9VAC5-40-5850 C 5; and
3. Monitor temperature of the landfill gas on a monthly basis as provided in 9VAC5-40-5850 C 5.
D. Each owner seeking to comply with 9VAC5-40-5820 C 2 c using an enclosed combustor shall calibrate, maintain, and operate according to the manufacturer's specifications, the following equipment.
1. A temperature monitoring device equipped with a continuous recorder and having a minimum accuracy of ± 1.0 percent of the temperature being measured expressed in degrees Celsius or ± 0.5 degrees Celsius, whichever is greater. A temperature monitoring device is not required for boilers or process heaters with design heat input capacity equal to or greater than 44 megawatts.
2. A device that records flow to or bypass of the control device. The owner shall either:
a. Install, calibrate, and maintain a gas flow rate measuring device that shall record the flow to the control device at least every 15 minutes; or
b. Secure the bypass line valve in the closed position with a car-seal or a lock-and-key type configuration. A visual inspection of the seal or closure mechanism shall be performed at least once every month to ensure that the valve is maintained in the closed position and that the gas flow is not diverted through the bypass line.
E. Each owner seeking to comply with 9VAC5-40-5820 C 2 c using an open flare shall install, calibrate, maintain, and operate according to the manufacturer's specifications the following equipment:
1. A heat sensing device, such as an ultraviolet beam sensor or thermocouple, at the pilot light or the flame itself to indicate the continuous presence of a flame.
2. A device that records flow to or bypass of the flare. The owner shall either:
a. Install, calibrate, and maintain a gas flow rate measuring device that shall record the flow to the control device at least every 15 minutes; or
b. Secure the bypass line valve in the closed position with a car-seal or a lock-and-key type configuration. A visual inspection of the seal or closure mechanism shall be performed at least once every month to ensure that the valve is maintained in the closed position and that the gas flow is not diverted through the bypass line.
F. Each owner seeking to demonstrate compliance with 9VAC5-40-5820 C 2 c using a device other than an open flare or an enclosed combustor shall provide information acceptable to the board as provided in 9VAC5-40-5820 C 2 a (2) describing the operation of the control device, the operating parameters that would indicate proper performance, and appropriate monitoring procedures. The board will review the information and either approve it, or request that additional information be submitted. The board may specify additional appropriate monitoring procedures.
G. Each owner seeking to install a collection system that does not meet the specifications in 9VAC5-40-5824 or seeking to monitor alternative parameters to those required by 9VAC5-40-5822, 9VAC5-40-5850, 9VAC5-40-5860, and 9VAC5-40-5870 shall provide information acceptable to the board as provided in 9VAC5-40-5820 C 2 a (2) and (3) describing the design and operation of the collection system, the operating parameters that would indicate proper performance, and appropriate monitoring procedures. The board may specify additional appropriate monitoring procedures.
H. Each owner seeking to demonstrate compliance with 9VAC5-40-5850 E, shall monitor surface concentrations of methane according to the instrument specifications and procedures provided in 9VAC5-40-5850 F. Any closed landfill that has no monitored exceedances of the operational standard in three consecutive quarterly monitoring periods may skip to annual monitoring. Any methane reading of 500 parts per million or more above background detected during the annual monitoring returns the frequency for that landfill to quarterly monitoring.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999; Volume 20, Issue 8, eff. January 29, 2004.
9VAC5-40-5880. Reporting.
A. The provisions of 9VAC5-40-5840 (Notification, records and reporting) apply.
B. Except as provided in 9VAC5-40-5820 C 2 a (2), the provisions of subsections C through I of this section apply.
C. Each owner subject to the requirements of this article shall submit an initial design capacity report to the board.
1. The initial design capacity report shall be submitted no later than June 30, 1999.
2. The initial design capacity report shall contain the following information:
a. A map or plot of the landfill, providing the size and location of the landfill, and identifying all areas where solid waste may be landfilled according to the permit issued by the department under Part V (9VAC20-81-400 et seq.) of 9VAC20 Chapter 81 (Solid Waste Management Regulations);
b. The maximum design capacity of the landfill. Where the maximum design capacity is specified in a permit issued by the department under Part V (9VAC20-81-400 et seq.) of 9VAC20 Chapter 81 (Solid Waste Management Regulations), a copy of the permit specifying the maximum design capacity may be submitted as part of the report. If the maximum design capacity of the landfill is not specified in the permit, the maximum design capacity shall be calculated using good engineering practices acceptable to the board. The calculations shall be provided, along with the relevant parameters as part of the report. The board may request other reasonable information as may be necessary to verify the maximum design capacity of the landfill.
3. An amended design capacity report shall be submitted to the board providing notification of an increase in the design capacity of the landfill within 90 days of an increase in the maximum design capacity of the landfill to or above (i) 1.0 million megagrams and 1.0 million cubic meters in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 2.5 million megagrams and 2.5 million cubic meters in the remaining areas of the Commonwealth. This increase in design capacity may result from an increase in the permitted volume of the landfill or an increase in the density as documented in the annual recalculation required in 9VAC5-40-5890 H.
D. Each owner subject to the requirements of this article shall submit an NMOC emission rate report to the board initially and annually thereafter, except as provided for in subdivisions D 1 b or D 3 of this section. The board may request such additional information as may be necessary to verify the reported NMOC emission rate.
1. The NMOC emission rate report shall contain an annual or five-year estimate of the NMOC emission rate calculated using the formula and procedures provided in 9VAC5-40-5860 B or C, as applicable.
a. The initial NMOC emission rate report shall be submitted by June 30, 1999, and may be combined with the initial design capacity report required in subsection C of this section. Subsequent NMOC emission rate reports shall be submitted annually thereafter, except as provided for in subdivisions D 1 b and D 3 of this section.
b. If the estimated NMOC emission rate as reported in the annual report to the board is less than (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth in each of the next five consecutive years, the owner may elect to submit an estimate of the NMOC emission rate for the next five-year period in lieu of the annual report. This estimate shall include the current amount of solid waste-in-place and the estimated waste acceptance rate for each year of the five years for which an NMOC emission rate is estimated. All data and calculations upon which this estimate is based shall be provided to the board. This estimate shall be revised at least once every five years. If the actual waste acceptance rate exceeds the estimated waste acceptance rate in any year reported in the five-year estimate, a revised five-year estimate shall be submitted to the board. The revised estimate shall cover the five-year period beginning with the year in which the actual waste acceptance rate exceeded the estimated waste acceptance rate.
2. The NMOC emission rate report shall include all the data, calculations, sample reports and measurements used to estimate the annual or five-year emissions.
3. Each owner subject to the requirements of this article is exempted from the requirements of subdivisions D 1 and 2 of this section, after the installation of a collection and control system in compliance with 9VAC5-40-5820 C 2, during such time as the collection and control system is in operation and in compliance with 9VAC5-40-5822 and 9VAC5-40-5850.
E. Each owner subject to the provisions of 9VAC5-40-5820 C 2 a shall submit a collection and control system design plan to the board within one year of the first report, required under subdivision D of this section, in which the emission rate is greater than or equal to (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, except as follows:
1. If the owner elects to recalculate the NMOC emission rate after Tier 2 NMOC sampling and analysis as provided in 9VAC5-40-5860 B 3 and the resulting rate is less than (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, annual periodic reporting shall be resumed, using the Tier 2 determined site-specific NMOC concentration, until the calculated emission rate is greater than or equal to (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, or the landfill is closed. The revised NMOC emission rate report, with the recalculated emission rate based on NMOC sampling and analysis, shall be submitted within 180 days of the first calculated exceedance of the emission rate applicability criteria.
2. If the owner elects to recalculate the NMOC emission rate after determining a site-specific methane generation rate constant (k), as provided in Tier 3 in 9VAC5-40-5860 B 4, and the resulting NMOC emission rate is less than (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth, annual periodic reporting shall be resumed. The resulting site-specific methane generation rate constant (k) shall be used in the emission rate calculation until such time as the emissions rate calculation results in an exceedance. The revised NMOC emission rate report based on the provisions of 9VAC5-40-5860 B 4 and the resulting site-specific methane generation rate constant (k) shall be submitted to the board within one year of the first calculated emission rate exceeding (i) 23 megagrams per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams per year in the remaining areas of the Commonwealth.
F. Each owner of a controlled landfill shall submit a closure report to the board within 30 days of waste acceptance cessation. The board may request additional information as may be necessary to verify that permanent closure has taken place in accordance with the requirements of 9VAC20-81-160. If a closure report has been submitted to the board, no additional wastes may be placed into the landfill without obtaining a permit issued by the department under Part V (9VAC20-81-400 et seq.) of 9VAC20 Chapter 81 (Solid Waste Management Regulations).
G. Each owner of a controlled landfill shall submit an equipment removal report to the board 30 days prior to removal or cessation of operation of the control equipment.
1. The equipment removal report shall contain all of the following items:
a. A copy of the closure report submitted in accordance with subsection F of this section;
b. A copy of the initial compliance test report demonstrating that the 15-year minimum control period has expired; and
c. Dated copies of three successive NMOC emission rate reports demonstrating that the landfill is no longer producing (i) 23 megagrams or greater of NMOC per year in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 50 megagrams or greater of NMOC per year in the remaining areas of the Commonwealth.
2. The board may request such additional information as may be necessary to verify that all of the conditions for removal in 9VAC5-40-5820 C 2 e have been met.
H. Each owner of a landfill seeking to comply with 9VAC5-40-5820 C 2 using an active collection system designed in accordance with 9VAC5-40-5820 C 2 b shall submit to the board annual reports of the recorded information in subdivisions H 1 through H 6 of this section. The initial annual report shall be submitted within 180 days of installation and startup of the collection and control system, and shall include the initial compliance test report. For enclosed combustion devices and flares, reportable exceedances are defined under 9VAC5-40-5890 E.
1. Value and length of time for exceedance of applicable parameters monitored under 9VAC5-40-5870 C, D, E, and F.
2. Description and duration of all periods when the gas stream is diverted from the control device through a bypass line or the indication of bypass flow as specified under 9VAC5-40-5870.
3. Description and duration of all periods when the control device was not operating for a period exceeding one hour and length of time the control device was not operating.
4. All periods when the collection system was not operating in excess of five days.
5. The location of each exceedance of the 500 parts per million methane concentration as provided in 9VAC5-40-5822 A 4 and the concentration recorded at each location for which an exceedance was recorded in the previous month.
6. The date of installation and the location of each well or collection system expansion added pursuant to subdivisions C 3, D, and E 4 of 9VAC5-40-5850.
I. Each owner seeking to comply with 9VAC5-40-5820 C 2 a shall include the following information with the initial compliance test report:
1. A diagram of the collection system showing collection system positioning including all wells, horizontal collectors, surface collectors, or other gas extraction devices, including the locations of any areas excluded from collection and the proposed sites for the future collection system expansion;
2. The data upon which the sufficient density of wells, horizontal collectors, surface collectors, or other gas extraction devices and the gas mover equipment sizing are based;
3. The documentation of the presence of asbestos or nondegradable material for each area from which collection wells have been excluded based on the presence of asbestos or nondegradable material;
4. The sum of the gas generation flow rates for all areas from which collection wells have been excluded based on nonproductivity and the calculations of gas generation flow rate for each excluded area; and
5. The provisions for increasing gas mover equipment capacity with increased gas generation flow rate, if the present gas mover equipment is inadequate to move the maximum flow rate expected over the life of the landfill; and
6. The provisions for the control of off-site migration.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999; Volume 20, Issue 8, eff. January 29, 2004; Volume 27, Issue 23, eff. August 17, 2011.
9VAC5-40-5890. Recordkeeping.
A. The provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
B. Except as provided in 9VAC5-40-5820 C 2 a (2), the provisions of subsections C through G of this section apply.
C. Each owner of an MSW landfill subject to the provisions of 9VAC5-40-5820 C shall keep for at least five years up-to-date, readily accessible, on-site records of the design capacity report which triggered 9VAC5-40-5820 C, the current amount of solid waste in-place, and the year-by-year waste acceptance rate. Off-site records may be maintained if they are retrievable within four hours. Either paper copy or electronic formats are acceptable.
D. Each owner of a controlled landfill shall keep up-to-date, readily accessible records for the life of the control equipment of the data listed in subdivisions D 1 through D 4 of this section as measured during the initial compliance test or compliance determination. Records of subsequent tests or monitoring shall be maintained for a minimum of five years. Records of the control device vendor specifications shall be maintained until removal.
1. Where an owner subject to the provisions of this article seeks to demonstrate compliance with 9VAC5-40-5820 C 2 b:
a. The maximum expected gas generation flow rate as calculated in 9VAC5-40-5850 C 1. The owner may use an alternative method to determine the maximum gas generation flow rate, if the method has been approved by the board.
b. The density of wells, horizontal collectors, surface collectors, or other gas extraction devices determined using the procedures specified in 9VAC5-40-5824 A 1.
2. Where an owner subject to the provisions of this article seeks to demonstrate compliance with 9VAC5-40-5820 C 2 c through use of an enclosed combustion device other than a boiler or process heater with a design heat input capacity equal to or greater than 44 megawatts:
a. The average combustion temperature measured at least every 15 minutes and averaged over the same time period of the compliance test.
b. The percent reduction of NMOC determined as specified in 9VAC5-40-5820 C 2 c (2) achieved by the control device.
3. Where an owner subject to the provisions of this article seeks to demonstrate compliance with 9VAC5-40-5820 C 2 c (2) (a) through use of a boiler or process heater of any size: a description of the location at which the collected gas vent stream is introduced into the boiler or process heater over the same time period of the compliance testing.
4. Where an owner subject to the provisions of this article seeks to demonstrate compliance with 9VAC5-40-5820 C 2 c (1) through use of an open flare, the flare type (i.e., steam-assisted, air-assisted, or nonassisted), all visible emission readings, heat content determination, flow rate or bypass flow rate measurements, and exit velocity determinations made during the compliance test as specified in 40 CFR 60.18; continuous records of the flare pilot flame or flare flame monitoring and records of all periods of operations during which the pilot flame of the flare flame is absent.
E. Each owner of a controlled landfill subject to the provisions of this article shall keep for five years up-to-date, readily accessible continuous records of the equipment operating parameters specified to be monitored in 9VAC5-40-5870 as well as up-to-date, readily accessible records for periods of operation during which the parameter boundaries established during the most recent compliance test are exceeded.
1. The following constitute exceedances that shall be recorded and reported under 9VAC5-40-5880 H:
a. For enclosed combustors except for boilers and process heaters with design heat input capacity of 44 megawatts (150 million British thermal units per hour) or greater, all three-hour periods of operation during which the average combustion temperature was more than 28 degrees Celsius below the average combustion temperature during the most recent compliance test at which compliance with 9VAC5-40-5820 C 2 c was determined.
b. For boilers or process heaters, whenever there is a change in the location at which the vent stream is introduced into the flame zone as required under subdivision D 3 of this section.
2. Each owner subject to the provisions of this article shall keep up-to-date, readily accessible continuous records of the indication of flow to the control device or the indication of bypass flow or records of monthly inspections of car-seals or lock-and-key configurations used to seal bypass lines, specified under 9VAC5-40-5870.
3. Each owner subject to the provisions of this article who uses a boiler or process heater with a design heat input capacity of 44 megawatts or greater to comply with 9VAC5-40-5820 C 2 c shall keep an up-to-date, readily accessible record of all periods of operation of the boiler or process heater. (Examples of such records could include records of steam use, fuel use, or monitoring data collected pursuant to other state or federal regulatory requirements.)
4. Each owner seeking to comply with the provisions of this article by use of an open flare shall keep up-to-date, readily accessible continuous records of the flame or flare pilot flame monitoring specified under 9VAC5-40-5870 E, and up-to-date, readily accessible records of all periods of operation in which the flame or flare pilot flame is absent.
F. Each owner subject to the provisions of this article shall keep for the life of the collection system an up-to-date, readily accessible plot map showing each existing and planned collector in the system and providing a unique identification location label for each collector.
1. Each owner subject to the provisions of this article shall keep up-to-date, readily accessible records of the installation date and location of all newly installed collectors as specified under 9VAC5-40-5850 D.
2. Each owner subject to the provisions of this article shall keep readily accessible documentation of the nature, date of deposition, amount, and location of asbestos-containing or nondegradable waste excluded from collection as provided in 9VAC5-40-5824 A 3 a as well as any nonproductive areas excluded from collection as provided in 9VAC5-40-5824 A 3 b.
G. Each owner subject to the provisions of this article shall keep for at least five years up-to-date, readily accessible records of all collection and control system exceedances of the operational standards in 9VAC5-40-5822, the reading in the subsequent month whether or not the second reading is an exceedance, and the location of each exceedance.
H. Landfill owners who convert design capacity from volume to mass or from mass to volume to demonstrate that the landfill design capacity is less than (i) 1.0 million megagrams or 1.0 million cubic meters in the Northern Virginia Volatile Organic Compound Emissions Control Area or (ii) 2.5 million megagrams or 2.5 million cubic meters in the remaining areas of the Commonwealth, as provided in the definition of "design capacity," shall keep readily accessible, on-site records of the annual recalculation of site-specific density, design capacity, and the supporting documentation. Off-site records may be obtained if they are retrievable within four hours. Either paper copy or electronic formats are acceptable.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999; Volume 20, Issue 8, eff. January 29, 2004.
9VAC5-40-5900. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-5910. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply except that the provisions of 9VAC5-20-180 E, F, and G shall apply only to the emission standards set forth in 9VAC5-40-5830 and 9VAC5-40-5840.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996; amended, Virginia Register Volume 20, Issue 8, eff. January 29, 2004.
9VAC5-40-5920. Permits.
A. A permit may be required prior to beginning any of the activities specified below if the provisions of 9VAC5 Chapter 50 (9VAC5-50) and 9VAC5 Chapter 60 (9VAC5-60) apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
6. Operation of a facility.
B. MSW landfills required to install a collection and control system according to the provisions of 9VAC5-40-5820 shall apply for a permit amendment in accordance with Part V (9VAC20-81-400 et seq.) of 9VAC20 Chapter 81 (Solid Waste Management Regulations).
C. Physical or operational changes made to an MSW landfill solely to comply with this article are not considered construction, reconstruction, or modification for the purposes of 40 CFR 60 Subpart WWW.
D. The owner of an MSW landfill subject to this article with a design capacity greater than or equal to 2.5 million megagrams and 2.5 million cubic meters is subject to Article 1 (9VAC5-80-50 et seq.) of Part II of 9VAC5 Chapter 80. When a landfill is closed, and either never needed control or meets the conditions for control system removal specified in 9VAC5-40-5820 C 2 e, an operating permit under Article 1 (9VAC5-80-50 et seq.) of Part II of 9VAC5 Chapter 80 is no longer required.
E. A landfill with a design capacity less than 2.5 million megagrams or 2.5 million cubic meters does not require an operating permit under Article 1 (9VAC5-80-50 et seq.) of Part II of 9VAC5 Chapter 80.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996; amended, Virginia Register Volume 15, Issue 12, eff. April 1, 1999; Volume 20, Issue 8, eff. January 29, 2004; Volume 27, Issue 23, eff. August 17, 2011.
Article 43.1
Emission Standards for Municipal Solid Waste Landfills for Which Construction, Reconstruction, or Modification Was Commenced on or Before July 17, 2014 (Rule 4-43.1)
9VAC5-40-5925. Applicability and designation of affected facility.
Article 43.1
Emission Standards for Municipal Solid Waste Landfills for which Construction, Reconstruction, or Modification was Commenced on or before July 17, 2014 (Rule 4-43.1)
A. The affected facility to which the provisions of this article apply is each existing municipal solid waste (MSW) landfill for which construction, reconstruction, or modification was commenced on or before July 17, 2014, and as further defined in Subpart Cf (40 CFR 60.30f et seq.) of 40 CFR Part 60.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
C. The owner of an MSW landfill shall obtain a federal operating permit as required by 40 CFR 60.31f(c). When an MSW landfill is closed, the owner is no longer subject to the requirement to maintain a federal operating permit if the conditions of 40 CFR 60.31f(d) are met.
D. For each MSW landfill in the closed landfill subcategory, the reporting provisions of 9VAC5-40-5975 may be met as provided in 40 CFR 60.31f(e).
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 33, Issue 10, eff. February 22, 2017.
9VAC5-40-5930. Definitions.
A. For the purpose of applying this article in the context of the Regulations for the Control and Abatement of Air Pollution and related uses, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined herein shall have the meanings given them in 9VAC5-10 (General Definitions), unless otherwise required by context.
C. Terms shall have the meanings given them in 40 CFR 60.41f, except for the following:
"Administrator" means the board.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 33, Issue 10, eff. February 22, 2017.
9VAC5-40-5935. Emission limits and emission standards.
A. The owner of each MSW landfill having a design capacity greater than or equal to 2.5 million megagrams by mass and 2.5 million cubic meters by volume that meets the conditions of 40 CFR 60.33f(a)(1) through (4) shall collect and control MSW landfill emissions in accordance with the provisions of 40 CFR 60.33f(b)(1) through (3), and 40 CFR 60.33f(c)(1) through (4) except as provided in 40 CFR 60.24.
B. The owner of each MSW landfill with a design capacity less than 2.5 million megagrams and 2.5 million cubic meters shall submit an initial design capacity report to the administrator as provided in 40 CFR 60.38f(a).The landfill may calculate design capacity in either megagrams or cubic meters for comparison with the exemption values. Any density conversions shall be documented and submitted with the report. Submittal of the initial design capacity report fulfills the requirements of this article except as provided in 40 CFR 60.33f(d)(1) and (2).
C. The owner of each MSW landfill with a design capacity greater than 2.5 million megagrams and 2.5 million cubic meters shall either install a collection and control system as provided in subsection A of this section or calculate an initial NMOC emission rate for the landfill using the procedures specified in 40 CFR 60.35f(a). The NMOC emission rate shall be recalculated annually, except as provided in 40 CFR 60.38f(c)(3). The owner shall follow the procedures specified in 40 CFR 60.33f(e)(1) through (3).
D. The owner of each MSW landfill may cap, remove, or decommission the collection and control system used to comply with subsection A of this section if the criteria of 40 CFR 60.33f(f)(1) through (4) are met.
E. An active collection system used to comply with subsection A of this section shall meet the specifications for active collection system of 40 CFR 60.40f(a) through (c).
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 33, Issue 10, eff. February 22, 2017.
9VAC5-40-5940. Standard for visible emissions and fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of 9VAC5-40 (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply, with the exception of 9VAC5-40-80 (Standard for visible emissions), 9VAC5-40-100 (Monitoring), 9VAC5-40-110 (Test methods and procedures), and 9VAC5-40-120 (Waivers).
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 33, Issue 10, eff. February 22, 2017.
9VAC5-40-5945. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of 9VAC5-40 (Emission Standards for Odor, Rule 4‑2) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 33, Issue 10, eff. February 22, 2017.
9VAC5-40-5950. Compliance schedule.
The provisions of 40 CFR 60.32f apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 33, Issue 10, eff. February 22, 2017.
9VAC5-40-5955. Operating requirements.
The owner of an MSW landfill with a gas collection and control system used to comply with the provisions of 40 CFR 60.33f(b) and (c) shall meet the requirements of 40 CFR 60.34f(a) through (g).
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 33, Issue 10, eff. February 22, 2017.
9VAC5-40-5960. Compliance.
A. With regard to the emissions limits in 9VAC5-40-5940 and 9VAC5-40-5945, the provisions of 9VAC5-40-20 (Compliance) apply.
B. With regard to the emission limits in 9VAC5-40-5935 and 9VAC5-40-5955, the following provisions apply:
1. 9VAC5-40-20 B, C, D, and E;
2. To the extent specified in the federal regulations cited in subdivision 3 of this subsection, 40 CFR 60.7, 40 CFR 60.8, 40 CFR 60.11, and 40 CFR 60.13; and
3. 40 CFR 60.32f and 40 CFR 60.36f(a) through (e).
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 33, Issue 10, eff. February 22, 2017.
9VAC5-40-5965. Test methods and procedures, monitoring of operations.
A. With regard to the emissions standards in 9VAC5-40-5940 and 9VAC5-40-5945, the provisions of 9VAC5-40-30 (Emission testing) and 9VAC5-40-40 (Monitoring) apply.
B. With regard to the emission limits in 9VAC5-40-5935 and 9VAC5-40-5955, the following provisions apply:
1. 9VAC5-40-30 D and G;
2. 9VAC5-40-40 A and F;
3. 40 CFR 60.8(b) through (f), with the exception of paragraph (a);
4. 40 CFR 60.13; and
5. 40 CFR 60.35f(a) through (e), and 40 CFR 60.37f(a) through (h), except as provided in 40 CFR 60.38f(d)(2).
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 33, Issue 10, eff. February 22, 2017.
9VAC5-40-5970. Reporting and recordkeeping.
A. With regard to the emissions standards in 9VAC5-40-5940 and 9VAC5-40-5945, the provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
B. With regard to the emission limits in 9VAC5-40-5935 and 9VAC5-40-5955, the following provisions apply:
1. 9VAC5-40-50 F and H;
2. 40 CFR 60.7; and
3. 40 CFR 60.38f(a) through (n) except as provided in 40 CFR 60.24 and 40 CFR 60.38f(d)(2), and 40 CFR 60.39f(a) through (j).
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 33, Issue 10, eff. February 22, 2017; amended, Virginia Register Volume 37, Issue 4, eff. November 11, 2020.
9VAC5-40-5975. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 33, Issue 10, eff. February 22, 2017.
9VAC5-40-5980. Facility and control equipment maintenance or malfunction.
A. With regard to the emissions standards in 9VAC5-40-5940 and 9VAC5-40-5945, the provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply.
B. With regard to the emission limits in 9VAC5-40-5935 and 9VAC5-40-5955, the following provisions apply:
1. 9VAC5-20-180 with the exception of subsections E, F, and G; and
2. 40 CFR 60.36f(e) and 40 CFR 60.37f(h).
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 33, Issue 10, eff. February 22, 2017.
9VAC5-40-5985. Other permits.
A permit may be required prior to beginning any of the activities specified below if the provisions of 9VAC5-50 (New and Modified Stationary Sources) and 9VAC5-80 (Permits for Stationary Sources) apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (re-startup) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 33, Issue 10, eff. February 22, 2017.
9VAC5-40-5990. Documents incorporated by reference.
The U.S. Environmental Protection Agency regulations promulgated at Subpart Cf (40 CFR 60.30f et seq., Emission Guidelines and Compliance Times for Municipal Solid Waste Landfills) of 40 CFR Part 60 are incorporated by reference into this article. The specific version of the provisions incorporated by reference shall be that contained in the CFR in effect as specified in 9VAC5-20-21.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 33, Issue 10, eff. February 22, 2017.
9VAC5-40-6000. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6010. (Repealed.)
Statutory Authority
§ 10.1-1308 of the Code of Virginia and 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6020. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6030. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6040. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6050. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6060. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6070. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6080. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6090. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6100. (Repealed.)
Statutory Authority
§ 10.1-1308 of the Code of Virginia and 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6110. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6120. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6130. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6140. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6150. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6160. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6170. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6180. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; Errata, 16:19 VA.R. 2399 June 5, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6190. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6200. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6210. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6220. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-6230. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 16, Issue 17, eff. July 1, 2000; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
Article 45
Emission Standards for Commercial/Industrial Solid Waste Incinerators (Rule 4-45)
9VAC5-40-6250. Applicability and designation of affected facility.
Article 45
Emission Standards for Commercial/Industrial Solid Waste Incinerators (Rule 4-45)
A. The affected facilities to which the provisions of this article apply are (i) commercial/industrial solid waste incinerator (CISWI) units and air curtain incinerators that commenced construction on or before November 30, 1999; (ii) CISWI units and air curtain incinerators that commenced construction after November 30, 1999, but on or before June 4, 2010, or that commenced reconstruction or modification on or after June 1, 2001, but no later than August 7, 2013; or (iii) CISWI units other than incinerator units that commenced construction before June 4, 2010.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
C. Exempted from the provisions of this article are those units that meet the criteria listed in 40 CFR 60.2555.
D. The provisions of this article do not apply to a CISWI unit if the owner makes changes that meet the definition of modification or reconstruction after August 7, 2013, at which point the CISWI unit becomes subject to subpart CCCC of 40 CFR Part 60.
E. If the owner makes physical or operational changes to an existing CISWI unit primarily to comply with this article, subpart CCCC of 40 CFR Part 60 does not apply to that unit. Such changes do not qualify as modifications or reconstructions under subpart CCCC of 40 CFR Part 60.
F. Each owner shall submit an application for a federal operating permit in accordance with the provisions of 40 CFR 60.2805. Owners to whom this section applies should contact the appropriate regional office for guidance on applying for a federal (Title V) operating permit.
G. The requirement under 40 CFR 60.2555(g)(1) with regard to obtaining a permit under § 3005 of the Solid Waste Disposal Act (42 USC § 6901 et seq.) may be met by obtaining a permit from the department as required by 9VAC5-60 (Hazardous Air Pollutant Sources).
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013; Volume 33, Issue 4, eff. November 16, 2016.
9VAC5-40-6260. Definitions.
A. For the purpose of applying this article in the context of the Regulations for the Control and Abatement of Air Pollution and related uses, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined herein shall have the meanings given them in 9VAC5-10 (General Definitions), unless otherwise required by context.
C. Terms shall have the meaning given them in 40 CFR 60.2875, except for the following:
"Administrator" means the board.
"Table 1" means 9VAC5-40-6420.
"You" means the owner of an affected CISWI unit.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6270. Emission limits and emission standards.
No owner or other person shall cause or permit to be discharged into the atmosphere from any CISWI any emissions in excess of that allowed under 40 CFR 60.2670.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6280. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; repealed, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6290. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; repealed, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6300. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; repealed, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6310. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; repealed, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6320. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; repealed, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6330. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; repealed, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6340. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; repealed, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6350. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; repealed, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6360. Standard for visible emissions.
A. The provisions of Article 1 (9VAC5-40-60 et seq.) of 9VAC5 Chapter 40 (Emission Standards for Visible Emissions) apply except that the provisions in subsection B of this section apply instead of 9VAC5-40-80.
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any CISWI any visible emissions that exhibit greater than 10% opacity.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6370. Standard for fugitive dust/emissions.
A. The provisions of Article 1 (9VAC5-40-60 et seq.) of 9VAC5-40 (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply, with the exception of 9VAC5-40-80 (Standard for visible emissions), 9VAC5-40-100 (Monitoring), 9VAC5-40-110 (Test methods and procedures), and 9VAC5-40-120 (Waivers).
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any ash conveying system (including conveyor transfer points) any visible emissions for more than 5.0% of hourly observation period, measured at three, 1-hour observation periods.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6380. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of 9VAC5-40 (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6390. Standard for toxic pollutants.
The provisions of Article 4 (9VAC5-60-200 et seq.) of 9VAC5-60 (Emission Standards for Toxic Pollutants, Rule 6-4) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6400. Operator training and qualification.
The provisions of 40 CFR 60.2635 through 40 CFR 60.2665 apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6410. Waste management plan.
The owner of an affected facility shall prepare a written waste management plan in accordance with the provisions of 40 CFR 60.2620 through 40 CFR 60.2630.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6420. Compliance schedule.
A. All CISWI units regardless of category shall achieve final compliance as expeditiously as practicable but not later than February 7, 2018.
B. The owner shall submit a final control plan no later than February 7, 2015.
C. The provisions of 40 CFR 60.2575 through 40 CFR 60.2615 apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; Errata, 19:25 VA.R. 3844 August 25, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6421. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; repealed, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6422. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; repealed, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6430. Operating limits.
No owner or other person shall operate any CISWI unit in a manner that does not comply with the provisions of 40 CFR 60.2675 through 40 CFR 60.2680.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6440. Facility and control equipment maintenance or malfunction.
A. With regard to the emission standards set forth in 9VAC5-40-6360 A, 9VAC5-40-6370 A, 9VAC5-40-6380, and 9VAC5-40-6390, the provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply.
B. With regard to the emission limits in 9VAC5-40-6270, 9VAC5-40-6360 B, and 9VAC5-40-6370 B, the provisions of 9VAC5-20-180 apply, with the exception of subsections E, F, and G.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013; Volume 33, Issue 4, eff. November 16, 2016.
9VAC5-40-6450. Performance testing.
A. With regard to the emissions standards in 9VAC5-40-6360 A, 9VAC5-40-6370 A, 9VAC5-40-6380, and 9VAC5-40-6390, the provisions of 9VAC5-40-30 (Emission testing) apply.
B. With regard to the emission limits in 9VAC5-40-6270, 9VAC5-40-6360 B, and 9VAC5-40-6370 B, the following provisions apply:
1. 9VAC5-40-30 D and G;
2. 40 CFR 60.8, with the exception of paragraph (a); and
3. 40 CFR 60.2690 through 40 CFR 60.2695.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6460. Compliance.
A. With regard to the emissions standards in 9VAC5-40-6360 A, 9VAC5-40-6370 A, 9VAC5-40-6380, and 9VAC5-40-6390, the provisions of 9VAC5-40-20 (Compliance) apply.
B. With regard to the emission limits in 9VAC5-40-6270, 9VAC5-40-6360 B, and 9VAC5-40-6370 B, the following provisions apply:
1. 9VAC5-40-20 B, C, D, and E;
2. 40 CFR 60.11; and
3. 40 CFR 60.2700 through 40 CFR 60.2725.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6470. Monitoring.
A. With regard to the emissions standards in 9VAC5-40-6360 A, 9VAC5-40-6370 A, 9VAC5-40-6380, and 9VAC5-40-6390, the provisions of 9VAC5-40-40 (Monitoring) apply.
B. With regard to the emission limits in 9VAC5-40-6270, 9VAC5-40-6360 B, and 9VAC5-40-6370 B, the following provisions apply:
1. 9VAC5-40-40 A and F;
2. 40 CFR 60.13; and
3. 40 CFR 60.2730 through 40 CFR 60.2735.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6480. Recordkeeping and reporting.
A. With regard to the emissions standards in 9VAC5-40-6360 A, 9VAC5-40-6370 A, 9VAC5-40-6380, and 9VAC5-40-6390, the provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
B. With regard to the emission limits in 9VAC5-40-6270, 9VAC5-40-6260 B, and 9VAC5-40-6370 B, the following provisions apply:
1. 9VAC5-40-50 F and H;
2. 40 CFR 60.7; and
3. 40 CFR 60.2740 through 40 CFR 60.2800.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6490. Air curtain incinerators.
The provisions of 40 CFR 60.2810 through 40 CFR 60.2870 apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6500. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6510. Permits.
A permit may be required prior to beginning any of the activities specified below if the provisions of 9VAC5-50 (New and Modified Stationary Sources) and 9VAC5-80 (Permits for Stationary Sources) apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (re-startup) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 29, Issue 24, eff. August 28, 2013.
9VAC5-40-6520. Documents incorporated by reference.
A. The U.S. Environmental Protection Agency (EPA) regulations promulgated at Subpart DDDD (Emissions Guidelines and Compliance Times for Commercial and Industrial Solid Waste Incineration Units) of 40 CFR Part 60 and designated in subsection B of this section are incorporated by reference into this article. The 40 CFR section numbers appearing in subsection B of this section identify the specific provisions incorporated by reference. The specific version of the provisions incorporated by reference shall be that contained in the CFR in effect as specified in 9VAC5-20-21 B.
B. The following documents from the U.S. Environmental Protection Agency are incorporated herein by reference:
Model Rule, Increments of Progress
§ 60.2575, What are my requirements for meeting increments of progress and achieving final compliance?
§ 60.2580, When must I complete each increment of progress?
§ 60.2585, What must I include in the notifications of achievement of increments of progress?
§ 60.2590, When must I submit the notifications of achievement of increments of progress?
§ 60.2595, What if I do not meet an increment of progress?
§ 60.2600, How do I comply with the increment of progress for submittal of a control plan?
§ 60.2605, How do I comply with the increment of progress for achieving final compliance?
§ 60.2610, What must I do if I close my CISWI unit and then restart it?
§ 60.2615, What must I do if I plan to permanently close my CISWI unit and not restart it?
Model Rule, Waste Management Plan
§ 60.2620, What is a waste management plan?
§ 60.2625, When must I submit my waste management plan?
§ 60.2630, What should I include in my waste management plan?
Model Rule, Operator Training and Qualification
§ 60.2635, What are the operator training and qualification requirements?
§ 60.2640, When must the operator training course be completed?
§ 60.2645, How do I obtain my operator qualification?
§ 60.2650, How do I maintain my operator qualification?
§ 60.2655, How do I renew my lapsed operator qualification?
§ 60.2660, What site-specific documentation is required?
§ 60.2665, What if all the qualified operators are temporarily not accessible?
Model Rule, Emission Limitations and Operating Limits
§ 60.2670, What emission limitations must I meet and by when?
§ 60.2675, What operating limits must I meet and by when?
§ 60.2680, What if I do not use a wet scrubber, fabric filter, activated carbon injection, selective noncatalytic reduction, an electrostatic precipitator, or a dry scrubber to comply with the emission limitations?
Model Rule, Performance Testing
§ 60.2690, How do I conduct the initial and annual performance test?
§ 60.2695, How are the performance test data used?
Model Rule, Initial Compliance Requirements
§ 60.2700, How do I demonstrate initial compliance with the amended emission limitations and establish the operating limits?
§ 60.2705, By what date must I conduct the initial performance test?
§ 60.2706, By what date must I conduct the initial air pollution control device inspection?
Model Rule, Continuous Compliance Requirements
§ 60.2710, How do I demonstrate continuous compliance with the amended emission limitations and the operating limits?
§ 60.2715, By what date must I conduct the annual performance test?
§ 60.2716, By what date must I conduct the annual air pollution control device inspection?
§ 60.2720, May I conduct performance testing less often?
§ 60.2725, May I conduct a repeat performance test to establish new operating limits?
Model Rule, Monitoring
§ 60.2730, What monitoring equipment must I install and what parameters must I monitor?
§ 60.2735, Is there a minimum amount of monitoring data I must obtain?
Model Rule, Recordkeeping and Reporting
§ 60.2740, What records must I keep?
§ 60.2745, Where and in what format must I keep my records?
§ 60.2750, What reports must I submit?
§ 60.2755, When must I submit my waste management plan?
§ 60.2760, What information must I submit following my initial performance test?
§ 60.2765, When must I submit my annual report?
§ 60.2770, What information must I include in my annual report?
§ 60.2775, What else must I report if I have a deviation from the operating limits or the emission limitations?
§ 60.2780, What must I include in the deviation report?
§ 60.2785, What else must I report if I have a deviation from the requirement to have a qualified operator accessible?
§ 60.2790, Are there any other notifications or reports that I must submit?
§ 60.2795, In what form can I submit my reports?
§ 60.2800, Can reporting dates be changed?
Model Rule, Title V Operating Permits
§ 60.2805, Am I required to apply for and obtain a Title V operating permit for my unit?
Model Rule, Air Curtain Incinerators
§ 60.2810, What is an air curtain incinerator?
§ 60.2815, What are my requirements for meeting increments of progress and achieving final compliance?
§ 60.2820, When must I complete each increment of progress?
§ 60.2825, What must I include in the notifications of achievement of increments of progress?
§ 60.2830, When must I submit the notifications of achievement of increments of progress?
§ 60.2835, What if I do not meet an increment of progress?
§ 60.2840, How do I comply with the increment of progress for submittal of a control plan?
§ 60.2845, How do I comply with the increment of progress for achieving final compliance?
§ 60.2850, What must I do if I close my air curtain incinerator and then restart it?
§ 60.2855, What must I do if I plan to permanently close my air curtain incinerator and not restart it?
§ 60.2860, What are the emission limitations for air curtain incinerators?
§ 60.2865, How must I monitor opacity for air curtain incinerators?
§ 60.2870, What are the recordkeeping and reporting requirements for air curtain incinerators?
Model Rule, Definitions
§ 60.2875, What definitions must I know?
TABLES
Table 2 to Subpart DDDD of Part 60, Model Rule, Emission Limitations that Apply to Incinerators Before February 7, 2018.
Table 3 to Subpart DDDD of Part 60, Model Rule, Operating Limits for Wet Scrubbers.
Table 4 to Subpart DDDD of Part 60, Model Rule, Toxic Equivalency Factors.
Table 5 to Subpart DDDD of Part 60, Model Rule, Summary of Reporting Requirements.
Table 6 to Subpart DDDD of Part 60, Emission Limitations that Apply to Incinerators on and after February 7, 2018.
Table 7 to Subpart DDDD of Part 60, Emission Limitations that Apply to Energy Recovery Units After May 20, 2011, on or after February 7, 2018.
Table 8 to Subpart DDDD of Part 60, Emission Limitations that Apply to Waste-Burning Kilns after February 7, 2018.
Table 9 to Subpart DDDD of Part 60, Emission Limitations that Apply to Small, Remote Incinerators after February 7, 2018.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 29, Issue 24, eff. August 28, 2013; amended, Virginia Register Volume 33, Issue 4, eff. November 16, 2016.
Article 46
Emission Standards for Small Municipal Waste Combustors (Rule 4-46)
9VAC5-40-6550. Applicability and designation of affected facility.
Article 46
Emission Standards for Small Municipal Waste Combustors (Rule 4-46)
A. Except as provided in subsections C and D of this section, the affected facilities to which the provisions of this article apply are small municipal waste combustion units that (i) have the capacity to combust at least 35 tons per day of municipal solid waste but no more than 250 tons per day of municipal solid waste or refuse-derived fuel, and (ii) have commenced construction on or before August 30, 1999.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
C. The following provisions govern changes to municipal waste combustion units.
1. If the owner of a municipal waste combustion unit makes changes that meet the definition of modification or reconstruction after June 6, 2001, for subpart AAAA of 40 CFR Part 60, the municipal waste combustion unit becomes subject to subpart AAAA of 40 CFR Part 60 and the provisions of this article no longer apply to that unit.
2. If the owner of a municipal waste combustion unit makes physical or operational changes to an existing municipal waste combustion unit primarily to comply with the provisions of this article, subpart AAAA of 40 CFR Part 60 does not apply to that unit. Such changes do not constitute modifications or reconstructions under subpart AAAA of 40 CFR Part 60.
D. Exempt from the provisions of this article are the following.
1. Small municipal waste combustion units that combust less than 11 tons per day and meet the following conditions.
a. The unit is subject to a federally enforceable permit limiting the amount of municipal solid waste combusted to less than 11 tons per day.
b. The owner notifies the board that the unit qualifies for the exemption.
c. The owner provides the board with a copy of the federally enforceable permit.
d. The owner keeps daily records of the amount of municipal solid waste combusted.
2. Small power production units that meet the following conditions.
a. The unit qualifies as a small power production facility under § 3(17)(C) of the Federal Power Act (16 USC § 796(17)(C)).
b. The unit combusts homogeneous waste (excluding refuse-derived fuel) to produce electricity.
c. The owner notifies the board that the unit qualifies for the exemption.
d. The board receives documentation from the owner that the unit qualifies for the exemption.
3. Cogeneration units that meet the following conditions.
a. The unit qualifies as a cogeneration facility under § 3(18)(B) of the Federal Power Act (16 USC § 796(18)(B)).
b. The unit combusts homogeneous waste (excluding refuse-derived fuel) to produce electricity and steam or other forms of energy used for industrial, commercial, heating, or cooling purposes.
c. The owner notifies the board that the unit qualifies for the exemption.
d. The board receives documentation from the owner that the unit qualifies for the exemption.
4. Municipal waste combustion units that combust only tires and meet the following conditions.
a. The unit combusts a single-item waste stream of tires and no other municipal waste (the unit can co-fire coal, fuel oil, natural gas, or other nonmunicipal solid waste).
b. The owner notifies the board that the unit qualifies for the exemption.
c. The board receives documentation from the owner that the unit qualifies for the exemption.
5. Hazardous waste combustion units that have received a permit under § 3005 of the Solid Waste Disposal Act (42 USC § 6901 et seq.).
6. Materials recovery units that combust waste mainly to recover metals. Primary and secondary smelters may qualify.
7. Co-fired units that meet the following conditions.
a. The unit has a federally enforceable permit limiting municipal solid waste combustion to 30% of the total fuel input by weight.
b. The board is notified by the owner that the unit qualifies for the exemption.
c. The owner provides the board with a copy of the federally enforceable permit.
d. The owner records the weights, each quarter, of municipal solid waste and of all other fuels combusted.
8. Plastics/rubber recycling units that meet the following conditions.
a. The pyrolysis/combustion unit is an integrated part of a plastics/rubber recycling unit.
b. The owner records the weight, each quarter, of plastics, rubber, and rubber tires processed.
c. The owner records the weight, each quarter, of feed stocks produced and marketed from chemical plants and petroleum refineries.
d. The owner maintains the name and address of the purchaser of the feed stocks.
9. Units that combust fuels made from products of plastics/rubber recycling plants and meet the following criteria.
a. The unit combusts gasoline, diesel fuel, jet fuel, fuel oils, residual oil, refinery gas, petroleum coke, liquefied petroleum gas, propane, or butane produced by chemical plants or petroleum refineries that use feed stocks produced by plastics/rubber recycling units.
b. The unit does not combust any other municipal solid waste.
10. Cement kilns that combust municipal solid waste.
11. Air curtain incinerators that combust 100% yard waste are exempt from the requirements of this article except they shall meet the requirements of 9VAC5-40-6780.
12. Affected municipal waste combustion units that meet the following criteria.
a. The owner reduces, by the final compliance dates in 9VAC5-40-6710, the maximum combustion capacity of the unit to less than 35 tons per day of municipal solid waste. A permit restriction or a change in the method of operation does not qualify as a reduction in capacity.
b. The owner submits a final control plan and the notifications of achievement of increments of progress as specified in 9VAC5-40-6710 B. The final control plan shall, at a minimum, include the following.
(1) A description of the physical changes that will be made to accomplish the reduction.
(2) Calculations of the current maximum combustion capacity and the planned maximum combustion capacity after the reduction. The combustion capacity of a municipal waste combustion unit shall be calculated as specified in 9VAC5-40-6730 F.
E. Each owner shall submit an application for a federal operating permit no later than December 6, 2003. If the unit is subject to the federal operating permit program as a result of some triggering requirement(s) other than this article (for example, being a major source), then the unit may be required to apply for and obtain a federal operating permit prior to the deadline in this subsection. If more than one requirement triggers the requirement to apply for a federal operating permit, the 12-month timeframe for filing a permit application is triggered by the requirement which first causes the source to be subject to the federal operating permit program.
F. The provisions of 40 CFR Part 60 cited in this article are applicable only to the extent that they are incorporated by reference in Article 5 (9VAC5-50-400 et seq.) of Part II of 9VAC5 Chapter 50.
G. The requirement of subdivision D 5 of this section with regard to obtaining a permit under § 3005 of the Solid Waste Disposal Act (42 USC § 6901 et seq.) may be met by obtaining a permit from the department as required by 9VAC20 Chapter 60.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6560. Definitions.
A. For the purpose of applying this article in the context of the Regulations for the Control and Abatement of Air Pollution related uses, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined herein shall have the meanings given them in 9VAC5 Chapter 10, unless otherwise required by context.
C. Terms defined.
"Air curtain incinerator" means an incinerator that operates by forcefully projecting a curtain of air across an open chamber or pit in which combustion occurs. Incinerators of that type can be constructed above or below ground and with or without refractory walls and floor.
"Batch municipal waste combustion unit" means a municipal waste combustion unit designed so it cannot combust municipal solid waste continuously 24 hours per day because the design does not allow waste to be fed to the unit or ash to be removed during combustion.
"Calendar quarter" means three consecutive months (nonoverlapping) beginning on January 1, April 1, July 1, or October 1.
"Calendar year" means 365 (or 366 consecutive days in leap years) consecutive days starting on January 1 and ending on December 31.
"Chief facility operator" means the person in direct charge and control of the operation of a municipal waste combustion unit. That person is responsible for daily onsite supervision, technical direction, management, and overall performance of the municipal waste combustion unit.
"Class I units" mean small municipal waste combustion units subject to this article that are located at municipal waste combustion plants with an aggregate plant combustion capacity greater than 250 tons per day of municipal solid waste. See the definition in this section of "municipal waste combustion plant capacity" for specification of which units at a plant site are included in the aggregate capacity calculation.
"Class II units" mean small municipal combustion units subject to this article that are located at municipal waste combustion plants with aggregate plant combustion capacity less than or equal to 250 tons per day of municipal solid waste. See the definition in this section of "municipal waste combustion plant capacity" for specification of which units at a plant site are included in the aggregate capacity calculation.
"Clean wood" means untreated wood or untreated wood products including clean untreated lumber, tree stumps (whole or chipped), and tree limbs (whole or chipped). Clean wood does not include: (i) yard waste, or (ii) construction, renovation, or demolition wastes (for example, railroad ties and telephone poles) that are exempt from the definition of "municipal solid waste" in this section.
"Co-fired combustion unit" means a unit that combusts municipal solid waste with nonmunicipal solid waste fuel (for example, coal, industrial process waste). To be considered a co-fired combustion unit, the unit shall be subject to a federally enforceable permit that limits it to combusting a fuel feed stream that is 30% or less (by weight) municipal solid waste as measured each calendar quarter.
"Continuous burning" means the continuous, semicontinuous, or batch feeding of municipal solid waste to dispose of the waste, produce energy, or provide heat to the combustion system in preparation for waste disposal or energy production. Continuous burning does not mean the use of municipal solid waste solely to thermally protect the grate or hearth during the startup period when municipal solid waste is not fed to the grate or hearth.
"Continuous emission monitoring system" means a monitoring system that continuously measures the emissions of a pollutant from a municipal waste combustion unit.
"Dioxins/furans" mean tetra-through octachlorinated dibenzo-p-dioxins and dibenzofurans.
"Eight-hour block average" means the average of all hourly emission concentrations or parameter levels when the municipal waste combustion unit operates and combusts municipal solid waste measured over any of three eight-hour periods of time: (i) midnight to 8 a.m., (ii) 8 a.m. to 4 p.m., and (iii) 4 p.m. to midnight.
"Federal operating permit" means a permit issued under Article 1 (9VAC5-80-50 et seq.) of Part II of 9VAC5-80.
"First calendar half" means the period that starts on January 1 and ends on June 30 in any year.
"Fluidized bed combustion unit" means a unit where municipal waste is combusted in a fluidized bed of material. The fluidized bed material may remain in the primary combustion zone or may be carried out of the primary combustion zone and returned through a recirculation loop.
"Four-hour block average" means the average of all hourly emission concentrations or parameter levels when the municipal waste combustion unit operates and combusts municipal solid waste measured over any of six four-hour periods: (i) midnight to 4 a.m., (ii) 4 a.m. to 8 a.m., (iii) 8 a.m. to noon, (iv) noon to 4 p.m., (v) 4 p.m. to 8 p.m., and (vi) 8 p.m. to midnight.
"Mass burn refractory municipal waste combustion unit" means a field-erected municipal waste combustion unit that combusts municipal solid waste in a refractory wall furnace. Unless otherwise specified, that includes municipal waste combustion units with a cylindrical rotary refractory wall furnace.
"Mass burn rotary waterwall municipal waste combustion unit" means a field-erected municipal waste combustion unit that combusts municipal solid waste in a cylindrical rotary waterwall furnace.
"Mass burn waterwall municipal waste combustion unit" means a field-erected municipal waste combustion unit that combusts municipal solid waste in a waterwall furnace.
"Maximum demonstrated load of a municipal waste combustion unit" means the highest four-hour block arithmetic average municipal waste combustion unit load achieved during four consecutive hours in the course of the most recent dioxins/furans emission test that demonstrates compliance with the applicable emission limit for dioxins/furans specified in this article.
"Maximum demonstrated temperature of the particulate matter control device" means the highest four-hour block arithmetic average flue gas temperature measured at the inlet of the particulate matter control device during four consecutive hours in the course of the most recent emission test for dioxins/furans emissions that demonstrates compliance with the limits specified in this article.
"Medical/infectious waste" means any waste generated in the diagnosis, treatment, or immunization of human beings or animals, in research pertaining thereto, or in the production or testing of biologicals that is listed in subdivisions 1 through 9 of this definition. The definition of medical/infectious waste does not include hazardous waste identified or listed under the regulations in 40 CFR Part 261; household waste, as defined in 40 CFR 261.4(b)(1); ash from incineration of medical/infectious waste, once the incineration process has been completed; human corpses, remains, and anatomical parts that are intended for interment or cremation; and domestic sewage materials identified in 40 CFR 261.4(a)(1).
1. Cultures and stocks of infectious agents and associated biologicals, including: cultures from medical and pathological laboratories; cultures and stocks of infectious agents from research and industrial laboratories; wastes from the production of biologicals; discarded live and attenuated vaccines; and culture dishes and devices used to transfer, inoculate, and mix cultures.
2. Human pathological waste, including tissues, organs, and body parts and body fluids that are removed during surgery or autopsy, or other medical procedures, and specimens of body fluids and their containers.
3. Human blood and blood products, regardless of whether containerized, including:
a. Liquid human blood;
b. Products of blood;
c. Items containing unabsorbed or free-flowing blood;
d. Items saturated or dripping or both with human blood; or
e. Items that were saturated and dripping or both with human blood that are now caked with dried human blood; including serum, plasma, and other blood components, and their containers, which were used or intended for use in either patient care, testing and laboratory analysis or the development of pharmaceuticals. Intravenous bags are also included in this category.
4. Regardless of the presence of infectious agents, sharps that have been used in animal or human patient care or treatment or in medical, research, or industrial laboratories, including hypodermic needles, syringes (with or without the attached needle), pasteur pipettes, scalpel blades, blood vials, needles with attached tubing, and culture dishes. Also included are other types of broken or unbroken glassware that may have been in contact with infectious agents, such as used slides and cover slips.
5. Animal waste including contaminated animal carcasses, body parts, and bedding of animals that were known to have been exposed to infectious agents during research (including research in veterinary hospitals), production of biologicals or testing of pharmaceuticals.
6. Isolation wastes including biological waste and discarded materials contaminated with blood, excretions, exudates, or secretions from humans who are isolated to protect others from certain highly communicable diseases, or isolated animals known to be infected with highly communicable diseases.
7. Unused sharps including the following unused, discarded sharps: hypodermic needles, suture needles, syringes, and scalpel blades.
8. Any waste that is contaminated or mixed with any waste listed in subdivisions 1 through 7 of this definition.
9. Any residue or contaminated soil, waste, or other debris resulting from the cleaning of a spill of any waste listed in subdivisions 1 through 8 of this definition.
"Mixed fuel-fired (pulverized coal/refuse-derived fuel) combustion unit" means a combustion unit that combusts coal and refuse-derived fuel simultaneously, in which pulverized coal is introduced into an air stream that carries the coal to the combustion chamber of the unit where it is combusted in suspension. That includes both conventional pulverized coal and micropulverized coal.
"Modification" or "modified municipal waste combustion unit" means a municipal waste combustion unit that has been modified after June 6, 2001, and that meets one of the following criteria: (i) the cumulative cost of the changes over the life of the unit exceeds 50% of the original cost of building and installing the unit (not including the cost of land) updated to current costs; or (ii) any physical change in the municipal waste combustion unit or change in the method of operating it that increases the emission level of any air pollutant for which new source performance standards have been established under § 129 or § 111 of the federal Clean Air Act. Increases in the emission level of any air pollutant are determined when the municipal waste combustion unit operates at 100% of its physical load capability and are measured downstream of all air pollution control devices. Load restrictions based on permits or other nonphysical operational restrictions cannot be considered in the determination.
"Modular excess-air municipal waste combustion unit" means a municipal waste combustion unit that combusts municipal solid waste, is not field-erected, and has multiple combustion chambers, all of which are designed to operate at conditions with combustion air amounts in excess of theoretical air requirements.
"Modular starved-air municipal waste combustion unit" means a municipal waste combustion unit that combusts municipal solid waste, is not field-erected, and has multiple combustion chambers in which the primary combustion chamber is designed to operate at substoichiometric conditions.
"Municipal solid waste or municipal-type solid waste" means household, commercial/retail, or institutional waste. Household waste includes material discarded by residential dwellings, hotels, motels, and other similar permanent or temporary housing. Commercial/retail waste includes material discarded by stores, offices, restaurants, warehouses, nonmanufacturing activities at industrial facilities, and other similar establishments or facilities. Institutional waste includes materials discarded by schools, by hospitals (nonmedical), by nonmanufacturing activities at prisons and government facilities, and other similar establishments or facilities. Household, commercial/retail, and institutional waste does include yard waste and refuse-derived fuel. Household, commercial/retail, and institutional waste does not include used oil; sewage sludge; wood pallets; construction, renovation, and demolition wastes (which include railroad ties and telephone poles); clean wood; industrial process or manufacturing wastes; medical waste; or motor vehicles (including motor vehicle parts or vehicle fluff).
"Municipal waste combustion plant" means one or more municipal waste combustion units at the same location.
"Municipal waste combustion plant capacity" means the aggregate municipal waste combustion capacity of all municipal waste combustion units at the plant that are not subject to subparts Ea, Eb, or AAAA of 40 CFR Part 60.
"Municipal waste combustion unit" means any setting or equipment that combusts solid, liquid, or gasified municipal solid waste including, but not limited to, field-erected combustion units (with or without heat recovery), modular combustion units (starved-air or excess-air), boilers (for example, steam generating units), furnaces (whether suspension-fired, grate-fired, mass-fired, air curtain incinerators, or fluidized bed-fired), and pyrolysis/combustion units. Municipal waste combustion units do not include pyrolysis or combustion units located at a plastics or rubber recycling unit. Municipal waste combustion units do not include cement kilns that combust municipal solid waste. Municipal waste combustion units do not include internal combustion engines, gas turbines, or other combustion devices that combust landfill gases collected by landfill gas collection systems. The municipal waste combustion unit includes, but is not limited to, the municipal solid waste fuel feed system, grate system, flue gas system, bottom ash system, and the combustion unit water system. The municipal waste combustion unit does not include air pollution control equipment, the stack, water treatment equipment, or the turbine-generator set. The municipal waste combustion unit boundary starts at the municipal solid waste pit or hopper and extends through: (i) the combustion unit flue gas system, which ends immediately after the heat recovery equipment or, if there is no heat recovery equipment, immediately after the combustion chamber; (ii) the combustion unit bottom ash system, which ends at the truck loading station or similar equipment that transfers the ash to final disposal. It includes all ash handling systems connected to the bottom ash handling system; and (iii) the combustion unit water system, which starts at the feed water pump and ends at the piping that exits the steam drum or superheater.
"Particulate matter" means total particulate matter emitted from municipal waste combustion units as measured using Reference Method 5 and the procedures specified in 9VAC5-40-6740 D.
"Plastics or rubber recycling unit" means an integrated processing unit for which plastics, rubber, or rubber tires are the only feed materials (incidental contaminants may be in the feed materials). The feed materials are processed and marketed to become input feed stock for chemical plants or petroleum refineries. Each calendar quarter, the combined weight of the feed stock that a plastics or rubber recycling unit produces shall be more than 70% of the combined weight of the plastics, rubber, and rubber tires that recycling unit processes. The plastics, rubber, or rubber tires fed to the recycling unit may originate from separating or diverting plastics, rubber, or rubber tires from municipal or industrial solid waste. The feed materials may include manufacturing scraps, trimmings, and off-specification plastics, rubber, and rubber tire discards. The plastics, rubber, and rubber tires fed to the recycling unit may contain incidental contaminants (for example, paper labels on plastic bottles or metal rings on plastic bottle caps).
"Potential hydrogen chloride emissions" means the level of emissions from a municipal waste combustion unit that would occur from combusting municipal solid waste without emission controls for acid gases.
"Potential mercury emissions" means the level of emissions from a municipal waste combustion unit that would occur from combusting municipal solid waste without controls for mercury emissions.
"Potential sulfur dioxide emissions" means the level of emissions from a municipal waste combustion unit that would occur from combusting municipal solid waste without emission controls for acid gases.
"Pyrolysis/combustion unit" means a unit that produces gases, liquids, or solids by heating municipal solid waste. The gases, liquids, or solids produced are combusted and the emissions vented to the atmosphere.
"Reconstruction" means rebuilding a municipal waste combustion unit and meeting two criteria: (i) the reconstruction begins after June 6, 2001; and (ii) the cumulative cost of the construction over the life of the unit exceeds 50% of the original cost of building and installing the municipal waste combustion unit (not including land) updated to current costs (current dollars). To determine what systems are within the boundary of the municipal waste combustion unit used to calculate the costs, see the definition in this section of "municipal waste combustion unit."
"Refractory unit" or "refractory wall furnace" means a municipal waste combustion unit that has no energy recovery (such as through a waterwall) in the furnace of the municipal waste combustion unit.
"Refuse-derived fuel" means a type of municipal solid waste produced by processing municipal solid waste through shredding and size classification. Refuse-derived fuel includes all classes of refuse-derived fuel, including low-density fluff refuse-derived fuel through densified refuse-derived fuel, and pelletized refuse-derived fuel.
"Same location" means the same or contiguous properties under common ownership or control, including those separated only by a street, road, highway, or other public right-of-way. Common ownership or control includes properties that are owned, leased, or operated by the same entity, parent entity, subsidiary, subdivision, or any combination thereof. Entities may include a municipality, other governmental unit, or any quasi-governmental authority (for example, a public utility district or regional authority for waste disposal).
"Second calendar half" means the period that starts on July 1 and ends on December 31 in any year.
"Shift supervisor" means the person who is in direct charge and control of operating a municipal waste combustion unit and who is responsible for onsite supervision, technical direction, management, and overall performance of the municipal waste combustion unit during an assigned shift.
"Spreader stoker, mixed fuel-fired (coal/refuse-derived fuel) combustion unit" means a municipal waste combustion unit that combusts coal and refuse-derived fuel simultaneously, in which coal is introduced to the combustion zone by a mechanism that throws the fuel onto a grate from above. Combustion takes place both in suspension and on the grate.
"Standard conditions," when referring to units of measure, means a temperature of 20°C and a pressure of 101.3 kilopascals.
"Startup period" means the period when a municipal waste combustion unit begins the continuous combustion of municipal solid waste. It does not include any warmup period during which the municipal waste combustion unit combusts fossil fuel or other solid waste fuel but receives no municipal solid waste.
"Stoker (refuse-derived fuel) combustion unit" means a steam generating unit that combusts refuse-derived fuel in a semisuspension combusting mode, using air-fed distributors.
"Total mass dioxins/furans or total mass" means the total mass of tetra-through octachlorinated dibenzo-p-dioxins and dibenzofurans as determined using Reference Method 23 and the procedures specified in 9VAC5-40-6740 D.
"Twenty-four hour daily average" or "24-hour daily average" means either the arithmetic mean or geometric mean (as specified) of all hourly emission concentrations when the municipal waste combustion unit operates and combusts municipal solid waste measured during the 24 hours between midnight and the following midnight.
"Untreated lumber" means wood or wood products that have been cut or shaped and include wet, air-dried, and kiln-dried wood products. Untreated lumber does not include wood products that have been painted, pigment-stained, or pressure-treated by compounds such as chromate copper arsenate, pentachlorophenol, and creosote.
"Waterwall furnace" means a municipal waste combustion unit that has energy (heat) recovery in the furnace (for example, radiant heat transfer section) of the combustion unit.
"Yard waste" means grass, grass clippings, bushes, shrubs, and clippings from bushes and shrubs that come from residential, commercial/retail, institutional, or industrial sources as part of maintaining yards or other private or public lands. Yard waste does not include: (i) construction, renovation, and demolition wastes that are exempt from the definition of "municipal solid waste" in this section; or (ii) clean wood that is exempt from the definition of "municipal solid waste" in this section.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6570. Standard for particulate matter.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any Class I unit any particulate emissions in excess of 27 milligrams per dry standard cubic meter, measured at 7.0% oxygen, three-run average.
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any Class II unit any particulate emissions in excess of 70 milligrams per dry standard cubic meter, measured at 7.0% oxygen, three-run average.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6580. Standard for carbon monoxide.
No owner or other person shall cause or permit to be discharged into the atmosphere from any small municipal waste combustion unit any carbon monoxide emissions in excess of the following.
1. For fluidized bed units: 100 parts per million by dry volume, measured at 7.0% oxygen, four-hour block average, arithmetic mean.
2. For fluidized bed, mixed fuel (wood/refuse-derived fuel) units: 200 parts per million by dry volume measured at 7.0% oxygen, 24-hour block average, geometric mean.
3. For mass burn rotary refractory units: 100 parts per million by dry volume measured at 7.0% oxygen, four-hour block average, arithmetic mean.
4. For mass burn rotary waterwall units: 250 parts per million by dry volume measured at 7.0% oxygen, 24-hour block average, arithmetic mean.
5. For mass burn waterwall and refractory units: 100 parts per million by dry volume measured at 7.0% oxygen, four-hour block average, arithmetic mean.
6. For mixed fuel-fired (pulverized coal/refuse-derived fuel) units: 150 parts per million by dry volume measured at 7.0% oxygen, four-hour block average, arithmetic mean.
7. For modular starved-air and excess air units: 50 parts per million by dry volume measured at 7.0% oxygen, four-hour block average, arithmetic mean.
8. For spreader stoker, mixed fuel-fired (coal/refuse-derived fuel) units: 200 parts per million by dry volume measured at 7.0% oxygen, 24-hour daily block average, arithmetic mean.
9. For stoker, refuse-derived fuel units: 200 parts per million by dry volume measured at 7.0% oxygen, 24-hour daily block average, arithmetic mean.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6590. Standard for dioxins/furans.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any Class I unit any dioxin/furan (total mass basis) emissions in excess of the following.
1. For units that do not use an electrostatic precipitator-based emission control system: 30 nanograms per dry standard cubic meter, measured at 7.0% oxygen, three-run average (minimum run duration of four hours).
2. For units that use electrostatic precipitator-based emission control system: 60 nanograms per dry standard cubic meter, measured at 7.0% oxygen, three-run average (minimum run duration of four hours).
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any Class II unit any dioxin/furan emissions (total mass basis) in excess of 125 nanograms per dry standard cubic meter, measured at 7.0% oxygen, three-run average (minimum run duration of four hours).
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6600. Standard for hydrogen chloride.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any Class I unit any hydrogen chloride emissions in excess of 31 parts per million by dry volume or 95% reduction of potential emissions, measured at 7.0% oxygen, three-run average (minimum run duration of one hour).
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any Class II unit any hydrogen chloride emissions in excess of 250 parts per million by dry volume or 50% reduction of potential emissions, measured at 7.0% oxygen, three-run average (minimum run duration of one hour).
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6610. Standard for sulfur dioxide.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any Class I unit any sulfur dioxide emissions in excess of 31 parts per million by dry volume or 75% reduction of potential emissions, measured at 7.0% oxygen, 24-hour daily block geometric average concentration or percent reduction.
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any Class II unit any sulfur dioxide emissions in excess of 77 parts per million by dry volume or 50% reduction of potential emissions, measured at 7.0% oxygen, 24-hour daily block geometric average concentration or percent reduction.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6620. Standard for nitrogen oxides.
No owner or other person shall cause or permit to be discharged into the atmosphere from any Class I unit any nitrogen oxide emissions in excess of the following:
1. For mass burn waterwall units: 200 parts per million by dry volume, measured at 7.0% oxygen, 24-hour daily block arithmetic average concentration.
2. For mass burn rotary waterwall units: 170 parts per million by dry volume measured at 7.0% oxygen, 24-hour daily block arithmetic average concentration.
3. For refuse-derived fuel units: 250 parts per million by dry volume, measured at 7.0% oxygen, 24-hour daily block arithmetic average concentration.
4. For fluidized bed units: 220 parts per million by dry volume, measured at 7.0% oxygen, 24-hour daily block arithmetic average concentration.
5. For mass burn refractory units: 350 parts per million by dry volume, measured at 7.0% oxygen, 24-hour daily block arithmetic average concentration.
6. For modular excess air units: 190 parts per million by dry volume, measured at 7.0% oxygen, 24-hour daily block arithmetic average concentration.
7. For modular starved air units: 380 parts per million by dry volume, measured at 7.0% oxygen, 24-hour daily block arithmetic average concentration.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003; amended, Virginia Register Volume 21, Issue 15, eff. May 4, 2005.
9VAC5-40-6630. Standard for lead.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any Class I unit any lead emissions in excess of 0.490 milligrams per dry standard cubic meter, measured at 7.0% oxygen, three-run average.
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any Class II unit any lead emissions in excess of 1.6 milligrams per dry standard cubic meter, measured at 7.0% oxygen, three-run average.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6640. Standard for cadmium.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any Class I unit any cadmium emissions in excess of 0.040 milligrams per dry standard cubic meter, measured at 7.0% oxygen, three-run average.
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any Class II unit any cadmium emissions in excess of 0.10 milligrams per dry standard cubic meter, measured at 7.0% oxygen, three-run average.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6650. Standard for mercury.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any Class I unit any mercury emissions in excess of 0.080 milligrams per dry standard cubic meter, measured at 7.0% oxygen, three-run average.
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any Class II unit any mercury emissions in excess of 0.080 milligrams per dry standard cubic meter, measured at 7.0% oxygen, three-run average.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6660. Standard for visible emissions.
A. The provisions of Article 1 (9VAC5-40-60 et seq.) of 9VAC5 Chapter 40 (Emission Standards for Visible Emissions) apply except that the provisions in subsection B of this section apply instead of 9VAC5-40-80.
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any small municipal waste combustion unit any visible emissions that exhibit greater than 10% opacity, measured at 30 six-minute averages.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6670. Standard for fugitive dust/emissions.
A. The provisions of Article 1 (9VAC5-40-60 et seq.) of 9VAC5 Chapter 40 (Emission Standards for Fugitive Dust/Emissions, Rule 4-1) apply.
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any small municipal waste combustion unit any fugitive ash visible emissions for more than 5.0% of hourly observation period, measured at three one-hour observation periods.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6680. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of 9VAC5 Chapter 40 (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6690. Standard for toxic pollutants.
The provisions of Article 4 (9VAC5-60-200 et seq.) of 9VAC5 Chapter 60 (Emission Standards for Toxic Pollutants, Rule 6-4) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6700. Operator training and certification.
A. Each chief facility operator, shift supervisor, and control room operator shall complete a training course as follows.
1. The operator training course shall be completed by the later of (i) January 31, 2004, (ii) six months after the municipal waste combustion unit starts up, or (iii) the date before an employee assumes responsibilities that affect operation of the municipal waste combustion unit.
2. The requirement in subdivision A 1 of this section does not apply to chief facility operators, shift supervisors, and control room operators who have obtained full certification from the American Society of Mechanical Engineers on or before January 31, 2003.
3. The owner may request that the board waive the requirement in subdivision A 1 of this section for chief facility operators, shift supervisors, and control room operators who have obtained provisional certification from the American Society of Mechanical Engineers on or before January 31, 2003.
B. A plant-specific training course and operating manual shall be established as follows.
1. All employees with responsibilities that affect how a municipal waste combustion unit operates, including but not limited to, chief facility operators, shift supervisors, control room operators, ash handlers, maintenance personnel, and crane or load handlers, shall complete the plant-specific training course.
2. A plant-specific operating manual shall be developed by the later of (i) six months after the municipal waste combustor unit starts up, or (ii) January 31, 2004.
3. A program to review the plant-specific operating manual with people whose responsibilities affect the operation of the municipal waste combustion unit shall be established. Initial review of the program shall be completed by the later of (i) January 31, 2004, (ii) six months after the municipal waste combustor unit starts up, or (iii) the date before an employee assumes responsibilities that affect operation of the municipal waste combustion unit.
4. The manual shall be updated and reviewed with staff annually.
5. The following information shall be included in the plant-specific operating manual.
a. A summary of all applicable requirements in this article.
b. A description of the basic combustion principles that apply to municipal waste combustion units.
c. Procedures for receiving, handling, and feeding municipal solid waste.
d. Procedures to be followed during periods of startup, shutdown, and malfunction of the municipal waste combustion unit.
e. Procedures for maintaining a proper level of combustion air supply.
f. Procedures for operating the municipal waste combustion unit in compliance with the requirements contained in this article.
g. Procedures for responding to periodic upset or off-specification conditions.
h. Procedures for minimizing carryover of particulate matter.
i. Procedures for handling ash.
j. Procedures for monitoring emissions from the municipal waste combustion unit.
k. Procedures for recordkeeping and reporting.
6. The operating manual shall be maintained in an easily accessible location at the plant. It shall be available for review or inspection by all employees who are required to review it and by the board.
C. Each chief facility operator and shift supervisor shall obtain operator certification as follows.
1. Each chief facility operator and shift supervisor shall obtain and maintain one of the following:
a. A current provisional operator certification from the American Society of Mechanical Engineers (QRO-1-1994); or
b. A current provisional operator certification approved by the board.
2. The certification and licensing required in subdivision 1 of this subsection shall be obtained by the later of the following:
a. For Class I units, January 31, 2004; for Class II units, July 31, 2004.
b. Six months after the municipal waste combustion unit starts up.
c. Six months after being transferred to the municipal waste combustion unit or six months after they are hired to work at the municipal waste combustion unit.
3. Each chief facility operator and shift supervisor shall take one of the following actions:
a. Obtain a full certification from the American Society of Mechanical Engineers or a certification approved by the board.
b. Schedule a full certification exam with the American Society of Mechanical Engineers (QRO-1-1994).
c. Schedule a full certification exam to obtain a certification approval by the board.
4. The chief facility operator and shift supervisor shall obtain the full certification or be scheduled to take the certification exam as required in subdivision C 3 of this section by the later of the following dates.
a. For Class I units, January 31, 2004; for Class II units, July 31, 2004.
b. Six months after the municipal waste combustion unit starts up.
c. Six months after they transfer to the municipal waste combustion unit or 6 months after they are hired to work at the municipal waste combustion unit.
D. After the required date for full or provisional certification, no municipal waste combustion unit shall be operated unless one of the following employees is on duty:
1. A fully certified chief facility operator.
2. A provisionally certified chief facility operator who is scheduled to take the full certification exam.
3. A fully certified shift supervisor.
4. A provisionally certified shift supervisor who is scheduled to take the full certification exam.
E. No owner of an affected facility shall allow the facility to be operated at any time unless a person is on duty who is responsible for the proper operation of the facility and has a license from the Board for Waste Management Facility Operators in the correct classification. No provision of this article shall relieve any owner from the responsibility to comply in all respects with the requirements of Chapter 22.1 (§ 54.1-2209 et seq.) of Title 54.1 of the Code of Virginia and with 18VAC155 Chapter 20.
F. If the certified chief facility operator and certified shift supervisor both are unavailable, a provisionally certified control room operator at the municipal waste combustion unit may fulfill the certified operator requirement. Depending on the length of time that a certified chief facility operator and certified shift supervisor are away, the owner shall meet one of the following:
1. When the certified chief facility operator and certified shift supervisor are both offsite for 12 hours or less and no other certified operator is onsite, the provisionally certified control room operator may perform those duties without notice to, or approval by, the board.
2. When the certified chief facility operator and certified shift supervisor are offsite for more than 12 hours, but for two weeks or less, and no other certified operator is onsite, the provisionally certified control room operator may perform those duties without notice to, or approval by, the board. The periods when the certified chief facility operator and certified shift supervisor are offsite shall be recorded and included in the annual report as specified under 9VAC5-40-6770 B 2 l.
3. When the certified chief facility operator and certified shift supervisor are offsite for more than two weeks, and no other certified operator is onsite, the provisionally certified control room operator may perform those duties without notice to, or approval by, the board, and the owner shall:
a. Notify the board in writing what caused the absence and what is being done to ensure that a certified chief facility operator or certified shift supervisor is onsite; and
b. Submit a status report and corrective action summary to the board every four weeks following the initial notification. If the board notifies the owner that the status report or corrective action summary is disapproved, the municipal waste combustion unit shall cease operation after 90 days. If corrective actions are taken in the 90-day period such that the board withdraws the disapproval, municipal waste combustion unit operation may continue.
G. The requirements of this section with regard to scheduling and obtaining certification through a program approved by the board may be met by obtaining a license from the Board for Waste Management Facility Operators. All training and licensing shall be conducted in accordance with Chapter 22.1 (54.1-2209 et seq.) of Title 54.1 of the Code of Virginia and with 18VAC155 Chapter 20.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6710. Compliance schedule.
A. Small municipal waste combustion units shall achieve final compliance or cease operation as expeditiously as practicable but not later than November 6, 2005.
B. The enforceable increments of progress shall be met as follows.
1. If a Class I unit plans to achieve compliance later than January 3, 2004, and a permit modification is not required, or more than one year following the date of issuance of a revised construction or operation permit if a permit modification is required, the Class I unit shall:
a. Submit a final control plan no later than August 6, 2003.
b. Submit a notification of retrofit contract award no later than April 6, 2004.
c. Initiate onsite construction no later than October 6, 2004.
d. Complete onsite construction no later than October 6, 2005.
e. Achieve final compliance no later than November 6, 2005.
2. Class I units that commenced construction after June 26, 1987, shall comply with the dioxins/furans and mercury limits specified in 9VAC5-40-6590 and 9VAC5-40-6650 no later than January 31, 2004, or one year following the issuance of a revised construction or operation permit, if a permit modification is required. Final compliance shall be achieved no later than November 6, 2005, even if the date one year after the issuance of a revised construction or operation permit is later than November 6, 2005.
3. If a Class II unit plans to achieve compliance later than January 31, 2004, and a permit modification is not required, or more than one year following the date of issuance of a revised construction or operation permit if a permit modification is required, the Class II unit shall:
a. Submit a final control plan no later than September 6, 2003.
b. Achieve final compliance no later than May 6, 2005.
C. The following provisions govern municipal waste combustor closure.
1. If a municipal waste combustion unit is closed but will reopen prior to the final compliance date, the increments of progress specified in subdivision B 1 of this section shall be met. If a municipal waste combustion unit is closed but will be restarted after the final compliance date, emission control retrofit shall be completed and emission limits and good combustion practices shall be met on the date the municipal waste combustion unit restarts operation.
2. If a municipal waste combustion unit will be closed rather than comply with this article, the owner shall submit a closure notification, including the date of closure, to the board by August 6, 2003. If the closure date is later than January 31, 2004, the owner shall enter into a legally binding closure agreement with the board by August 6, 2003. The agreement shall specify (i) the date by which operation will cease, which shall be no later than November 6, 2005, and (ii) for Class I units only, dioxin/furan emission test results as specified under 9VAC5-40-6740 B.
D. Notification of achievement of increments of progress shall be prepared and submitted as follows.
1. The notification shall state that the increment of progress has been achieved and shall include any items required to be submitted with the increment of progress listed in subdivision 3 of this subsection. The notification shall be signed by the owner or operator of the municipal waste combustion unit, and shall be postmarked no later than 10 days after the compliance date for the increment.
2. If an increment of progress is not met, the owner shall submit a notification to the board postmarked within 10 business days after the specified date in subsection B of this section for achieving that increment of progress. The notification shall inform the board that the increment was not met, explain why, and include a plan for meeting the increment as expeditiously as possible. Reports shall be submitted each subsequent month until the increment of progress is met.
3. Individual increments of progress shall be reported as follows.
a. For the control plan increment of progress, the owner shall submit the final control plan, including a description of the devices for air pollution control and process changes that will be used to comply with the emission limits and other requirements of this article. An onsite copy of the final control plan shall be maintained.
b. For the awarding contracts increment of progress, the owner shall submit a signed copy of the contracts awarded to initiate onsite construction, initiate onsite installation of emission control equipment, and incorporate process changes. A copy of the contracts shall be included with the notification that the increment of progress has been achieved, exclusive of documents incorporated by reference or attachments to the contracts.
c. For the initiating onsite construction increment of progress, the owner shall initiate onsite construction and installation of emission control equipment and initiate the process changes outlined in the final control plan.
d. For the completing onsite construction increment of progress, the owner shall complete onsite construction and installation of emission control equipment and complete process changes outlined in the final control plan.
e. For the final compliance increment of progress, the owner shall complete all process changes and complete retrofit construction as specified in the final control plan; and connect the air pollution control equipment with the municipal waste combustion unit identified in the final control plan and complete process changes to the municipal waste combustion unit so that if the affected municipal waste combustion unit is brought online, all necessary process changes and air pollution control equipment are operating as designed.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6720. Operating requirements.
A. No owner shall operate any municipal waste combustion unit at loads greater than 110% of the maximum demonstrated load of the municipal waste combustion unit (four-hour block average).
B. The municipal waste combustion unit shall be operated such that the temperature at the inlet of the particulate matter control device does not exceed 17°C above the maximum demonstrated temperature of the particulate matter control device (four-hour block average).
C. If the municipal waste combustion unit uses activated carbon to control dioxins/furans or mercury emissions, an eight-hour block average carbon feed rate at or above the highest average level established during the most recent dioxins/furans or mercury test shall be maintained.
D. If the municipal waste combustion unit uses activated carbon to control dioxins/furans or mercury emissions, the total carbon usage for each calendar quarter shall be evaluated. The total amount of carbon purchased and delivered to the municipal waste combustion plant shall be at or above the required quarterly usage of carbon. The owner may choose to evaluate required quarterly carbon usage on a municipal waste combustion unit basis for each individual municipal waste combustion unit. The quarterly usage of carbon shall be calculated as required in 9VAC5-40-6760 F 1 e (1) and (2).
E. A municipal waste combustion unit is exempt from limits on load level, temperature at the inlet of the particulate matter control device, and carbon feed rate during any of the following.
1. Annual tests for dioxins/furans.
2. Annual mercury tests (for carbon feed rate requirements only).
3. The two weeks preceding annual tests for dioxins/furans.
4. The two weeks preceding annual mercury tests (for carbon feed rate requirements only).
5. Whenever the board allows any of the following.
a. Evaluation of system performance.
b. Testing of new technology or control technologies.
c. Performance of diagnostic testing.
d. Performance of other activities to improve unit performance.
e. Performance of other activities to advance the state of the art for emission controls for the municipal waste combustion unit.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6730. Compliance.
A. The provisions governing compliance shall be as follows:
1. With regard to the emissions standards in 9VAC5-40-6670 A, 9VAC5-40-6680, and 9VAC5-40-6690, the provisions of 9VAC5-40-20 (Compliance) apply.
2. With regard to the emission limits in 9VAC5-40-6570 through 9VAC5-40-6660 and 9VAC5-40-6670 B, the following provisions apply:
a. 9VAC5-40-20 B, C, D, and E;
b. 40 CFR 60.11; and
c. Subsections B through F of this section.
B. After the date the initial emission test and continuous emission monitoring system evaluation are required or completed, whichever is earlier, the owner shall meet the applicable emission limits specified in 9VAC5-40-6570 through 9VAC5-40-6660.
C. Initial and annual emission tests shall be conducted to measure the emission levels of dioxins/furans, cadmium, lead, mercury, particulate matter, opacity, hydrogen chloride, and fugitive ash. The results of emission tests for dioxins/furans, cadmium, lead, mercury, particulate matter, opacity, hydrogen chloride, and fugitive ash shall be used to demonstrate compliance with the applicable emission limits. Compliance for carbon monoxide, nitrogen oxides, and sulfur dioxide shall be demonstrated as provided in subsection E of this section.
D. The owner shall (i) install continuous emission monitoring systems for certain gaseous pollutants, (ii) operate continuous emission monitoring systems correctly, (iii) obtain the minimum amount of monitoring data, and (iv) install a continuous opacity monitoring system.
E. The owner shall use data from the continuous emission monitoring systems for sulfur dioxide, nitrogen oxides, and carbon monoxide in order to demonstrate continuous compliance with the applicable emission limits specified in 9VAC5-40-6610, 9VAC5-40-6620, and 9VAC5-40-6580.
F. Municipal waste combustion unit capacity shall be determined as follows.
1. For a municipal waste combustion unit that can operate continuously for 24-hour periods, the municipal waste combustion unit capacity shall be calculated based on 24 hours of operation at the maximum charge rate. The maximum charge rate shall be determined by one of the following methods.
a. For municipal waste combustion units with a design based on heat input capacity, the maximum charging rate shall be calculated based on the maximum heat input capacity and one of the following heating values:
(1) If the municipal waste combustion unit combusts refuse-derived fuel, a heating value of 12,800 kilojoules per kilogram (5,500 British thermal units per pound) shall be used; or
(2) If the municipal waste combustion unit combusts municipal solid waste, a heating value of 10,500 kilojoules per kilogram (4,500 British thermal units per pound) shall be used.
b. For municipal waste combustion units with a design not based on heat input capacity, the maximum designed charging rate shall be used.
2. Batch municipal waste combustion unit capacity shall be determined by calculating the maximum design amount of municipal solid waste that can be charged per batch multiplied by the maximum number of batches that can be processed in 24 hours. The maximum number of batches shall be calculated by dividing 24 by the number of hours needed to process one batch. Fractional batches shall be retained in the calculation; for example, if one batch requires 16 hours, the municipal waste combustion unit can combust 24/16, or 1.5 batches, in 24 hours.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6740. Test methods and procedures.
A. The provisions governing test methods and procedures shall be as follows:
1. With regard to the emissions standards in 9VAC5-40-6670 A, 9VAC5-40-6680, and 9VAC5-40-6690, the provisions of 9VAC5-40-30 (Emission testing) apply.
2. With regard to the emission limits in 9VAC5-40-6570 through 9VAC5-40-6660 and 9VAC5-40-6670 B, the following provisions apply:
a. 9VAC5-40-30 D and G;
b. 40 CFR 60.8 (b) through (f) with the exception of paragraph (a); and
c. Subsections B through F of this section.
B. Class I units shall submit dioxin/furan emission test results for at least one test conducted during or after 1990. The emission tests shall have been conducted according to the procedures specified under subsection D of this section.
C. Emission testing shall be conducted on the following schedule.
1. Initial emission tests for the pollutants listed in 9VAC5-40-6730 C shall be conducted no later than 180 days after the final compliance date specified in 9VAC5-40-6710 A.
2. Annual emission tests for the pollutants listed in 9VAC5-40-6730 C shall be conducted no later than 13 months after the initial emission test and no later than 13 months after the previous emission test thereafter.
D. Emission testing shall be conducted as follows.
1. Specific testing requirements are as follows.
a. For dioxins/furans: Reference Method 1 shall be used to determine the sampling location. Reference Method 23 shall be used to measure the pollutant concentration; oxygen (or carbon dioxide) shall be measured simultaneously using Reference Method 3A or 3B. The minimum sampling time shall be four hours per test run while the municipal waste combustion unit is operating at full load.
b. For cadmium: Reference Method 1 shall be used to determine the sampling location. Reference Method 29 shall be used to measure the pollutant concentration; oxygen (or carbon dioxide) shall be measured simultaneously using Reference Method 3A or 3B. Compliance testing shall be performed while the municipal waste combustion unit is operating at full load.
c. For lead: Reference Method 1 shall be used to determine the sampling location. Reference Method 29 shall be used to measure the pollutant concentration; oxygen (or carbon dioxide) shall be measured simultaneously using Reference Method 3A or 3B. Compliance testing shall be performed while the municipal waste combustion unit is operating at full load.
d. For mercury: Reference Method 1 shall be used to determine the sampling location. Reference Method 29 shall be used to measure the pollutant concentration; oxygen (or carbon dioxide) shall be measured simultaneously using Reference Method 3A or 3B. Compliance testing shall be performed while the municipal waste combustion unit is operating at full load.
e. For opacity: Reference Method 9 shall be used to determine the sampling location, and Reference Method 9 shall be used to measure the pollutant concentration. Reference Method 9 shall be used to determine compliance with the opacity limits, using a three-hour observation period (30 six-minute averages).
f. For particulate matter: Reference Method 1 shall be used to determine the sampling location, and Reference Method 5 or 29 shall be used to measure the pollutant concentration. The minimum sample probe volume shall be 1.0 cubic meters. The probe and filter holder heating systems in the sampling train shall be set to provide a gas temperature no greater than 160 ± 14°C. The minimum sampling time is one hour.
g. For hydrogen chloride: Reference Method 1 shall be used to determine the sampling location. Reference Method 26 or 26A shall be used to measure the pollutant concentration; oxygen (or carbon dioxide) shall be measured simultaneously using Reference Method 3A or 3B. Test runs shall be at least one hour long while the municipal waste combustion unit is operating at full load.
h. For fugitive ash: No sampling location applies. Reference Method 22 (visible emissions) shall be used to measure the pollutant concentration. The three one-hour observation periods shall include periods when the facility transfers fugitive ash from the municipal waste combustion unit to the area where the fugitive ash is stored or loaded onto containers or trucks.
i. For sulfur dioxide, nitrogen oxide, and carbon monoxide, continuous emission monitoring systems shall be used. Emission tests are not required except for quality assurance requirements in appendix F of 40 CFR Part 60.
2. Emission tests for all pollutants shall consist of at least three test runs as specified in 40 CFR 60.8. The average of the pollutant emission concentrations from the three test runs shall be used to determine compliance with the applicable emission limits.
3. Oxygen (or carbon dioxide) measurements shall be obtained at the same time as the pollutant measurements to determine diluent gas levels, as specified in 9VAC5-40-6750 B.
4. The percent reduction in potential hydrogen chloride emission shall be calculated using the following equation:
%PHCI = (Ei – Eo) * (100/Ei)
where:
%PHCI = percent reduction of the potential hydrogen chloride emissions
Ei = hydrogen chloride emission concentration as measured at the air pollution control device inlet, corrected to 7.0% oxygen, dry basis
Eo = hydrogen chloride emission concentration as measured at the air pollution control device outlet, corrected to 7.0% oxygen, dry basis
5. The reduction efficiency for mercury emissions shall be calculated using the following equation:
Hg = (Ei – Eo)*(100/Ei)
where:
Hg = percent reduction of potential mercury emissions
Ei = mercury emission concentration as measured at the air pollution control device inlet, corrected to 7.0% oxygen, dry basis
Eo = mercury emission concentration as measured at the air pollution control device outlet, corrected to 7.0% oxygen, dry basis
6. The owner may apply to the board for approval under 40 CFR 60.8(b) to use a reference method with minor changes in methodology, use an equivalent method, use an alternative method the results of which the board has determined are adequate for demonstrating compliance, waive the requirement for an emission test because the owner has demonstrated compliance by other means, or use a shorter sampling time or smaller sampling volume.
E. Alternative emission testing schedules may be established as follows.
1. A Class II unit that has conducted emission tests for dioxins/furans, cadmium, lead, mercury, particulate matter, opacity, hydrogen chloride, and fugitive ash over three consecutive years, and has demonstrated compliance with the emission limits is not required to conduct an emission test for that pollutant for the next two years. An emission test shall be conducted within 36 months of the anniversary date of the third consecutive emission test that shows compliance with the emission limit. Thereafter, emission tests shall be performed every third year but no later than 36 months following the previous emission tests. If an emission test shows noncompliance with an emission limit, annual emission tests for that pollutant shall be conducted until all emission tests over three consecutive years show compliance with the emission limit for that pollutant.
2. An alternative test schedule for dioxins/furans emissions may be established if the following criteria are met: (i) the affected facility contains multiple municipal waste combustion units onsite that are subject to this article; and (ii) those municipal waste combustion units have demonstrated levels of dioxins/furans emissions less than or equal to 15 nanograms per dry standard cubic meter (total mass) for Class I units, or 30 nanograms per dry standard cubic meter (total mass) for Class II units, for two consecutive years. If these criteria are met, annual emission tests shall be conducted on only one municipal waste combustion unit per year. emission tests conducted under the provisions of this subdivision shall be conducted as follows.
a. The annual emission test shall be conducted no more than 13 months following an emission test on any municipal waste combustion unit subject to this article. Each year a different municipal waste combustion unit subject to this article shall be tested. All municipal waste combustion units subject to this article shall be tested in a sequence determined by the owner. Once a testing sequence has been determined it shall not be changed without approval of the board.
b. If each annual emission test shows levels of dioxins/furans emissions less than or equal to 15 nanograms per dry standard cubic meter (total mass) for Class I units, or 30 nanograms per dry standard cubic meter (total mass) for Class II units, emission tests may be conducted on only one municipal waste combustion unit subject to this article per year.
c. If any annual emission test indicates levels of dioxins/furans emissions greater than 15 nanograms per dry standard cubic meter (total mass) for Class I units, or 30 nanograms per dry standard cubic meter (total mass) for Class II units, subsequent annual emission tests shall be conducted on all municipal waste combustion units subject to this article. The owner may return to testing one municipal waste combustion unit subject to this article per year if it can demonstrate dioxins/furans emissions levels less than or equal to 15 nanograms per dry standard cubic meter (total mass) for Class I units, or 30 nanograms per dry standard cubic meter (total mass) for Class II units, for all municipal waste combustion units at a stationary source subject to this article for two consecutive years.
F. No owner of an affected facility shall deviate from the 13-month testing schedules specified in 9VAC5-40-6740 C and 9VAC5-40-6740 E 2 a without applying to the board for an alternative schedule, and the board approves the request for alternate scheduling prior to the date on which the owner would otherwise have been required to conduct the next emission test.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6750. Monitoring.
A. The provisions governing monitoring shall be as follows:
1. With regard to the emissions standards in 9VAC5-40-6670 A, 9VAC5-40-6680, and 9VAC5-40-6690, the provisions of 9VAC5-40-40 (Monitoring) apply.
2. With regard to the emission limits in 9VAC5-40-6570 through 9VAC5-40-6660 and 9VAC5-40-6670 B, the following provisions apply:
a. 9VAC5-40-40 A and F;
b. 40 CFR 60.13; and
c. Subsections B through L of this section.
B. Continuous emission monitoring systems for gaseous pollutants shall be installed as follows.
1. Each affected municipal waste combustion unit shall install, calibrate, maintain, and operate continuous emission monitoring systems for oxygen (or carbon dioxide), sulfur dioxide, and carbon monoxide. Class I municipal waste combustion units shall also install, calibrate, maintain, and operate a continuous emission monitoring system for nitrogen oxides. The continuous emission monitoring systems for sulfur dioxide, nitrogen oxides, and oxygen (or carbon dioxide) shall be installed at the outlet of the air pollution control device.
2. Each continuous emission monitoring system shall be installed, evaluated, and operated according to the monitoring requirements in 40 CFR 60.13.
3. The oxygen (or carbon dioxide) concentration shall be monitored at each location where sulfur dioxide and carbon monoxide are monitored. Class I units shall also monitor the oxygen (or carbon dioxide) concentration at the location where nitrogen oxides are monitored.
4. Carbon dioxide may be monitored instead of oxygen as a diluent gas. If carbon dioxide is monitored, then an oxygen monitor is not required and the requirements in 9VAC5-40-6750 F shall be met.
5. If compliance is demonstrated by monitoring the percent reduction of sulfur dioxide, continuous emission monitoring systems for sulfur dioxide and oxygen (or carbon dioxide) shall be installed at the inlet of the air pollution control device.
6. If an alternative sulfur dioxide monitoring method is used, such as parametric monitoring, or if the source cannot monitor emissions at the inlet of the air pollution control device to determine percent reduction, an alternative monitoring method may be used on approval of the board under 40 CFR 60.13(i).
C. Continuous emission monitoring systems shall be operated as follows.
1. Initial, daily, quarterly, and annual evaluations of the continuous emission monitoring systems that measure oxygen (or carbon dioxide), sulfur dioxide, nitrogen oxides (Class I units only), and carbon monoxide shall be conducted.
2. The initial evaluation of the continuous emission monitoring systems shall be completed within 180 days after the final compliance date specified in 9VAC5-40-6710 A.
3. For initial and annual evaluations, data shall be collected concurrently (or within 30 to 60 minutes) using the oxygen (or carbon dioxide) continuous emission monitoring system, the sulfur dioxide, nitrogen oxides, or carbon monoxide continuous emission monitoring systems, as appropriate, using the following test methods:
a. For nitrogen oxides as monitored by Class I units, the pollutant concentration levels shall be validated using Reference Method 7, 7A, 7B, 7C, 7D, or 7E; oxygen (or carbon monoxide) shall be measured using Reference Method 3 or 3A.
b. For sulfur dioxide, the pollutant concentration levels shall be validated using Reference Method 6 or 6C; oxygen (or carbon monoxide) shall be measured using Reference Method 3 or 3A.
c. For carbon monoxide, the pollutant concentration levels shall be validated using Reference Method 10, 10A, or 10B; oxygen (or carbon monoxide) shall be measured using Reference Method 3 or 3A.
4. Data shall be collected during each initial and annual evaluation of the continuous emission monitoring systems as follows.
a. For opacity: the span value shall be 100%, and Performance Specification 1 shall be used. Reference Method 9 shall be used if needed to meet minimum data requirements.
b. For nitrogen oxides as monitored by Class I units: the span value for the control device outlet shall be 125% of the maximum expected hourly potential nitrogen oxides emissions of the municipal waste combustion unit, and Performance Standard 2 shall be used. Reference Method 7E shall be used if needed to meet minimum data requirements.
c. For sulfur dioxide:
(1) For the inlet to the control device: the span value shall be 125% of the maximum expected hourly potential sulfur dioxide emissions of the municipal waste combustion unit, and Performance Standard 2 shall be used. Reference Method 6C shall be used if needed to meet minimum data requirements.
(2) For the control device outlet: the span value shall be 50% of the maximum expected hourly potential sulfur dioxide emissions of the municipal waste combustion unit, and Performance Standard 2 shall be used. Reference Method 6C shall be used if needed to meet minimum data requirements.
d. For carbon monoxide: the span value shall be 125% of the maximum expected hourly potential carbon monoxide emissions of the municipal waste combustion unit, and Performance Specification 4A shall be used. Reference Method 10 with alternative interference trap shall be used if needed to meet minimum data requirements.
e. For oxygen or carbon dioxide: the span value shall be 25% oxygen or 25% carbon dioxide, and Performance Specification 3 shall be used. Reference Method 3A or 3B shall be used if needed to meet minimum data requirements.
5. The quality assurance procedures in Procedure 1 of appendix F of 40 CFR Part 60 shall be followed for each continuous emission monitoring system.
D. The accuracy tests for the sulfur dioxide continuous emission monitoring system require evaluation of the oxygen (or carbon dioxide) continuous emission monitoring system. Therefore, the oxygen (or carbon dioxide) continuous emission monitoring system is exempt from Section 2.3 of Performance Specification 3 in appendix B of 40 CFR Part 60 (relative accuracy requirement) and Section 5.1.1 of appendix F of 40 CFR Part 60 (relative accuracy test audit).
E. The following schedule for evaluating continuous emission monitoring systems shall be met.
1. Annual evaluations of the continuous emission monitoring systems shall be conducted no more than 13 months after the previous evaluation was conducted.
2. Continuous emission monitoring systems shall be evaluated daily and quarterly as specified in appendix F of 40 CFR Part 60.
F. The relationship between oxygen and carbon dioxide shall be established during the initial evaluation of the continuous emission monitoring systems, and may be reestablished during annual evaluations. The relationship shall be established as follows.
1. Reference Method 3A or 3B shall be used to determine oxygen concentration at the location of the carbon dioxide monitor.
2. At least three test runs for oxygen shall be conducted. Each test run shall represent a one-hour average, and sampling shall continue for at least 30 minutes in each hour.
3. The fuel-factor equation in Reference Method 3B shall be used to determine the relationship between oxygen and carbon dioxide.
G. The following monitoring data shall be collected.
1. Where continuous emission monitoring systems are required, one-hour arithmetic averages shall be obtained. The averages for sulfur dioxide, nitrogen oxides (Class I units only), and carbon monoxide shall be in parts per million by dry volume at 7.0% oxygen (or the equivalent carbon dioxide level). The one-hour averages of oxygen (or carbon dioxide) data from the continuous emission monitoring system shall be used to determine the actual oxygen (or carbon dioxide) level and to calculate emissions at 7.0% oxygen (or the equivalent carbon dioxide level).
2. At least two data points per hour shall be obtained in order to calculate a valid one-hour arithmetic average. 40 CFR 60.13(e)(2) requires the continuous emission monitoring systems to complete at least one cycle of operation (sampling, analyzing, and data recording) for each 15-minute period.
3. Valid one-hour averages shall be obtained for 75% of the operating hours per day for 90% of the operating days per calendar quarter. An operating day is any day the unit combusts any municipal solid waste or refuse-derived fuel.
4. Failure to obtain the minimum data required in subdivisions G 1 through 3 of this section constitutes a violation of the data collection requirement regardless of the emission level monitored. In such case the board shall be notified according to 9VAC5-40-6770 B 2 e.
5. If the minimum data required in subdivisions G 1 through 3 of this section is not obtained, the owner shall nevertheless use all valid data from the continuous emission monitoring systems in calculating emission concentrations and percent reductions in accordance with subsection H of this section.
H. One-hour arithmetic averages shall be converted into averaging times and units as follows.
1. Emissions shall be calculated at 7.0% oxygen using the following equation:
C7%=Cunc*(13.9)*(1/(20.9–CO2))
where:
C7% = concentration corrected to 7.0% oxygen.
Cunc = uncorrected pollutant concentration.
CO2 = concentration of oxygen (percent).
2. Reference Method 19 shall be used to calculate the daily geometric average concentrations of sulfur dioxide emissions. Owners monitoring the percent reduction of sulfur dioxide shall use Reference Method 19 to determine the daily geometric average percent reduction of potential sulfur dioxide emissions.
3. Class I units shall use Reference Method 19 to calculate the daily arithmetic average for concentrations of nitrogen oxides.
4. Reference Method 19 shall be used to calculate the four-hour or 24-hour daily block averages (as applicable) for concentrations of carbon monoxide.
I. Operating parameters required for continuous monitoring are as follows.
1. Municipal waste combustion unit load shall be monitored as follows:
a. Municipal waste combustion units that generate steam shall install, calibrate, maintain, and operate a steam flowmeter or a feed water flowmeter as follows.
(1) The measurements of steam (or feed water) shall be continuously measured and recorded in kilograms (or pounds) per hour.
(2) The steam (or feed water) flow shall be calculated in four-hour block averages.
(3) The steam (or feed water) flow rate shall be calculated using the method in "American Society of Mechanical Engineers Power Test Codes: Test Code for Steam Generating Units, Power Test Code 4.1—1964 (R1991)," section 4 (see 9VAC5-20-21).
(4) Nozzles or orifices for flow rate measurements shall be designed, constructed, installed, calibrated, and used following the recommendations in "American Society of Mechanical Engineers Interim Supplement 19.5 on Instruments and Apparatus: Application, Part II of Fluid Meters," 6th Edition (1971), chapter 4 (see 9VAC5-20-21).
(5) Before each dioxins/furans emission test, or at least once a year, all signal conversion elements associated with steam (or feed water) flow measurements shall be calibrated according to the manufacturer's instructions.
b. If the municipal waste combustion units do not generate steam, or if the municipal waste combustion units have shared steam systems and steam load cannot be estimated per unit, the owner shall determine, to the satisfaction of the board, one or more operating parameters that can be used to continuously estimate load level (for example, the feed rate of municipal solid waste or refuse-derived fuel). The selected parameters shall be monitored continuously.
2. The owner shall install, calibrate, maintain, and operate a device to continuously measure the temperature of the flue gas stream at the inlet of each particulate matter control device.
3. Municipal waste combustion units that use activated carbon to control dioxins/furans or mercury emissions shall perform the following.
a. A carbon injection system operating parameter that can be used to calculate carbon feed rate (for example, screw feeder speed) shall be selected.
b. During each dioxins/furans and mercury emission test, the average carbon feed rate in kilograms (or pounds) per hour and the average operating parameter level that correlates to the carbon feed rate shall be determined. A relationship between the operating parameter and the carbon feed rate in order to calculate the carbon feed rate based on the operating parameter level shall be established.
c. The selected operating parameter shall be continuously monitored during all periods when the municipal waste combustion unit is operating and combusting waste, and the eight-hour block average carbon feed rate shall be calculated in kilograms (or pounds) per hour, based on the selected operating parameter. When calculating the eight-hour block average, (i) hours when the municipal waste combustion unit is not operating shall be excluded, and (ii) hours when the municipal waste combustion unit is operating but the carbon feed system is not working correctly shall be included.
4. Continuous parameter monitoring systems shall meet the following requirements.
a. One-hour arithmetic averages shall be obtained for the following parameters:
(1) Load level of the municipal waste combustion unit;
(2) Temperature of the flue gases at the inlet of the particulate matter control device; and
(3) Carbon feed rate if activated carbon is used to control dioxins/furans or mercury emissions.
b. In order to calculate a valid one-hour arithmetic average, at least two data points per hour shall be obtained.
c. Valid one-hour averages shall be obtained for at least 75% of the operating hours per day for 90% of the operating days per calendar quarter. An operating day is any day the unit combusts any municipal solid waste or refuse-derived fuel.
d. If the minimum data required in subdivisions 4 a through c of this subsection are not obtained, the owner is in violation of the data collection requirement, and shall notify the board according to 9VAC5-40-6770 B 2 e.
J. An initial evaluation of the continuous opacity monitoring system shall be completed according to Performance Specification 1 in appendix B of 40 CFR Part 60 no later than 180 days after the final compliance date specified in 9VAC5-40-6710 A. Each annual evaluation of the continuous opacity monitoring system shall be completed no more than 13 months after the previous evaluation. Tests shall be conducted according to Reference Method 9, as specified in 9VAC5-40-6740 D, to determine compliance with the opacity limit in 9VAC5-40-6660. The data obtained from the continuous opacity monitoring system are not used to determine compliance with the opacity limit.
K. Operation of the continuous emission monitoring systems and continuous opacity monitoring system shall use the required span values and applicable performance specifications in 9VAC5-40-6750 C.
L. If any continuous emission monitoring systems are temporarily unavailable to meet the data collection requirements due to systems malfunction or when repairs, calibration checks, or zero and span checks prevent collection of the minimum amount of data, the alternate methods found in 9VAC5-40-6740 D shall be used.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6760. Recordkeeping.
A. The provisions governing recordkeeping shall be as follows:
1. With regard to the emissions standards in 9VAC5-40-6670 A, 9VAC5-40-6680, and 9VAC5-40-6690, the provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
2. With regard to the emission limits in 9VAC5-40-6570 through 9VAC5-40-6660 and 9VAC5-40-6670 B, the following provisions apply:
a. 9VAC5-40-50 F and H;
b. 40 CFR 60.7; and
c. Subsections B through F of this section.
B. All records shall be kept onsite in paper copy or electronic format unless the board approves another format. All records on each municipal waste combustion unit shall be kept for at least five years, and shall be available for submittal to the board or for onsite review by an inspector.
C. The following records for operator training and certification shall be maintained.
1. Records of provisional certifications, including:
a. For the municipal waste combustion plant, names of the chief facility operator, shift supervisors, and control room operators who are provisionally certified by the American Society of Mechanical Engineers, or an equivalent board-approved certification program.
b. Dates of the initial provisional certifications.
c. Documentation showing current provisional certifications.
2. Records of full certifications and licenses, including:
a. For the municipal waste combustion plant, names of the chief facility operator, shift supervisors, and control room operators who are fully certified by the American Society of Mechanical Engineers or an equivalent board-approved program.
b. Dates of initial and renewal of full certifications and licenses.
c. Documentation showing current full certifications and licenses.
3. Records showing completion of the operator training course, including:
a. For the municipal waste combustion plant, names of the chief facility operator, shift supervisors, and control room operators who have completed the EPA municipal waste combustion operator training course or or an equivalent board-approved program.
b. Dates of completion of the operator training course.
c. Documentation showing completion of the operator training course.
4. Records of reviews for plant-specific operating manuals, including:
a. Names of persons who have reviewed the operating manual.
b. Date of the initial review.
c. Dates of subsequent annual reviews.
5. Records of when a certified operator is temporarily offsite, including:
a. If the certified chief facility operator and certified shift supervisor are offsite for more than 12 hours, but for two weeks or less, and no other certified operator is onsite, the dates that the certified chief facility operator and certified shift supervisor were offsite shall be recorded.
b. When all certified chief facility operators and certified shift supervisors are offsite for more than two weeks and no other certified operator is onsite, the following records shall be kept:
(1) The notice that all certified persons are offsite.
(2) The conditions that cause those people to be offsite.
(3) The corrective actions being taken to ensure a certified chief facility operator or certified shift supervisor is onsite.
(4) Copies of the written reports submitted every four weeks that summarize the actions taken to ensure that a certified chief facility operator or certified shift supervisor will be onsite.
6. Records of calendar dates. Include the calendar date on each record.
D. For emission tests required under 9VAC5-40-6730 C, the following records shall be kept.
1. Emission test results for dioxins/furans, cadmium, lead, mercury, opacity, particulate matter, hydrogen chloride, and fugitive ash.
2. Test reports, including supporting calculations that document the results of all emission tests.
3. The maximum demonstrated load of the municipal waste combustion units and maximum temperature at the inlet of the particulate matter control device during all emission tests for dioxins/furans emissions.
4. The calendar date of each record.
E. For continuously monitored pollutants or parameters, the following records shall be maintained.
1. Records of monitoring data, including the following parameters measured using continuous monitoring systems:
a. All six-minute average levels of opacity.
b. All one-hour average concentrations of sulfur dioxide emissions.
c. For Class I units, all one-hour average concentrations of nitrogen oxides emissions.
d. All one-hour average concentrations of carbon monoxide emissions.
e. All one-hour average load levels of the municipal waste combustion unit.
f. All one-hour average flue gas temperatures at the inlet of the particulate matter control device.
2. Records of average concentrations and percent reductions.
a. All 24-hour daily block geometric average concentrations of sulfur dioxide emissions or average percent reductions of sulfur dioxide emissions.
b. For Class I units, all 24-hour daily arithmetic average concentrations of nitrogen oxides emissions.
c. All four-hour block or 24-hour daily block arithmetic average concentrations of carbon monoxide emissions.
d. All four-hour block arithmetic average load levels of the municipal waste combustion unit.
e. All four-hour block arithmetic average flue gas temperatures at the inlet of the particulate matter control device.
3. Records of exceedances, including:
a. Calendar dates whenever any of the pollutant or parameter levels recorded in subdivision 2 of this subsection or the opacity level recorded in subdivision 1 of this subsection did not meet the emission limits or operating levels specified in this article.
b. Reasons why the applicable emission limits or operating levels were exceeded.
c. Corrective actions taken or being taken to meet the emission limits or operating levels.
4. Records of minimum data, including the following:
a. Calendar dates for which the minimum amount of data required under 9VAC5-40-6750 G and I 4 were not collected for the following types of pollutants and parameters:
(1) Sulfur dioxide emissions.
(2) For Class I units, nitrogen oxides emissions.
(3) Carbon monoxide emissions.
(4) Load levels of the municipal waste combustion unit.
(5) Temperatures of the flue gases at the inlet of the particulate matter control device.
b. Reasons why the minimum data were not collected.
c. Corrective actions taken or being taken to obtain the required amount of data.
5. Records of exclusions, including documentation of each time data was excluded from the calculation of averages for any of the following pollutants or parameters and the reasons why the data were excluded:
a. Sulfur dioxide emissions.
b. For Class I units, nitrogen oxides emissions.
c. Carbon monoxide emissions.
d. Load levels of the municipal waste combustion unit.
e. Temperatures of the flue gases at the inlet of the particulate matter control device.
6. Records of drift and accuracy, including documentation of the results of daily drift tests and quarterly accuracy determinations according to procedure 1 of appendix F of 40 CFR Part 60, for the sulfur dioxide, nitrogen oxides (Class I units only), and carbon monoxide continuous emissions monitoring systems.
7. Records of the relationship between oxygen and carbon dioxide. If carbon dioxide is monitored instead of oxygen as a diluent gas, document the relationship between oxygen and carbon dioxide, as specified in 9VAC5-40-6750 F.
8. Records of calendar dates shall be included on each record.
F. Municipal waste combustion units that use activated carbon to control dioxins/furans or mercury emissions shall maintain the following records.
1. Records of average carbon feed rate, including documentation of the following:
a. Average carbon feed rate in kilograms (or pounds) per hour during all emission tests for dioxins/furans and mercury emissions, with supporting calculations.
b. For the operating parameter chosen to monitor carbon feed rate, average operating level during all emission tests for dioxins/furans and mercury emissions. Supporting data that document the relationship between the operating parameter and the carbon feed rate shall be included in the records.
c. All eight-hour block average carbon feed rates in kilograms (or pounds) per hour calculated from the monitored operating parameter.
d. Total carbon purchased and delivered to the municipal waste combustion plant for each calendar quarter. If the total carbon purchased and delivered is evaluated on a municipal waste combustion unit basis, the total carbon purchased and delivered for each individual municipal waste combustion unit shall be recorded. Supporting documentation shall be included in the records.
e. Required quarterly usage of carbon for the municipal waste combustion plant. If the required quarterly usage for carbon is evaluated on a municipal waste combustion unit basis, the required quarterly usage for each municipal waste combustion unit shall be recorded. Supporting calculations shall be included in the records.
(1) The following equation shall be used for calculation on a plant basis:
where:
C = required quarterly carbon usage for the plant in kilograms (or pounds).
fi = required carbon feed rate for the municipal waste combustion unit in kilograms (or pounds) per hour. That is, the average carbon feed rate during the most recent mercury or dioxins/furans emission tests (whichever has a higher feed rate).
hi = number of hours the municipal waste combustion unit was in operation during the calendar quarter (hours).
n = number of municipal waste combustion units, i, located at the plant.
(2) The following equation shall be used for calculation on a unit basis:
C=f*h
where:
C = required quarterly carbon usage for the unit in kilograms (or pounds).
f = required carbon feed rate for the municipal waste combustion unit in kilograms (or pounds) per hour. That is, the average carbon feed rate during the most recent mercury or dioxins/furans emission tests (whichever has a higher feed rate).
h = number of hours the municipal waste combustion unit was in operation during the calendar quarter (hours).
2. Records of low carbon feed rates, including the following:
a. The calendar dates when the average carbon feed rate over an eight-hour block was less than the average carbon feed rates determined during the most recent emission test for dioxins/furans or mercury emissions (whichever has a higher feed rate).
b. Reasons for the low carbon feed rates.
c. Corrective actions taken or being taken to meet the eight-hour average carbon feed rate requirement.
3. Records of minimum carbon feed rate data, including the following:
a. Calendar dates for which the minimum amount of carbon feed rate data required under 9VAC5-40-6750 I 4 were not collected.
b. Reasons why the minimum data was not collected.
c. Corrective actions taken or being taken to obtain the required amount of data.
4. Records of exclusions, including documentation of each time data were excluded from the calculation of average carbon feed rates and the reasons why.
5. Records of calendar dates, including the calendar date on each record.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6770. Reporting.
A. The provisions governing reporting shall be as follows:
1. With regard to the emissions standards in 9VAC5-40-6670 A, 9VAC5-40-6680, and 9VAC5-40-6690, the provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
2. With regard to the emission limits in 9VAC5-40-6570 through 9VAC5-40-6660 and 9VAC5-40-6670 B, the following provisions apply:
a. 9VAC5-40-50 F and H;
b. 40 CFR 60.7; and
c. Subsections B and C of this section.
B. The owner of an affected facility shall submit (i) an initial report; (ii) annual reports; and (iii) semiannual reports for any emission or parameter level that does not meet the provisions of this article, as described in subdivisions B 1 through 3 of this subsection. All reports shall be submitted on paper, postmarked on or before the submittal dates in subdivisions B 1 through 3. Electronic reports may be submitted with the board's prior approval. All reports required by subdivisions B 1 a, 2, and 3 shall be maintained onsite for five years.
1. As specified in 40 CFR 60.7(c), the initial report shall be submitted no later than 180 days after the final compliance date specified in 9VAC5-40-6710 A. The initial report shall include the following:
a. The emission levels measured on the date of the initial evaluation of the continuous emission monitoring systems for all of the following pollutants or parameters as recorded in accordance with 9VAC5-40-6760 E 2:
(1) The 24-hour daily geometric average concentration of sulfur dioxide emissions or the 24-hour daily geometric percent reduction of sulfur dioxide emissions.
(2) For Class I units, the 24-hour daily arithmetic average concentration of nitrogen oxides emissions.
(3) The four-hour block or 24-hour daily arithmetic average concentration of carbon monoxide emissions.
(4) The four-hour block arithmetic average load level of the municipal waste combustion unit.
(5) The four-hour block arithmetic average flue gas temperature at the inlet of the particulate matter control device.
b. The results of the initial emission tests as required by 9VAC5-40-6730 C and recorded in 9VAC5-40-6760 D.
c. The test report that documents the initial emission tests, including supporting calculations.
d. The initial performance evaluation of the continuous emissions monitoring systems, using the applicable performance specifications in appendix B of 40 CFR Part 60 to conduct the evaluation.
e. The maximum demonstrated load of the municipal waste combustion unit and the maximum demonstrated temperature of the flue gases at the inlet of the particulate matter control device, using values established during the initial emission test for dioxins/furans emissions, and including supporting calculations.
f. If activated carbon is used to control dioxins/furans or mercury emissions, the average carbon feed rates recorded during the initial emission tests for dioxins/furans and mercury emissions, including supporting calculations as specified in 9VAC5-40-6760 F 1 a and b.
g. If carbon dioxide is monitored instead of oxygen as a diluent gas, the relationship between oxygen and carbon dioxide as specified in 9VAC5-40-6750 F.
2. The annual report shall be submitted no later than February 1 of each year that follows the calendar year in which the data is collected. If the facility has a federal operating permit for any unit, the permit may require submittal of semiannual reports. The annual report shall summarize data collected for all pollutants and parameters regulated under this article, and shall include:
a. The results of the annual emission test as required by 9VAC5-40-6730 C and as recorded under 9VAC5-40-6760 D 1.
b. A list of the highest average levels recorded, in the appropriate units, for the following pollutants and parameters:
(1) Sulfur dioxide emissions.
(2) For Class I units, nitrogen oxides emissions.
(3) Carbon monoxide emissions.
(4) Load level of the municipal waste combustion unit.
(5) Temperature of the flue gases at the inlet of the particulate matter air pollution control device (four-hour block average).
c. The highest six-minute opacity level measured. The value shall be based on all six-minute average opacity levels recorded by the continuous opacity monitoring system as required by 9VAC5-40-6760 E 1 a.
d. For municipal waste combustion units that use activated carbon for controlling dioxins/furans or mercury emissions, the following records shall be included:
(1) The average carbon feed rates recorded during the most recent dioxins/furans and mercury emission tests.
(2) The lowest eight-hour block average carbon feed rate recorded during the year.
(3) The total carbon purchased and delivered to the municipal waste combustion plant for each calendar quarter. If the total carbon purchased and delivered is evaluated on a municipal waste combustion unit basis, the total carbon purchased and delivered for each individual municipal waste combustion unit shall be recorded.
(4) The required quarterly carbon usage of the municipal waste combustion plant calculated using the equations in 9VAC5-40-6760 F 1 e (1) and (2). If the required quarterly usage for carbon is evaluated on a municipal waste combustion unit basis, the required quarterly usage for each municipal waste combustion unit shall be recorded.
e. The total number of days the minimum number of hours of data for the following pollutants or parameters were not obtained, including the reasons why data were not obtained and corrective actions taken to obtain the data in the future:
(1) Sulfur dioxide emissions.
(2) For Class I units, nitrogen oxides emissions.
(3) Carbon monoxide emissions.
(4) Load level of the municipal waste combustion unit.
(5) Temperature of the flue gases at the inlet of the particulate matter air pollution control device.
(6) Carbon feed rate.
f. The number of hours data have been excluded from the calculation of average levels (include the reasons for excluding it), for the following pollutants and parameters:
(1) Sulfur dioxide emissions.
(2) For Class I units, nitrogen oxides emissions.
(3) Carbon monoxide emissions.
(4) Load level of the municipal waste combustion unit.
(5) Temperature of the flue gases at the inlet of the particulate matter air pollution control device.
(6) Carbon feed rate.
g. A notice of intent to begin a reduced emission testing schedule for dioxins/furans emissions during the following calendar year if the facility is eligible for alternative scheduling as provided in 9VAC5-40-6740 E 1 or 2.
h. A notice of intent to begin a reduced emission testing schedule for other pollutants during the following calendar year if the facility is eligible for alternative scheduling as provided in 9VAC5-40-6740 E 1.
i. A summary of any emission or parameter level that did not meet the limits specified in this article.
j. A summary of the data in subdivisions B 2 a through d of this section from the year preceding the reporting year, which gives the board a summary of the performance of the municipal waste combustion unit over a two-year period.
k. If carbon dioxide is monitored instead of oxygen as a diluent gas, documentation of the relationship between oxygen and carbon dioxide, as specified in 9VAC5-40-6750 F.
l. Documentation of periods when all certified chief facility operators and certified shift supervisors are offsite for more than 12 hours.
3. A semiannual report on any recorded emission or parameter level that does not meet the requirements specified in this article shall be submitted. For data collected during the first half of a calendar year, the report shall be submitted by August 1 of that year. For data collected during the second half of the calendar year, the report shall be submitted by February 1 of the following year. The following information shall be included:
a. For any of the following pollutants and parameters that exceeded the limits specified in this article, the calendar date they exceeded the limits, the averaged and recorded data for that date, the reasons for exceeding the limits, and corrective actions taken:
(1) Concentration or percent reduction of sulfur dioxide emissions.
(2) For Class I units, concentration of nitrogen oxides emissions.
(3) Concentration of carbon monoxide emissions.
(4) Load level of the municipal waste combustion unit.
(5) Temperature of the flue gases at the inlet of the particulate matter air pollution control device.
(6) Average six-minute opacity level. The data obtained from the continuous opacity monitoring system are not used to determine compliance with the limit on opacity emissions.
b. If the results of the annual emission tests (as recorded in 9VAC5-40-6760 D 1) show emissions above the limits for dioxins/furans, cadmium, lead, mercury, particulate matter, opacity, hydrogen chloride, and fugitive ash, a copy of the test report that documents the emission levels and corrective actions taken shall be included.
c. Municipal waste combustion units that apply activated carbon to control dioxins/furans or mercury emissions shall include the following.
(1) Documentation of all dates when the eight-hour block average carbon feed rate (calculated from the carbon injection system operating parameter) is less than the highest carbon feed rate established during the most recent mercury and dioxins/furans emission test, as specified in 9VAC5-40-6760 F 1 a, including (i) eight-hour average carbon feed rate, (ii) reasons for occurrences of low carbon feed rates, (iii) corrective actions taken to meet the carbon feed rate requirement, and (iv) the calendar date.
(2) Documentation of each quarter when total carbon purchased and delivered to the municipal waste combustion plant is less than the total required quarterly usage of carbon. If the total carbon purchased and delivered is evaluated on a municipal waste combustion unit basis, the total carbon purchased and delivered for each individual municipal waste combustion unit shall be recorded. The following information shall be included: (i) amount of carbon purchased and delivered to the plant, (ii) required quarterly usage of carbon, (iii) reasons for not meeting the required quarterly usage of carbon, (iv) corrective actions taken to meet the required quarterly usage of carbon, and (v) the calendar date.
C. Changes to semiannual or annual reporting dates may be pursued in accordance with the procedures of 40 CFR 60.19(c), and with the approval of the board.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6780. Requirements for air curtain incinerators that burn 100% yard waste.
A. The owner of an air curtain incinerator subject to the provisions of this article shall meet the following opacity requirements no later than 180 days after the final compliance date specified in 9VAC5-40-6710 A.
1. The opacity limit is 10% (six-minute average) for air curtain incinerators that can combust at least 35 tons per day of municipal solid waste and no more than 250 tons per day of municipal solid waste.
2. The opacity limit is 35% (six-minute average) during the startup period that is within the first 30 minutes of operation.
3. Except during malfunctions, the requirements of this article apply at all times. Each malfunction shall not exceed three hours.
4. Compliance with the opacity limit shall be achieved as follows.
a. Reference Method 9 shall be used to determine compliance with the opacity limit.
b. An initial test for opacity as specified in 40 CFR 60.8 shall be conducted no later than 180 days after the final compliance date specified in 9VAC5-40-6710 A.
c. After the initial test for opacity, annual tests shall be conducted no more than 13 calendar months following the date of the previous test.
B. The owner of an air curtain incinerator subject to the provisions of this article shall meet the following recordkeeping and reporting requirements.
1. A notice of construction shall be provided that includes the following:
a. The intent to construct the air curtain incinerator.
b. The planned initial startup date.
c. Types of fuels planned to combust.
d. Incinerator capacity, including supporting capacity calculations, as specified in 9VAC5-40-6730 F.
2. Records of results of all opacity tests shall be maintained onsite in either paper copy or electronic format unless the board approves another format.
3. All records for each incinerator shall be maintained for at least five years.
4. All records shall be available to the board or for onsite review by an inspector.
5. The results (each six-minute average) of the opacity tests shall be submitted no later than February 1 of the year following the year of the opacity emission test.
6. Reports shall be submitted as a paper copy on or before the applicable submittal date. Reports may be submitted on electronic media with prior approval of the board.
7. Annual reporting dates may be revised with the prior approval of the board (see 40 CFR 60.19(c)).
8. All reports shall be maintained onsite for a period of five years.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6790. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6800. Facility and control equipment maintenance or malfunction.
A. The provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply to the emission standards set forth in 9VAC5-40-6670 A, 9VAC5-40-6680, and 9VAC5-40-6690.
B. The provisions of 9VAC5-20-180 A, B, C, D, H, and I and subsections C through E of this section apply to the emission limits in 9VAC5-40-6530 through 9VAC5-40-6660 and 9VAC5-40-6670 B.
C. The emission limitations and operating limits apply at all times except during periods of municipal waste combustion unit startup, shutdown, or malfunction. No startup, shutdown, or malfunction shall last for longer than three hours. This subsection shall not apply to the emission standards set forth in 9VAC5-40-6670 A, 9VAC5-40-6680, and 9VAC5-40-6690.
D. A maximum of three hours of test data may be dismissed from compliance calculations during periods of startup, shutdown, or malfunction.
E. During startup, shutdown, or malfunction periods longer than three hours, emissions data shall not be discarded from compliance calculations, and all provisions under 40 CFR 60.11(d) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
9VAC5-40-6810. Permits.
A permit may be required prior to beginning any of the activities specified below if the provisions of 9VAC5-50 and 9VAC5-80 apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 19, Issue 24, eff. September 10, 2003.
Article 47
Emission Standards for Solvent Metal Cleaning Operations in the Northern Virginia Volatile Organic Compound Emissions Control Area (Rule 4-47)
9VAC5-40-6820. Applicability and designation of affected facility.
Article 47
Emission Standards for Solvent Metal Cleaning Operations in the Northern Virginia Volatile Organic Compound Emissions Control Area (Rule 4-47)
A. The affected facility to which the provisions of this article apply is each solvent metal cleaning operation, including, but not limited to, cold or vapor degreasing at service stations; motor vehicle repair shops; automobile dealerships; machine shops; and any other metal refinishing, cleaning, repair, or fabrication facility. Certain provisions of this article also apply to sellers of solvents for use in a cold cleaning machine.
B. The provisions of this article apply only to sources and persons in the Northern Virginia volatile organic compounds emissions control area designated in 9VAC5-20-206.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-6830. Definitions.
A. For the purpose of applying this article in the context of the Regulations for the Control and Abatement of Air Pollution and related uses, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined herein shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10), unless otherwise required by context.
C. Terms defined.
"Airless cleaning system" means a solvent cleaning machine that is automatically operated and seals at a differential pressure of 0.50 pounds per square inch gauge (psig) or less, prior to the introduction of solvent or solvent vapor into the cleaning chamber and maintains differential pressure under vacuum during all cleaning and drying cycles.
"Air-tight cleaning system" means a solvent cleaning machine that is automatically operated and seals at a differential pressure no greater than 0.50 psig, prior to the introduction of solvent or solvent vapor into the cleaning chamber and during all cleaning and drying cycles.
"Batch vapor cleaning machine" means a vapor cleaning machine in which individual parts or a set of parts move through the entire cleaning cycle before new parts are introduced into the cleaning machine. The term includes solvent cleaning machines, such as ferris wheel cleaners or cross rod machines, that clean multiple loads simultaneously and are manually loaded. The term does not include machines that do not have a solvent/air interface, such as airless and air-tight cleaning systems.
"Carbon adsorber" means a bed of activated carbon into which an air/solvent gas-vapor stream is routed and which adsorbs the solvent on the carbon.
"Cold cleaning machine" means a device or piece of equipment, containing or using an unheated liquid that contains greater than 5.0% volatile organic compound or 5.0% hazardous air pollutant (HAP) by weight, where parts are placed to remove dirt, grease, oil or other contaminants and coatings, from the surfaces of the parts or to dry the parts. The term does not include machines that do not have a solvent/air interface, such as airless and air-tight cleaning systems.
"Dwell" means holding parts within the freeboard area of a solvent cleaning machine but above the solvent vapor zone. Dwell occurs after cleaning to allow solvent to drain from the parts or parts baskets back into the solvent cleaning machine.
"Dwell time" means the period of time between when a parts basket is placed in the vapor zone of a batch vapor or in-line vapor cleaning machine and when solvent dripping ceases. Dwell time is determined by placing a basket of parts in the vapor zone and measuring the amount of time between when the parts are placed in the vapor zone and dripping ceases.
"Freeboard ratio" means for a cold cleaning machine, the distance from the liquid solvent to the top edge of the cold cleaning machine divided by the width of the cold cleaning machine; for an operating batch vapor cleaning machine or an in-line vapor cleaning machine, the distance from the top of the solvent vapor layer to the top edge of the vapor cleaning machine divided by the width of the vapor cleaning machine.
"Freeboard refrigeration device" means a set of secondary coils mounted in the freeboard area of a solvent cleaning machine that carries a refrigerant or other chilled substance to provide a chilled air blanket above the solvent vapor. A solvent cleaning machine primary condenser that is capable of maintaining a temperature in the center of the chilled air blanket at not more than 30% of the solvent boiling point is both a primary condenser and a freeboard refrigeration device.
"Immersion cold cleaning machine" means a cold cleaning machine in which the parts are immersed in the solvent when being cleaned.
"In-line vapor cleaning machine" means a vapor cleaning machine that uses an automated parts handling system, typically a conveyor, to automatically provide a supply of parts to be cleaned. In-line vapor cleaning machines are fully enclosed except for the conveyor inlet and exit portals.
"Reduced room draft" means decreasing the flow or movement of air across the top of the freeboard area of a solvent cleaning machine to less than 50 feet per minute (15.2 meters per minute) by methods including redirecting fans or air vents, moving a machine to a corner where there is less room draft, or constructing a partial or complete enclosure.
"Remote reservoir cold cleaning machine" means a machine in which liquid solvent is pumped to a sink-like work area that immediately drains solvent back into an enclosed container while parts are being cleaned, allowing no solvent to pool in the work area.
"Solvent/air interface" means the location of contact between the concentrated solvent vapor layer and the air. This location of contact is defined as the midline height of the primary condenser coils. For a cold cleaning machine, it is the location of contact between the liquid solvent and the air.
"Solvent cleaning machine" means a device or piece of equipment that uses solvent liquid or vapor to remove contaminants, such as dirt, grease, oil, and coatings, from the surfaces of materials. Types of solvent cleaning machines include batch vapor cleaning machines, in-line vapor cleaning machines, immersion cold cleaning machines, remote reservoir cold cleaning machines, airless cleaning systems and air-tight cleaning systems.
"Solvent cleaning machine automated parts handling system" means a mechanical device that carries all parts and parts baskets at a controlled speed from the initial loading of soiled or wet parts through the removal of the cleaned or dried parts.
"Solvent cleaning machine down time" means the period when a solvent cleaning machine is not cleaning parts and the sump heating coils, if present, are turned off.
"Solvent cleaning machine idle time" means the period when a solvent cleaning machine is not actively cleaning parts and the sump heating coil, if present, is turned on.
"Solvent metal cleaning operation" means the process of cleaning foreign matter from metal surfaces by using solvents, including, but not limited to, cold cleaning machines that process metal parts and contain more than one liter of volatile organic compounds; batch vapor cleaning machines that process metal parts; in-line vapor cleaning machines; and airless cleaning machines and air-tight cleaning machines that process metal parts.
"Superheated vapor system" means a system that heats the solvent vapor to a temperature 10 degrees Farenheit above the solvent's boiling point. Parts are held in the superheated vapor before exiting the machine to evaporate the liquid solvent on the parts.
"Vapor cleaning machine" means a solvent cleaning machine that boils liquid solvent, generating a vapor, or that heats liquid solvent that is used as part of the cleaning or drying cycle. The term does not include machines that do not have a solvent/air interface, such as airless and air-tight cleaning systems.
"Vapor cleaning machine primary condenser" means a series of circumferential cooling coils on a vapor cleaning machine through which a chilled substance is circulated or recirculated to provide continuous condensation of rising solvent vapors, and thereby, create a concentrated vapor zone.
"Vapor up control switch" means a thermostatically controlled switch that shuts off or prevents condensate from being sprayed when there is no vapor. On in-line vapor cleaning machines the switch also prevents the conveyor from operating when there is no vapor.
"Working mode cover" means any cover or solvent cleaning machine design that allows the cover to shield the cleaning machine openings from outside air disturbances while parts are being cleaned in the cleaning machine. A cover that is used during the working mode is opened only during parts entry and removal.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-6840. Standard for volatile organic compounds.
A. No owner or other person shall use or permit the use of a cold cleaning machine that processes metal parts and contains more than one liter of volatile organic compounds unless the machine complies with this article. The board may make an exception if the owner demonstrates and the board approves in writing that compliance with the article will result in unsafe operating conditions.
1. Immersion cold cleaning machines shall have a freeboard ratio of 0.75 or greater unless the machines are equipped with covers that are kept closed except when parts are being placed into or being removed from the machine.
2. Immersion cold cleaning machines and remote reservoir cold cleaning machines shall:
a. Have a permanent, conspicuous label summarizing the operating requirements in subdivision 3 of this subsection.
b. Be equipped with a cover that shall be closed at all times except during cleaning of parts or the addition or removal of solvent. For remote reservoir cold cleaning machines that drain directly into the solvent storage reservoir, a perforated drain with a diameter of not more than six inches shall constitute an acceptable cover.
3. Cold cleaning machines shall be operated in accordance with the following procedures:
a. Waste solvent shall be collected and stored in closed containers. The closed containers may contain a device that allows pressure relief, but does not allow liquid solvent to drain from the container.
b. Cleaned parts shall be drained at least 15 seconds or until dripping ceases, whichever is longer. Parts having cavities or blind holes shall be tipped or rotated while the part is draining. During the draining, tipping or rotating, the parts shall be positioned so that solvent drains directly back to the cold cleaning machine.
c. Flushing of parts using a flexible hose or other flushing device shall be performed only within the freeboard area of the cold cleaning machine. The solvent spray shall be a solid fluid stream, not an atomized or shower spray.
d. The owner shall ensure that when the cover is open the cold cleaning machine is not exposed to drafts greater than 40 meters per minute (132 feet per minute), as measured between 1 and 2 meters (3.3 and 6.6 feet) upwind and at the same elevation as the tank lip.
e. Sponges, fabric, wood, leather, paper products and other absorbent materials shall not be cleaned in the cold cleaning machine.
f. When a pump-agitated solvent bath is used, the agitator shall be operated to produce a rolling motion of the solvent with no observable splashing of the solvent against the tank walls or the parts being cleaned. Air agitated solvent baths may not be used.
g. Spills during solvent transfer and use of the cold cleaning machine shall be cleaned up immediately, and the wipe rags or other sorbent material shall be immediately stored in covered containers for disposal or recycling.
h. Work area fans shall be located and positioned so that they do not blow across the opening of the degreaser unit.
i. The owner shall ensure that the solvent level does not exceed the fill line.
4. No person shall use, sell, or offer for sale for use in a cold cleaning machine any solvent with a vapor pressure of 1.0 millimeters of mercury (mm Hg) or greater, measured at 20 degrees Centigrade (68 degrees Fahrenheit containing volatile organic compounds.
5. Any person who sells or offers for sale any solvent containing volatile organic compounds for use in a cold cleaning machine shall provide to the purchaser the following written information:
a. The name and address of the solvent supplier.
b. The type of solvent including the product or vendor identification number.
c. The vapor pressure of the solvent measured in mm Hg at 20 degrees Centigrade (68 degrees Fahrenheit.
6. A person who operates a cold cleaning machine shall maintain for not less than two years and shall provide to the board, on request, the information specified in subdivision A 5 of this section. An invoice, bill of sale, certificate that corresponds to a number of sales, Material Safety Data Sheet (MSDS), or other appropriate documentation acceptable to the board may be used to comply with this section.
B. No owner or other person shall use or permit the use of a batch vapor cleaning machine that processes metal parts unless the machine complies with this article.
1. Batch vapor cleaning machines shall be equipped with:
a. Either a fully enclosed design or a working and downtime mode cover that completely covers the cleaning machine openings when in place, is free of cracks, holes and other defects, and can be readily opened or closed without disturbing the vapor zone. If the solvent cleaning machine opening is greater than 10 square feet, the cover shall be powered. If a lip exhaust is used, the closed cover shall be below the level of the lip exhaust.
b. Sides that result in a freeboard ratio greater than or equal to 0.75.
c. A safety switch (thermostat and condenser flow switch) that shuts off the sump heat if the coolant is not circulating.
d. A vapor up control switch that shuts off the spray pump if vapor is not present.
e. An automated parts handling system that moves the parts or parts baskets at a speed of 11 feet (3.4 meters) per minute or less when the parts are entering or exiting the vapor zone. If the parts basket or parts being cleaned occupy more than 50% of the solvent/air interface area, the speed of the parts basket or parts shall not exceed three feet per minute.
f. A device that shuts off the sump heat if the sump liquid solvent level drops to the sump heater coils.
g. A vapor level control device that shuts off the sump heat if the vapor level in the vapor cleaning machine rises above the height of the primary condenser.
h. Each vapor cleaning machine shall have a primary condenser.
i. Each vapor cleaning machine that uses a lip exhaust shall be designed and operated to route all collected solvent vapors through a properly operated and maintained carbon adsorber such that the concentration of organic solvent in the exhaust does not exceed 100 parts per million.
j. A permanent, conspicuous label summarizing the operating requirements found in subdivision B 4 of this section.
2. In addition to the requirements of subdivision B 1 of this section, the owner of a batch vapor cleaning machine with a solvent/air interface area of 13 square feet or less shall implement one of the following options:
a. A working mode cover, freeboard ratio of 1.0, and superheated vapor.
b. A freeboard refrigeration device operated to ensure that the chilled air blanket temperature is no greater than 30% of the solvent's boiling point and superheated vapor.
c. A working mode cover and a freeboard refrigeration device operated to ensure that the chilled air blanket temperature is no greater than 30% of the solvent's boiling point.
d. Reduced room draft, freeboard ratio of 1.0 and superheated vapor;
e. A freeboard refrigeration device operated to ensure that the chilled air blanket temperature is no greater than 30% of the solvent's boiling point and reduced room draft.
f. A freeboard refrigeration device operated to ensure that the chilled air blanket temperature is no greater than 30% of the solvent's boiling point and a freeboard ratio of 1.0.
g. A freeboard refrigeration device operated to ensure that the chilled air blanket temperature is no greater than 30% of the solvent's boiling point and dwell. Dwell shall be not less than 35% of the dwell time determined for the part or parts.
h. Reduced room draft, dwell and a freeboard ratio of 1.0.
i. A freeboard refrigeration device operated to ensure that the chilled air blanket temperature is no greater than 30% of the solvent's boiling point and a carbon adsorber that reduces solvent emissions in the exhaust to a level not to exceed 100 ppm at any time.
j. A freeboard ratio of 1.0, superheated vapor and a carbon adsorber that reduces solvent emissions in the exhaust to a level not to exceed 100 ppm at any time.
3. In addition to the requirements of subdivision B 1 of this section, the owner of a batch vapor cleaning machine with a solvent/air interface area of greater than 13 square feet shall use one of the following devices or strategies:
a. A freeboard refrigeration device operated to ensure that the chilled air blanket temperature is no greater than 30% of the solvent's boiling point, a freeboard ratio of 1.0 and superheated vapor.
b. Dwell, a freeboard refrigeration device operated to ensure that the chilled air blanket temperature is no greater than 30% of the solvent's boiling point, and reduced room draft. Dwell shall be not less than 35% of the dwell time determined for the part or parts.
c. A working mode cover and a freeboard refrigeration device operated to ensure that the chilled air blanket temperature is no greater than 30%6c; of the solvent's boiling point and superheated vapor.
d. Reduced room draft, freeboard ratio of 1.0 and superheated vapor.
e. A freeboard refrigeration device operated to ensure that the chilled air blanket temperature is no greater than 30% of the solvent's boiling point, reduced room draft and superheated vapor.
f. A freeboard refrigeration device operated to ensure that the chilled air blanket temperature is no greater than 30% of the solvent's boiling point, reduced room draft and a freeboard ratio of 1.0.
g. A freeboard refrigeration device operated to ensure that the chilled air blanket temperature is no greater than 30% of the solvent's boiling point, superheated vapor, and a carbon adsorber which reduces solvent emissions in the exhaust to a level not to exceed 100 ppm at any time.
4. Batch vapor cleaning machines shall be operated in accordance with the following procedures:
a. Waste solvent, still bottoms and sump bottoms shall be collected and stored in closed containers. The closed containers may contain a device that allows pressure relief, but does not allow liquid solvent to drain from the container.
b. Cleaned parts shall be drained at least 15 seconds or until dripping ceases, whichever is longer. Parts having cavities or blind holes shall be tipped or rotated while the part is draining. A superheated vapor system shall be an acceptable alternate technology.
c. Parts baskets or parts shall not be removed from the batch vapor cleaning machine until dripping has ceased.
d. Flushing or spraying of parts using a flexible hose or other flushing device shall be performed within the vapor zone of the batch vapor cleaning machine or within a section of the machine that is not exposed to the ambient air. The solvent spray shall be a solid fluid stream, not an atomized or shower spray.
e. When the cover is open, the batch vapor cleaning machine shall not be exposed to drafts greater than 40 meters per minute (132 feet per minute), as measured between 1 and 2 meters (3.3 and 6.6 feet) upwind and at the same elevation as the tank lip.
f. Sponges, fabric, wood, leather, paper products and other absorbent materials shall not be cleaned in the batch vapor cleaning machine.
g. Spills during solvent transfer and use of the batch vapor cleaning machine shall be cleaned up immediately or the machine shall be shut down. Wipe rags or other sorbent material shall be immediately stored in covered containers for disposal or recycling.
h. Work area fans shall be located and positioned so that they do not blow across the opening of the batch vapor cleaning machine.
i. During startup of the batch vapor cleaning machine, the primary condenser shall be turned on before the sump heater.
j. During shutdown of the batch vapor cleaning machine, the sump heater shall be turned off and the solvent vapor layer allowed to collapse before the primary condenser is turned off.
k. When solvent is added to or drained from the batch vapor cleaning machine, the solvent shall be transferred using threaded or other leakproof couplings and the end of the pipe in the solvent sump shall be located beneath the liquid solvent surface.
l. The working and downtime covers shall be closed at all times except during parts entry and exit from the machine, during maintenance of the machine when the solvent has been removed, and during addition of solvent to the machine.
m. If a lip exhaust is used on the open top vapor degreaser, the ventilation rate shall not exceed 20 m³/min/m² (65 ft³/min/ft²) of degreaser open area, unless a higher rate is necessary to meet OSHA requirements.
C. No owner or other person shall use or permit the use of an in-line vapor cleaning machine unless the machine complies with this article.
1. In-line vapor cleaning machines shall be equipped with:
a. Either a fully enclosed design or a working and downtime mode cover that completely covers the cleaning machine openings when in place, is free of cracks, holes and other defects, and can be readily opened or closed without disturbing the vapor zone.
b. A switch (thermostat and condenser flow switch) that shuts off the sump heat if the coolant is not circulating.
c. Sides that result in a freeboard ratio greater than or equal to 0.75.
d. A vapor up control switch.
e. An automated parts handling system that moves the parts or parts baskets at a speed of 11 feet (3.4 meters) per minute or less when the parts are entering or exiting the vapor zone. If the parts basket or parts being cleaned occupy more than 50% of the solvent/air interface area, the speed of the parts basket or parts shall not exceed three feet per minute.
f. A device that shuts off the sump heat if the sump liquid solvent level drops to the sump heater coils.
g. A vapor level control device that shuts off the sump heat if the vapor level in the vapor cleaning machine rises above the height of the primary condenser.
h. A permanent, conspicuous label summarizing these operating requirements.
i. A primary condenser.
j. Each machine that uses a lip exhaust shall be designed and operated to route all collected solvent vapors through a properly operated and maintained carbon adsorber such that the concentration of organic solvent in the exhaust does not exceed 100 parts per million.
2. In addition to the requirements of subdivision C 1 of this section, the owner of an in-line vapor cleaning machine shall use one of the following devices or strategies:
a. A freeboard ratio of 1.0 and superheated vapor.
b. A freeboard refrigeration device operated to ensure that the chilled air blanket temperature is no greater than 30% of the solvent's boiling point and a freeboard ratio of 1.0.
c. Dwell and a freeboard refrigeration device operated to ensure that the chilled air blanket temperature is no greater than 30% of the solvent's boiling point. Dwell shall be not less than 35% of the dwell time determined for the part or parts.
d. Dwell and a carbon adsorber that reduces solvent emissions in the exhaust to a level not to exceed 100 ppm at any time. Dwell shall be not less than 35% of the dwell time determined for the part or parts.
3. In-line vapor cleaning machines shall be operated in accordance with the following procedures:
a. Waste solvent, still bottoms, and sump bottoms shall be collected and stored in closed containers. The closed containers may contain a device that allows pressure relief, but does not allow liquid solvent to drain from the container.
b. Parts shall be oriented so that the solvent drains freely from the parts. Cleaned parts shall be drained at least 15 seconds or until dripping ceases, whichever is longer. Parts having cavities or blind holes shall be tipped or rotated while the part is draining.
c. Parts baskets or parts shall not be removed from the in-line vapor cleaning machine until dripping has ceased.
d. Flushing or spraying of parts using a flexible hose or other flushing device shall be performed within the vapor zone of the in-line vapor cleaning machine or within a section of the machine that is not exposed to the ambient air. The solvent spray shall be a solid fluid stream, not an atomized or shower spray.
e. Sponges, fabric, wood, leather, paper products and other absorbent materials shall not be cleaned in the in-line vapor cleaning machine.
f. Spills during solvent transfer and use of the in-line vapor cleaning machine shall be cleaned up immediately, and the wipe rags or other sorbent material shall be immediately stored in covered containers for disposal or recycling.
g. Workplace fans shall not be used near the degreaser opening, and ensure that exhaust ventilation shall not exceed 20 m³/min/m² of degreaser opening, unless a higher rate is necessary to meet OSHA requirements.
h. During startup of the in-line vapor cleaning machine the primary condenser shall be turned on before the sump heater.
i. During shutdown of the in-line vapor cleaning machine, the sump heater shall be turned off and the solvent vapor layer allowed to collapse before the primary condenser is turned off.
j. Spraying operations shall be done in the vapor zone or within a section of the machine that is not exposed to the ambient air.
k. When solvent is added to or drained from the in-line vapor cleaning machine, the solvent shall be transferred using threaded or other leakproof couplings and the end of the pipe in the solvent sump shall be located beneath the liquid solvent surface.
l. Openings shall be minimized during operation so that entrances and exits silhouette workloads with an average clearance between the parts and the edge of the degreaser opening of less than 10 cm (4 in) or less than 10% of the width of the opening.
D. No owner or other person shall use or permit the use of an airless cleaning machine or air-tight cleaning machine that processes metal parts unless the machine complies with this article.
1. The owner of each machine shall maintain a log of solvent additions and deletions for each machine including the weight of solvent contained in activated carbon or other sorbent material used to control emissions from the cleaning machine.
2. The owner of each machine shall demonstrate that the emissions from each machine, on a three-month rolling average, are equal to or less than the allowable limit determined by the use of Table 4-47A or the following equation if the volume of the cleaning machine exceeds 2.95 cubic meters:
EL = 330 (vol)0.6
where:
EL = the three-month rolling average monthly emission limit (kilograms/month)
vol = the cleaning capacity of machine (cubic meters)
Table 4-47A | |||||
Cleaning capacity (cubic meters) | 3-Month rolling average monthly emission limit (kilograms/month) | Cleaning capacity (cubic meters) | 3-Month rolling average monthly emission limit (kilograms/month) | Cleaning capacity (cubic meters) | 3-Month rolling average monthly emission limit (kilograms/month) |
0.00 | 0 | 1.00 | 330 | 2.00 | 500 |
0.05 | 55 | 1.05 | 340 | 2.05 | 508 |
0.10 | 83 | 1.10 | 349 | 2.10 | 515 |
0.15 | 106 | 1.15 | 359 | 2.15 | 522 |
0.20 | 126 | 1.20 | 368 | 2.20 | 530 |
0.25 | 144 | 1.25 | 377 | 2.25 | 537 |
0.30 | 160 | 1.30 | 386 | 2.30 | 544 |
0.35 | 176 | 1.35 | 395 | 2.35 | 551 |
0.40 | 190 | 1.40 | 404 | 2.40 | 558 |
0.45 | 204 | 1.45 | 412 | 2.45 | 565 |
0.50 | 218 | 1.50 | 421 | 2.50 | 572 |
0.55 | 231 | 1.55 | 429 | 2.55 | 579 |
0.60 | 243 | 1.60 | 438 | 2.60 | 585 |
0.65 | 255 | 1.65 | 446 | 2.65 | 592 |
0.70 | 266 | 1.70 | 454 | 2.70 | 599 |
0.75 | 278 | 1.75 | 462 | 2.75 | 605 |
0.80 | 289 | 1.80 | 470 | 2.80 | 612 |
0.85 | 299 | 1.85 | 477 | 2.85 | 619 |
0.90 | 310 | 1.90 | 485 | 2.90 | 625 |
0.95 | 320 | 1.95 | 493 | 2.95 | 632 |
3. The owner of each machine shall operate the machine in conformance with the manufacturer's instructions and good air pollution control practices.
4. The owner of each machine equipped with a solvent adsorber shall measure and record the concentration of solvent in the exhaust of the carbon adsorber weekly with a colorimetric detector tube designed to measure a concentration of 100 ppm by volume of solvent to air at an accuracy of plus or minus 25 ppm by volume. This test shall be conducted while the solvent cleaning machine is in the working mode and is venting to the adsorber.
5. The owner of each machine equipped with a solvent adsorber shall maintain and operate the machine and adsorber system so that emissions from the adsorber exhaust do not exceed 100 ppm by volume measured while the solvent cleaning machine is in the working mode and is venting to the adsorber.
6. The machine shall be equipped with a permanent, conspicuous label summarizing the operating requirements in subdivision 7 of this subsection.
7. Airless cleaning machines and air-tight cleaning machines shall be operated in accordance with the following procedures:
a. Waste solvent, still bottoms, and sump bottoms shall be collected and stored in closed containers. The closed containers may contain a device that allows pressure relief, but does not allow liquid solvent to drain from the container.
b. Parts shall be oriented so that the solvent drains freely from the parts. Cleaned parts shall be drained at least 15 seconds or until dripping ceases, whichever is longer. Parts having cavities or blind holes shall be tipped or rotated while the part is draining.
c. Parts baskets or parts shall not be removed from the in-line vapor cleaning machine until dripping has ceased.
d. Sponges, fabric, wood, leather, paper products and other absorbent materials shall not be cleaned in the airless cleaning machines and air-tight cleaning machines.
e. Spills during solvent transfer and use of the airless cleaning machines and air-tight cleaning machines shall be cleaned up immediately, and the wipe rags or other sorbent material shall be immediately stored in covered containers for disposal or recycling.
f. Work area fans shall be located and positioned so that they do not blow across the airless cleaning machine and air-tight cleaning machine.
g. Spraying operations shall be done in the vapor zone or within a section of the machine that is not exposed to the ambient air.
h. When solvent is added to or drained from the airless cleaning machine and air-tight cleaning machine, the solvent shall be transferred using threaded or other leakproof couplings and the end of the pipe in the solvent sump shall be located beneath the liquid solvent surface.
E. As an alternative to complying with the provisions of subsections B through D of this section the owner of a solvent cleaning machine may demonstrate compliance with subdivision 1 or 2 of this subsection. The owner shall maintain records sufficient to demonstrate compliance. The records shall include, at a minimum, the quantity of solvent added to and removed from the solvent cleaning machine, the dates of the addition and removal and shall be maintained for not less than two years.
1. If the cleaning machine has a solvent/air interface, the owner shall:
a. Maintain a log of solvent additions and removals for each solvent cleaning machine.
b. Ensure that emissions from each solvent cleaning machine are equal to or less than the applicable emission limit presented in Table 4-47B.
| Table 4-47B | ||
| Solvent cleaning machine | 3-month rolling average monthly emission limit | |
| kg/m2/month | lb/ft2/month | |
| Batch vapor solvent cleaning machines | 150 | 30.7 |
| Existing in-line solvent cleaning machines | 153 | 31.3 |
| New in-line solvent cleaning machines | 99 | 20.2 |
2. If the cleaning machine is a batch vapor cleaning machine and does not have a solvent/air interface, the owner shall:
a. Maintain a log of solvent additions and deletions for each solvent cleaning machine.
b. Ensure that the emissions from each solvent cleaning machine are equal to or less than the appropriate limits as described in subdivisions 3 and 4 of this subsection. Each owner of a batch vapor or in-line cleaning machine complying with this section shall demonstrate compliance with the applicable three-month rolling average monthly emission limit on a monthly basis.
3. For cleaning machines with a cleaning capacity that is less than or equal to 2.95 cubic meters, the emission limit shall be determined using Table 4-47A or the equation in subdivision 4 of this subsection. If the table is used and the cleaning capacity of the cleaning machine falls between two cleaning capacity sizes, then the lower of the two emission limits applies.
4. For cleaning machines with a cleaning capacity that is greater than 2.95 cubic meters, the emission limit shall be determined using the following equation:
EL = 330 (vol)0.6
where:
EL = the three-month rolling average monthly emission limit (kilograms/month)
vol = the cleaning capacity of machine (cubic meters)
5. Each owner of a batch vapor or in-line solvent cleaning machine complying with this subsection shall demonstrate compliance with the applicable three-month rolling average monthly emission limit on a monthly basis. If the applicable three-month rolling average emission limit is not met, an exceedance has occurred. All exceedances shall be reported to the board within 30 days of the determination of the exceedance.
F. The owner of a batch vapor or in-line solvent cleaning machine complying with subsection E shall maintain records and determine compliance with the applicable provisions in accordance with the following.
1. On the first operating day of every month ensure that the solvent cleaning machine system contains only clean liquid solvent. This includes, but is not limited to, fresh unused solvent, recycled solvent and used solvent that has been cleaned of soils. A fill line shall be indicated during the first month the measurements are made. The solvent level within the machine shall be returned to the same fill-line each month, immediately prior to calculating monthly emissions as specified in subdivision 2 of this subsection. The solvent cleaning machine does not have to be emptied and filled with fresh unused solvent prior to the calculations.
2. Using the records of all solvent additions and deletions for the previous monthly reporting period, determine solvent emissions (E) using one of the following equations:
For cleaning machines with a solvent/air interface:
| E = | SA - LSR - SSR |
| AREA |
where:
E = the total halogenated hazardous air pollutant (HAP) solvent emissions from the solvent cleaning machine during the most recent monthly reporting period (kilograms of solvent per square meter of solvent/air interface area per month)
SA = the total amount of halogenated HAP liquid solvent added to the solvent cleaning machine during the most recent monthly reporting period (kilograms of solvent per month)
LSR = the total amount of halogenated HAP liquid solvent removed from the solvent cleaning machine during the most recent monthly reporting period (kilograms of solvent per month)
SSR = the total amount of halogenated HAP solvent removed from the solvent cleaning machine in solid waste during the most recent monthly reporting period (kilograms of solvent per month) determined from tests conducted using EPA Reference Method 25d or by engineering calculations included in the compliance report
Area = the solvent/air interface area of the solvent cleaning machine (square meters)
For cleaning machines without a solvent/air interface:
E = SA - LSR - SSR
where:
E = the total halogenated HAP solvent emissions from the solvent cleaning machine during the most recent monthly reporting period i, (kilograms of solvent per month)
SA = the total amount of halogenated HAP liquid solvent added to the solvent cleaning machine during the most recent monthly reporting period (kilograms of solvent per month)
LSR = the total amount of halogenated HAP liquid solvent removed from the solvent cleaning machine during the most recent monthly reporting period (kilograms of solvent per month)
SSR = the total amount of halogenated HAP solvent removed from the solvent cleaning machine in solid waste during the most recent monthly reporting period (kilograms of solvent per month) determined from tests conducted using EPA reference method 25d or by engineering calculations included in the compliance report
3. Determine the monthly rolling average, EA, for the three-month period ending with the most recent reporting period using one of the following equations:
For cleaning machines with a solvent/air interface:
where:
EA = the average halogenated HAP solvent emissions over the preceding three-monthly reporting periods (kilograms of solvent per square meter of solvent/air interface area per month)
E = halogenated HAP solvent emissions for each month (j) for the most recent three-monthly reporting periods (kilograms of solvent per square meter of solvent/air interface area)
j=1 = the most recent monthly reporting period
j=2 = the monthly reporting period immediately prior to j=1
j=3 = the monthly reporting period immediately prior to j=2
For cleaning machines without a solvent/air interface:
where:
EA = the average halogenated HAP solvent emissions over the preceding three monthly reporting periods (kilograms of solvent per month)
E = halogenated HAP solvent emissions for each month (j) for the most recent three monthly reporting periods (kilograms of solvent per month)
j=1 = the most recent monthly reporting period
j=2 = the monthly reporting period immediately prior to j=1
j=3 = the monthly reporting period immediately prior to j=2
G. The owner of a solvent cleaning machine subject to the provisions of subsections B through D of this section shall conduct monitoring and recordkeeping as follows.
1. If a freeboard refrigeration device is used to comply with these standards, the owner shall use a thermometer or thermocouple to measure the temperature at the center of the air blanket during the idling mode. Measurements and recordings shall be made weekly.
2. If a superheated vapor system is used to comply with these standards, the owner shall use a thermometer or thermocouple to measure the temperature at the center of the superheated solvent vapor zone while the solvent cleaning machine is in the idling mode. Measurements and recordings shall be made weekly.
3. If a cover (working-mode, downtime-mode, or idling-mode cover) is used to comply with these standards, the owner shall conduct a visual inspection to determine if the cover is opening and closing properly, completely covers the cleaning machine openings when closed, and is free of cracks, holes, and other defects. Observations and recordings shall be made weekly.
4. If dwell is used, the owner shall determine the actual dwell time by measuring the period of time that parts are held within the freeboard area of the solvent cleaning machine after cleaning. Observations and recordings shall be made monthly.
5. The owner shall determine the hoist speed by measuring the time it takes for the hoist to travel a measured distance. The speed is equal to the distance in meters divided by the time in minutes (meters per minute). Measurements and recordings shall be made monthly.
6. The owner of a batch vapor or in-line solvent cleaning machine complying using reduced room draft, maintained by controlling room parameters (i.e., redirecting fans, closing doors and windows, etc.), shall conduct monitoring and record the results as follows.
a. Initially measure the windspeed within six inches above the top of the freeboard area of the solvent cleaning machine in accordance with the following:
(1) Determine the direction of the wind current by slowly rotating a velometer or similar device until the maximum speed is located.
(2) Orient a velometer in the direction of the wind current at each of the four corners of the machine.
(3) Record the reading for each corner.
(4) Average the values obtained at each corner and record the average wind speed.
b. Record the room parameters established during the initial compliance test to achieve the reduced room draft.
c. Quarterly monitoring of the windspeed in accordance with subdivision 6 a of this subsection.
d. Weekly monitoring of the room parameters as specified in subdivision 6 b of this subsection.
7. If an enclosure (full or partial) is used to achieve reduced room draft, the owner shall conduct an initial monitoring test and, thereafter, monthly monitoring tests of the windspeed within the enclosure by slowly rotating a velometer inside the entrance to the enclosure until the maximum speed is located and record the maximum wind speed. The owner shall also conduct a monthly visual inspection of the enclosure to determine if it is free of cracks, holes and other defects.
8. The owner of a machine using a carbon adsorber to comply with this section shall measure and record the concentration of halogenated HAP solvent in the exhaust of the carbon adsorber weekly with a colorimetric detector tube. This test shall be conducted while the solvent cleaning machine is in the working mode and is venting to the carbon adsorber. The exhaust concentration shall be determined using a colorimetric detector tube designed to measure a concentration of 100 parts per million by volume of solvent in air to an accuracy of plus or minus 25 parts per million by volume. The concentration shall be determined through a sampling port for monitoring within the exhaust outlet that is easily accessible and located at least eight stack or duct diameters downstream and two stack or duct diameters upstream from any flow disturbance such as a bend, expansion, contraction, or outlet, and downstream from no other inlet.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; Errata, 20:18 VA.R. 2027 May 17, 2004.
9VAC5-40-6850. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of 9VAC5 Chapter 40 (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) do not apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-6860. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of 9VAC5 Chapter 40 (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-6870. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of 9VAC5 Chapter 40 (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-6880. Standard for toxic pollutants.
The provisions of Article 4 (9VAC5-60-200 et seq.) of 9VAC5 Chapter 60 (Emission Standards for Toxic Pollutants from Existing Sources, Rule 6-4) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-6890. Compliance.
The provisions of subsections B, D, F, and J of 9VAC5-40-20 (Compliance) apply. The other provisions of 9VAC5-40-20 do not apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-6900. Compliance schedules.
Affected persons shall comply with the provisions of this article as expeditiously as possible but in no case later than January 1, 2005.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-6910. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission testing) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-6920. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-6930. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-6940. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-6950. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-6960. Permits.
A permit may be required prior to beginning any of the activities specified below if the provisions of 9VAC5 Chapter 50 (9VAC5-50) and 9VAC5 Chapter 80 (9VAC5-80) apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
Article 48
Emission Standards for Mobile Equipment Repair and Refinishing Operations (Rule 4-48)
9VAC5-40-6970. Applicability and designation of affected facility.
Article 48
Emission Standards for Mobile Equipment Repair and Refinishing Operations (Rule 4-48)
A. Except as provided in 9VAC5-40-6975, the affected facility to which the provisions of this article apply is each mobile equipment repair and refinishing operation. Certain provisions also apply to each person providing or selling affected coatings.
B. The provisions of this article apply only to sources and persons in the Northern Virginia, Fredericksburg, and Richmond Volatile Organic Compound Emissions Control Areas designated in 9VAC5-20-206.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; Volume 29, Issue 26, eff. October 1, 2013.
9VAC5-40-6975. Exemptions.
The provisions of this article do not apply under any of the following circumstances:
1. The mobile equipment repair and refinishing operation is subject to Article 28 (9VAC5-40-3860 et seq.) of 9VAC5-40 (Emission Standards for Automobile and Light Duty Truck Coating Application Systems).
2. The mobile equipment repair and refinishing operation is subject to Article 34 (9VAC5-40-4760 et seq.) of 9VAC5-40 (Emission Standards for Miscellaneous Metal Parts and Products Coating Application Systems).
3. The person applying the coatings does not receive compensation for the application of the coatings.
4. The mobile equipment repair and refinishing operation uses coatings required to meet military specifications (MILSPEC) where no other existing coating can be used that meets the provisions of this article.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 29, Issue 26, eff. October 1, 2013.
9VAC5-40-6980. Definitions.
A. For the purpose of applying this article in the context of the Regulations for the Control and Abatement of Air Pollution and related uses, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined herein shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10), unless otherwise required by context.
C. Terms defined.
"Airless spray" means a spray coating method in which the coating is atomized by forcing it through a small nozzle opening at high pressure. The coating is not mixed with air before exiting from the nozzle opening.
"Antique motor vehicle" means a motor vehicle, but not a reproduction thereof, manufactured more than 25 years prior to the current year that has been maintained in or restored to a condition that is substantially in conformance with manufacturer specifications.
"Automotive elastomeric coating" means a coating designed for application over surfaces of flexible mobile equipment and mobile equipment components, such as elastomeric bumpers.
"Automotive impact-resistant coating" means a coating designed to resist chipping caused by road debris.
"Automotive jambing clearcoat" means a fast-drying, ready-to-spray clearcoat applied to surfaces such as door jambs and trunk and hood edges to allow for quick closure.
"Automotive lacquer" means a thermoplastic coating applied directly to bare metal surfaces of mobile equipment and mobile equipment components that dries primarily by solvent evaporation and that is resoluble in its original solvent.
"Automotive low-gloss coating" means a coating that exhibits a gloss reading less than or equal to 25 on a 60 degree glossmeter.
"Automotive multicolored topcoat" means a topcoat that exhibits more than one color, is packaged in a single container, and camouflages surface defects on areas of heavy use, such as cargo beds and other surfaces of trucks and other utility vehicles.
"Automotive pretreatment" means a primer that contains a minimum of 0.5% acid, by weight, that is applied directly to bare metal surfaces of mobile equipment and mobile equipment components to provide corrosion resistance and to promote adhesion of subsequent coatings.
"Automotive primer-sealer" means a coating applied to mobile equipment and mobile equipment components prior to the application of a topcoat for the purpose of providing corrosion resistance, promoting adhesion of subsequent coatings, promoting color uniformity, and promoting the ability of the undercoat to resist penetration by the topcoat.
"Automotive primer-surfacer" means a coating applied to mobile equipment and mobile equipment components prior to the application of topcoat for the purpose of filling surface imperfections in the substrate, providing corrosion resistance, or promoting adhesion of subsequent coatings.
"Automotive specialty coating" means coatings including, but not limited to, elastomeric coatings, adhesion promoters, low gloss coatings, bright metal trim repair coatings, jambing clearcoats, impact resistant coatings, rubberized asphaltic underbody coatings, uniform finish blenders, weld-through primers applied to automotive surfaces and lacquer topcoats applied to a classic motor vehicle or to an antique motor vehicle.
"Automotive topcoat" means a coating or series of coatings applied over an automotive primer-surfacer, automotive primer-sealer or existing finish on the surface of mobile equipment and mobile equipment components for the purpose of protection or beautification.
"Automotive touch up repair" means the application of automotive topcoat finish materials to cover minor finishing imperfections equal to or less than one inch in diameter.
"Classic motor vehicle" means a motor vehicle, but not a reproduction thereof, manufactured at least 15 years prior to the current year that has been maintained in or restored to a condition that is substantially in conformity with manufacturer specifications and appearance.
"Mobile equipment" means equipment that may be driven or is capable of being driven on a roadway including, but not limited to, automobiles; trucks, truck cabs, truck bodies and truck trailers; buses; motorcycles; utility bodies; camper shells; mobile cranes; bulldozers; street cleaners; golf carts; ground support vehicles, used in support of aircraft activities at airports; and farm equipment.
"Mobile equipment repair and refinishing operation" means any facility that applies automotive pretreatment, automotive primer-surface, automotive primer-sealer, automotive topcoat, or automotive specialty or color matched coatings to mobile equipment or mobile equipment components.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-6990. Standard for volatile organic compounds.
A. No owner or other person may apply to mobile equipment or mobile equipment components any automotive pretreatment, automotive primer-surface, automotive primer-sealer, automotive topcoat, or automotive specialty coatings, including any VOC-containing materials added to the original coating supplied by the manufacturer, that contain VOCs in excess of the limits specified in Table 4-48A.
Table 4-48A. | ||
Weight of VOC per Volume of Coating (minus water and non-VOC solvents) | ||
Coating Type | Limit | |
| Pounds per gallon | Grams per Liter |
Automotive pretreatment primer | 6.5 | 780 |
Automotive primer-surfacer | 4.8 | 575 |
Automotive primer-sealer | 4.6 | 550 |
Automotive topcoat: |
|
|
Single stage-topcoat | 5.0 | 600 |
2 stage basecoat/clearcoat | 5.0 | 600 |
3 or 4-stage basecoat/clearcoat | 5.2 | 625 |
Automotive Multi-colored Topcoat | 5.7 | 680 |
Automotive specialty | 7.0 | 840 |
B. A person who provides mobile equipment repair and refinishing coatings subject to this section shall provide documentation concerning the VOC content of the coatings calculated in accordance with the following:
1. The mass of VOC per combined volume of VOC and coating solids, less water and exempt compounds shall be calculated by the following equation:
| VOC = | (Wv - Ww - Wec) |
(V - Vw - Vec) |
where:
VOC = VOC content in grams per liter (g/l) of coating less water and non-VOC solvents;
Wv = Mass of total volatiles, in grams;
Ww = Mass of water, in grams;
Wec = Mass of exempt compounds, in grams;
V = Volume of coating, in liters;
Vw = Volume of water, in liters; and
Vec = Volume of exempt compounds, in liters.
To convert from grams per liter to pounds per gallon (lb/gal), multiply the result (VOC content) by 8.345 x 10-3 (lb/gal/g/l).
2. The VOC content of a multi-stage topcoat shall be calculated by the following equation:
where:
VOCmulti = VOC content of multistage topcoat, g/l
VOCbc = VOC content of basecoat, g/l
VOCmci = VOC content of the midcoat(s), g/l
VOCcc = VOC content of the clear coat, g/l
M = number of midcoats
C. A person subject to the provisions of this section shall use one or more of the following application techniques to apply any finish material listed in Table 4-48A:
1. Flow/curtain coating;
2. Dip coating;
3. Roller coating;
4. Brush coating;
5. Cotton-tipped swab application;
6. Electrodeposition coating;
7. High volume low pressure (HVLP) spraying;
8. Electrostatic spray;
9. Airless spray; or
10. Other coating application methods that achieve emission reductions equivalent to or greater than those achieved by HVLP or electrostatic spray application methods.
D. The following activities are exempt from the application equipment requirements listed in subsections E and F of this section:
1. The use of airbrush application methods for stenciling, lettering, and other identification markings;
2. The application of coatings sold in nonrefillable aerosol containers; and
3. The application of automotive touch-up repair finish materials.
E. Spray guns used to apply mobile equipment repair and refinishing coatings shall be cleaned by one of the following:
1. An enclosed spray gun cleaning system that is kept closed when not in use;
2. Unatomized discharge of solvent into a paint waste container that is kept closed when not in use;
3. Disassembly of the spray gun and cleaning in a vat that is kept closed when not in use; or
4. Atomized spray into a paint waste container that is fitted with a device designed to capture atomized solvent emissions.
F. The owner of a facility subject to the provisions of this article shall implement the following housekeeping and pollution prevention and training measures:
1. Fresh and used coatings, solvent, and cleaning solvents, shall be stored in nonabsorbent, nonleaking containers. The containers shall be kept closed at all times except when filling or emptying;
2. Cloth and paper, or other absorbent applicators, moistened with coatings, solvents, or cleaning solvents, shall be stored in closed, nonabsorbent, nonleaking containers;
3. Handling and transfer procedures shall minimize spills during the transfer of coatings, solvents, and cleaning solvents; and
4. Ensure that a person who applies mobile equipment repair and refinishing coatings has completed training approved by the manufacturer of the coatings in the proper use and handling of the mobile equipment repair and refinishing coatings, solvents and waste products in order to minimize the emission of air contaminants and to comply with this section.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; Errata, 20:18 VA.R. 2027 May 17, 2004.
9VAC5-40-7000. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of 9VAC5 Chapter 40 (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) do not apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-7010. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of 9VAC5 Chapter 40 (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-7020. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of 9VAC5 Chapter 40 (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-7030. Standard for toxic pollutants.
The provisions of Article 4 (9VAC5-60-200 et seq.) of 9VAC5 Chapter 60 (Emission Standards for Toxic Pollutants from Existing Sources, Rule 6-4) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-7040. Compliance.
The provisions of subsections B, D, F, and J of 9VAC5-40-20 (Compliance) apply. The other provisions of 9VAC5-40-20 do not apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-7050. Compliance schedules.
Affected persons and facilities shall comply with the provisions of this article as expeditiously as possible but in no case later than:
1. January 1, 2005, in the Northern Virginia VOC Emissions Control Area;
2. January 1, 2008, in the Fredericksburg VOC Emissions Control Area; or
3. March 1, 2014, in the Richmond VOC Emissions Control Area.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; Volume 29, Issue 26, eff. October 1, 2013.
9VAC5-40-7060. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission testing) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-7070. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-7080. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-7090. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-7100. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-7110. Permits.
A permit may be required prior to beginning any of the activities specified below if the provisions of 9VAC5 Chapter 50 (9VAC5-50) and 9VAC5 Chapter 80 (9VAC5-80) apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act, 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004.
9VAC5-40-7120. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7130. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7140. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; Errata 20:18 VA.R. 2027 May 17, 2004; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; Errata, 23:5 VA.R. 791 November 13, 2006; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7150. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7160. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7170. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7180. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7190. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7200. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7210. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; amended, Volume 22, Issue 26, eff. October 4, 2006; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7220. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; Errata 20:18 VA.R. 2027 May 17, 2004; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7230. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 20, Issue 12, eff. March 24, 2004; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7240. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 21, Issue 11, eff. March 9, 2005; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7250. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 21, Issue 11, eff. March 9, 2005; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7260. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 21, Issue 11, eff. March 9, 2005; Errata 21:13 VA.R. 1941 March 7, 2005; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; Errata 23:5 VA.R. 791 November 13, 2006; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7270. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 21, Issue 11, eff. March 9, 2005; Errata, 21:13 VA.R. 1941 March 7, 2005; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7280. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 21, Issue 11, eff. March 9, 2005; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7290. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 21, Issue 11, eff. March 9, 2005; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7300. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 21, Issue 11, eff. March 9, 2005; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7310. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 21, Issue 11, eff. March 9, 2005; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7320. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 21, Issue 11, eff. March 9, 2005; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7330. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 21, Issue 11, eff. March 9, 2005; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7340. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 21, Issue 11, eff. March 9, 2005; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7350. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 21, Issue 11, eff. March 9, 2005; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
9VAC5-40-7360. (Repealed.)
Historical Notes
Derived from Virginia Register Volume 21, Issue 11, eff. March 9, 2005; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; repealed, Virginia Register Volume 28, Issue 25, eff. September 27, 2012.
Article 51
Emission Standards for Stationary Sources Subject to Case-By-Case Ract Determination (Rule 4-51)
9VAC5-40-7370. Applicability and designation of affected facility.
Article 51
Emission Standards for Stationary Sources Subject to Case-by-Case RACT Determination (Rule 4-51)
A. The affected facility to which the provisions of this article apply is each facility that is within a stationary source that has a theoretical potential to emit equal to or greater than the applicable source threshold specified in Table 4-51A or 4-51B, and Table 4-51C or 4-51E.
B. The provisions of this article apply to all Emission Control Areas as defined in 9VAC5-20-206 and indicated in Table 4-51A or 4-51B, and Table 4-51C or 4-51E.
C. The provisions of this article do not apply to a particular pollutant from an affected facility if the affected facility is subject to other emission standards in this chapter covering the same pollutant.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7380. Definitions.
A. For the purpose of applying this article in the context of the Regulations for the Control and Abatement of Air Pollution and related uses, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5-10, unless otherwise required by context.
C. Terms defined.
"Capacity factor" means the ratio of the average load on a machine or equipment for the period of time considered to be the capacity rating of the machine or equipment.
"Combustion modification" means any change to the configuration of the burners or the firing method or mechanism of any combustion equipment for the purpose of reducing the emissions of nitrogen oxides. Acceptable combustion equipment changes within the context of this term include, but are not limited to, reburning, burners out of service, flue gas recirculation, fuel substitution, engine adjustments, engine modifications, fuel modifications and the addition of over fire air and low nitrogen oxides burner systems.
"Fossil fuel" means natural gas, petroleum, coal and any form of solid, liquid or gaseous fuel derived from such materials for the purpose of creating useful heat.
"Fuel burning equipment" means any furnace, with fuel burning equipment appurtenances thereto, used in the process of burning fuel for the primary purpose of producing heat to be utilized by indirect heat transfer or producing power. This includes facilities that are designed as boilers to produce steam or heated water and are designed to burn either fossil fuel or refuse derived fuel. It does not include such facilities if designed primarily to burn raw refuse.
"Gas turbine" means a rotary internal combustion engine fueled by liquid or gaseous fuel.
"Heat input" means the total gross calorific value of all fuels burned.
"Incinerator" means any device, apparatus, equipment, or structure using combustion or pyrolysis for destroying, or reducing the volume of any material or substance.
"Internal combustion engine" means a reciprocating engine that is fueled by liquid or gaseous fuel.
"Presumptive RACT" means the emission limit that a particular source is capable of meeting by the application of reasonably available control technology that is defined in 9VAC5-40-7430.
"Process heater" means any fuel burning equipment that is used to produce heat for use in a manufacturing process. This term includes boilers that use a heat transfer medium other than water, but does not include drying ovens, steam generating units, or other drying apparatus.
"Rated capacity" means the capacity as stipulated in the purchase contract for the condition of 100% load, or such other capacities as mutually agreed to by the board and owner using good engineering judgment.
"Reasonably available control technology" or "RACT" means the lowest emission limit that a particular source is capable of meeting by the application of control technology that is reasonably available, considering technological and economic feasibility.
"Refuse derived fuel (RDF)" means fuel produced from solid or liquid waste (includes materials customarily referred to as refuse and other discarded materials) or both that has been segregated and classified, with the useable portions being put through a size reduction and classification process which results in a relatively homogeneous mixture.
"Steam generating unit" means any furnace, boiler or other device used for combusting fuel for the purpose of producing steam.
"Theoretical potential to emit" means the maximum capacity of a stationary source to emit a pollutant based on emissions at design capacity or maximum production and maximum operating hours (8,760 hours/year) before add-on controls, unless the facility is subject to state and federally enforceable permit conditions that limit production rates or hours of operation. Emissions from all facilities, including facilities exempt from any other emission standard for volatile organic compounds or nitrogen oxides in this chapter, shall be added together to determine theoretical potential to emit.
"Tpy" means tons per year.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7390. Standard for volatile organic compounds (one-hour ozone standard).
A. No owner or other person shall cause or permit to be discharged from any affected facility any volatile organic compounds (VOCs) emissions in excess of that resultant from using RACT.
B. The provisions of this section apply to all facilities that (i) are within a stationary source in the emissions control areas specified in Table 4-51A and (ii) are within a stationary source that has a theoretical potential to emit at the applicable source thresholds specified Table 4-51A.
TABLE 4-51A. | |||
Emissions Control Area | Source Threshold | Notification Date | Compliance Date |
Richmond | ≥ 100 tpy | October 1, 1991 | May 31, 1995 |
Northern Virginia | ≥ 100 tpy | October 1, 1991 | May 31, 1995 |
Northern Virginia | ≥ 50 tpy and < 100 tpy | April 1, 1993 | May 31, 1995 |
Northern Virginia | ≥ 25 tpy and < 50 tpy | July 1, 1996 | May 31, 1996 |
C. For facilities subject to the provisions of this section, the owners shall, by the notification dates specified in Table 4-51A, (i) notify the board of their applicability status, (ii) commit to making a determination as to what constitutes RACT for the facilities and (iii) provide a schedule acceptable to the board for making this determination and for achieving compliance with the emission standard as expeditiously as possible but no later than the compliance dates specified in Table 4-51A.
D. For the purposes of this section only, the Richmond Emissions Control Area shall not include Prince George County and Petersburg City.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7400. Standard for volatile organic compounds (eight-hour ozone standard).
A. No owner or other person shall cause or permit to be discharged from any affected facility any volatile organic compounds (VOCs) emissions in excess of that resultant from using RACT.
B. The provisions of this section apply to all facilities that (i) are within a stationary source in the emissions control areas specified in Table 4-51B and (ii) are within a stationary source that has a theoretical potential to emit at the applicable source thresholds specified Table 4-51B.
| TABLE 4-51B. | |||
Standard | Emissions Control Area | Source Threshold | Notification Date | Compliance Date |
1997 (0.08 ppm) | Northern Virginia | ≥ 50 tpy | March 1, 2007 | April 1, 2009 |
2008 (0.075 ppm) | Northern Virginia | ≥ 50 tpy | February 1, 2016 | January 1, 2017 |
C. For facilities subject to the provisions of this section, the owners shall, by the notification dates specified in Table 4-51B, (i) notify the board of their applicability status, (ii) commit to making a determination as to what constitutes RACT for the facilities, and (iii) provide a schedule acceptable to the board for making this determination and for achieving compliance with the emission standard as expeditiously as possible but no later than the compliance dates specified in Table 4-51B.
D. Nothing in this article shall exempt any facility subject to the provisions of 9VAC5-40-7390 from being subject to the provisions of this section. The board may reevaluate any RACT determination made under 9VAC5-40-7390 and require compliance with a new RACT determination as necessary to implement this section.
E. Upon the request of the board, the owner of a facility subject to or exempt from the provisions of 9VAC5-40-7390 shall provide such information as the board deems necessary to determine if the facility is subject to this section.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006; amended, Virginia Register Volume 32, Issue 5, eff. December 2, 2015.
9VAC5-40-7410. Standard for nitrogen oxides (one-hour ozone standard).
A. No owner or other person shall cause or permit to be discharged from any affected facility any nitrogen oxides (NOX) emissions in excess of that resultant from using RACT.
B. Unless the owner demonstrates otherwise to the satisfaction of the board, facilities to which the presumptive RACT provisions of 9VAC5-40-7430 are applicable shall comply with the provisions of subsection A of this section by the use of presumptive RACT.
C. The provisions of this section apply to all facilities that (i) are within a stationary source in the emissions control areas specified in Table 4-51C and (ii) are within a stationary source that has a theoretical potential to emit at the applicable source thresholds specified in Table 4-51C.
TABLE 4-51C. | |||
Emissions Control Area | Source Threshold | Notification Date | Compliance Date |
Northern Virginia | ≥ 50 tpy | April 1, 1993 | May 31, 1995 |
Northern Virginia | ≥ 25 tpy and < 50 tpy | September 4, 2003 | November 15, 2005 |
Western Virginia | ≥ 100 tpy | June 24, 2004 | November 15, 2005 |
D. For facilities subject to the provisions of this section and for which there is no presumptive RACT definition, the owners shall, by the notification dates specified in Table 4-51C, (i) notify the board of their applicability status, (ii) commit to making a determination as to what constitutes RACT for the facilities and (iii) provide a schedule acceptable to the board for making this determination and for achieving compliance with the emission standard as expeditiously as possible but no later than the compliance dates specified in Table 4-51C.
E. For facilities subject to the provisions of this section and for which there is a presumptive RACT definition, the owners shall, by the notification dates specified in Table 4-51D, (i) notify the board of their applicability status, (ii) commit to accepting the presumptive RACT emission limits as RACT for the applicable facilities or to submitting a demonstration as provided in subsection B of this section and (iii) provide a schedule acceptable to the board for submitting the demonstration no later than the demonstration dates specified in Table 4-51D, and for achieving compliance with the emission standard as expeditiously as possible but no later than the compliance dates specified in Table 4-51D.
TABLE 4-51D. | ||||
Emissions Control Area | Source Threshold | Notification Date | Demonstration Date | Compliance Date |
Northern Virginia | ≥ 50 tpy | April 1, 1993 | January 1, 1994 | May 31, 1995 |
Northern Virginia | ≥ 25 tpy and < 50 tpy | September 4, 2003 | January 1, 2004 | November 15, 2005 |
Western Virginia | ≥ 100 tpy | June 24, 2004 | January 1, 2004 | November 15, 2005 |
F. No owner or other person shall cause or permit to be discharged from any facility any NOX emissions in excess of those necessary to achieve emissions reductions identified in any attainment or maintenance plan or any other legally enforceable document submitted to the U.S. Environmental Protection Agency as a revision to the state implementation plan.
1. The facilities to which the provisions of this subsection apply are facilities within any emissions control area (see 9VAC5-20-206) identified in any attainment or maintenance plan submitted to the U.S. Environmental Protection Agency as a revision to the state implementation plan.
2. The board may establish case-by-case emission limits and other requirements as may be necessary to achieve the required emission reductions via permits, consent orders, or other legally enforceable means.
3. Facilities subject to this subsection shall be in compliance with any limits and other requirements established pursuant to subdivision 2 of this subsection within the timeframes established in any state plan revision, permit, or other legally enforceable document.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7420. Standard for nitrogen oxides (eight-hour ozone standard).
A. No owner or other person shall cause or permit to be discharged from any affected facility any nitrogen oxides (NOX) emissions in excess of that resultant from using RACT.
B. Unless the owner demonstrates otherwise to the satisfaction of the board, facilities to which the presumptive RACT provisions of 9VAC5-40-7430 are applicable shall comply with the provisions of subsection A of this section by the use of presumptive RACT.
C. The provisions of this section apply to all facilities that (i) are within a stationary source in the emissions control areas specified in Table 4-51E and (ii) are within a stationary source that has a theoretical potential to emit at the applicable source thresholds specified in Table 4-51E.
TABLE 4-51E. | ||||
Standard | Emissions Control Area | Source Threshold | Notification Date | Compliance Date |
1997 (0.08 ppm) | Northern Virginia | ≥ 100 tpy | March 1, 2007 | April 1, 2009 |
2008 (0.075 ppm) | Northern Virginia | ≥ 100 tpy | February 1, 2016 | January 1, 2017 |
D. For facilities subject to the provisions of this section and for which there is no presumptive RACT definition, the owners shall, by the notification dates specified in Table 4-51E, (i) notify the board of their applicability status, (ii) commit to making a determination as to what constitutes RACT for the facilities, and (iii) provide a schedule acceptable to the board for making this determination and for achieving compliance with the emission standard as expeditiously as possible but no later than the compliance dates specified in Table 4-51E.
E. For facilities subject to the provisions of this section and for which there is a presumptive RACT definition, the owners shall, by the notification dates specified in Table 4-51F, (i) notify the board of their applicability status, (ii) commit to accepting the presumptive RACT emission limits as RACT for the applicable facilities or to submitting a demonstration as provided in subsection B of this section, and (iii) provide a schedule acceptable to the board for submitting the demonstration no later than the demonstration dates specified in Table 4-51F and for achieving compliance with the emission standard as expeditiously as possible but no later than the compliance dates specified in Table 4-51F.
TABLE 4-51F. | |||||
Standard | Emissions Control Area | Source Threshold | Notification Date | Demonstration Date | Compliance Date |
1997 (0.08 ppm) | Northern Virginia | ≥ 100 tpy | March 1, 2007 | June 1, 2007 | April 1, 2009 |
2008 (0.075 ppm) | Northern Virginia | ≥ 100 tpy | February 1, 2016 | February 1, 2016 | January 1, 2017 |
F. Nothing in this article shall exempt any facility subject to the provisions of 9VAC5-40-7410 from being subject to the provisions of this section. The board may reevaluate any RACT determination made under 9VAC5-40-7410 and require compliance with a new RACT determination as necessary to implement this section.
G. Upon the request of the board, the owner of a facility subject to or exempt from the provisions of 9VAC5-40-7410 shall provide such information as the board deems necessary to determine if the facility is subject to this section.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006; amended, Virginia Register Volume 26, Issue 8, eff. January 20, 2010; Volume 32, Issue 5, eff. December 2, 2015.
9VAC5-40-7430. Presumptive reasonably available control technology guidelines for stationary sources of nitrogen oxides.
A. Unless otherwise approved by the board, this section defines presumptive RACT for the purposes of compliance with 9VAC5-40-7410 A or 9VAC5-20-7420 A for the source types specified here.
B. Presumptive RACT is defined as follows.
1. For the source types listed below, RACT is defined as the emission limits specified below based upon the application of combustion modification; however, owners may elect to use any alternative control technology, provided such alternative is capable of achieving the prescribed emission limits.
a. The maximum allowable emission rate for NOX from steam generating units and process heaters is as follows:
TABLE 4-51G. | |||
Fuel Type | Firing Method | ||
Face* and Tangential | Cyclone | Stokers | |
Coal – wet bottom | 1.0 | .55 | N/A |
Coal – dry bottom | .38 | N/A | 0.4 |
Oil or Gas or both | .25 | .43 | N/A |
Gas only | .20 | N/A | N/A |
*Includes wall, opposed and vertical firing methods |
b. The maximum allowable emission rate for NOX from gas turbines is as follows:
TABLE 4-51H. | ||
Fuel Type | Turbine Type | |
Simple Cycle | Combined Cycle | |
Gas | 42 | 42 |
Oil | 65/77* | 65/77* |
*Limit shall be 65 ppm for fuel bound nitrogen (FBN) <0.015% and 77 ppm for FBN ≥ .015%. |
2. Any demonstration of compliance with the limits in subdivision B 1 of this section shall be on a daily basis.
3. The following sources are not required to make demonstration of RACT as required by 9VAC5-40-7410 B or 9VAC5-40-7420 B.
a. Any steam generating unit, process heater or gas turbine with an annual capacity factor of less than 5.0%, except that three months following any calendar year during which the capacity factor is 5.0% or greater, the facility shall be subject to 9VAC5-40-7410 A or B, or 9VAC5-40 7420 A or B, as applicable, and the owner shall comply with 9VAC5-40-7410 D or E, or 9VAC5-40-7420 D or E, as applicable, except the compliance date shall be two years after approval of the schedule by the board. Time periods during which a stand-by unit is used to provide replacement services for a unit being altered to comply with the provisions of 9VAC5-40-7410 A or B, or 9VAC5-40-7420 A or B, shall not be used as the basis for a determination that the stand-by unit exceeded the annual capacity factor criteria of 5.0%.
b. Any stationary internal combustion engine with a rated capacity of less than 450 hp of output power.
c. Any incinerator with a maximum capacity of less than 50 tons of waste per day.
d. Any incinerator or thermal or catalytic oxidizer used exclusively as air pollution control equipment.
e. Any generator used solely to supply emergency power to buildings during periods when normal power supplies are interrupted and during periods of scheduled maintenance.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7440. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7450. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7460. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7470. Standard for toxic pollutants.
The provisions of Article 4 (9VAC5-60-200 et seq.) of 9VAC5 Chapter 60 (Emission Standards for Toxic Pollutants, Rule 6-4) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7480. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7490. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission Testing) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7500. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7510. Notification, records and reporting.
The provisions of 9VAC5-40-50 (Notification, Records and Reporting) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7520. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7530. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and Control Equipment Maintenance or Malfunction) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
9VAC5-40-7540. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5-50 and 9VAC5-80 may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 5, eff. December 15, 2006.
Article 52
Emission Standards for Stationary Sources Subject to Case-By-Case Bart Determinations
9VAC5-40-7550. Applicability and designation of affected facility.
Article 52
Emission Standards for Stationary Sources Subject to Case-by-Case BART Determinations
A. Except as provided in subsection C of this section, the affected facility to which the provisions of this article apply is each BART-eligible source that emits any air pollutant that may reasonably be anticipated to cause or contribute to any impairment of visibility in any mandatory federal class I area.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
C. Exempted from the provisions of this article are the following:
1. Any BART-eligible source with the potential to emit less than 40 tons per year of SO2 or NOX, or less than 15 tons per year of PM10.
2. Any existing stationary facility subject to the requirement under 9VAC5-40-7580 to install, operate, and maintain BART for which the board has granted an exemption in accordance with 9VAC5-40-7560 or for which the administrator has granted an exemption under 40 CFR 51.303 with which the board concurs.
3. The provisions of this article do not apply to sources subject to Part IV (9VAC5-140-3010 et seq.) of 9VAC5-140, Regulation for Emissions Trading.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7560. Exemptions from control.
A. Any existing stationary facility subject to the requirement to install, operate, and maintain BART may apply to the board for an exemption from that requirement. An application under this subsection shall include all available documentation relevant to the impact of the source's emissions on visibility in any mandatory federal class I area and a demonstration by the existing stationary facility that it does not or will not, by itself or in combination with other sources, emit any air pollutant that may be reasonably anticipated to cause or contribute to a significant impairment of visibility in any mandatory federal class I area.
B. Any fossil-fuel fired power plant with a total generating capacity of 750 megawatts or more may receive an exemption from BART only if the owner demonstrates to the satisfaction of the board that the power plant is located at such a distance from all mandatory federal class I areas that it does not or will not, by itself or in combination with other sources, emit any air pollutant that may reasonably be anticipated to cause or contribute to significant impairment of visibility in any such mandatory federal class I area.
C. The existing stationary facility shall give prior written notice to all affected federal land managers of any application for exemption under this section. The federal land manager may provide an initial recommendation or comment on the disposition of such application. Such recommendation, where provided, must be part of the exemption application. This recommendation is not to be construed as the concurrence required under subsection D of this section. The board, within 90 days of receipt of an application for exemption from control, will provide notice of receipt of an exemption application and notice of opportunity for public hearing on the application. After notice and opportunity for public hearing, the board may grant or deny the exemption.
D. An exemption granted by the board will be effective only upon concurrence by all affected federal land managers and the administrator with the board's determination.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7570. Definitions.
A. For the purpose of applying this article in the context of the Regulations for the Control and Abatement of Air Pollution and related uses, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined herein shall have the meaning given them in 9VAC5-10, General Definitions, unless otherwise required by context.
C. Terms defined.
"Administrator" means the administrator of the U.S. Environmental Protection Agency (EPA) or an authorized representative.
"BART-eligible source" means an existing stationary facility as defined in this subsection.
"Best available retrofit technology" or "BART" means an emission limitation based on the degree of reduction achievable through the application of the best system of continuous emission reduction for each pollutant that is emitted by an existing stationary facility. The emission limitation shall be established, on a case-by-case basis, taking into consideration the technology available, the costs of compliance, the energy and nonair quality environmental impacts of compliance, any pollution control equipment in use or in existence at the source, the remaining useful life of the source, and the degree of improvement in visibility that may reasonably be anticipated to result from the use of such technology.
"Existing stationary facility" means any of the following stationary sources of air pollutants, including any reconstructed source, which were not in operation prior to August 7, 1962, and were in existence on August 7, 1977, and have the potential to emit 250 tons per year or more of any air pollutant. In determining potential to emit, fugitive emissions, to the extent quantifiable, must be counted.
1. Fossil-fuel fired steam electric plants of more than 250 million British thermal units per hour heat input,
2. Coal cleaning plants (thermal dryers),
3. Kraft pulp mills,
4. Portland cement plants,
5. Primary zinc smelters,
6. Iron and steel mill plants,
7. Primary aluminum ore reduction plants,
8. Primary copper smelters,
9. Municipal incinerators capable of charging more than 250 tons of refuse per day,
10. Hydrofluoric, sulfuric, and nitric acid plants,
11. Petroleum refineries,
12. Lime plants,
13. Phosphate rock processing plants,
14. Coke oven batteries,
15. Sulfur recovery plants,
16. Carbon black plants (furnace process),
17. Primary lead smelters,
18. Fuel conversion plants,
19. Sintering plants,
20. Secondary metal production facilities,
21. Chemical process plants,
22. Fossil-fuel boilers of more than 250 million British thermal units per hour heat input,
23. Petroleum storage and transfer facilities with a capacity exceeding 300,000 barrels,
24. Taconite ore processing facilities,
25. Glass fiber processing plants, and
26. Charcoal production facilities.
"Federal class I area" means any federal land that is classified or reclassified class I.
"Federal land manager" or "FLM" means the secretary of the department with authority over the federal class I area (or the secretary's designee).
"Federally enforceable" means all limitations and conditions that are enforceable by the administrator under the federal Clean Air Act including those requirements developed pursuant to 40 CFR Parts 60 and 61, requirements within any applicable implementation plan, and any permit requirements established pursuant to 40 CFR 52.21 or under regulations approved pursuant to 40 CFR Parts 51, 52, or 60.
"Fugitive emissions" means those emissions that could not reasonably pass through a stack, chimney, vent, or other functionally equivalent opening.
"In existence" means that the owner has obtained all necessary preconstruction approvals or permits required by federal, state, or local air pollution emissions and air quality laws or regulations and either has (i) begun, or caused to begin, a continuous program of physical on-site construction of the facility or (ii) entered into binding agreements or contractual obligations, which cannot be cancelled or modified without substantial loss to the owner, to undertake a program of construction of the facility to be completed in a reasonable time.
"In operation" means engaged in activity related to the primary design function of the source.
"Integral vista" means a view perceived from within the mandatory federal class I area of a specific landmark or panorama located outside the boundary of the mandatory federal class I area.
"Mandatory federal class I area" means any area identified in subpart D of 40 CFR Part 81.
"Potential to emit" means the maximum capacity of a stationary source to emit a pollutant under its physical and operational design. Any physical or operational limitation on the capacity of the source to emit a pollutant including air pollution control equipment and restrictions on hours of operation or on the type or amount of material combusted, stored, or processed, shall be treated as part of its design if the limitation or the effect it would have on emissions is federally enforceable. Secondary emissions do not count in determining the potential to emit of a stationary source.
"Reasonably attributable" means attributable by visual observation or any other technique the board deems appropriate.
"Regional haze" means visibility impairment that is caused by the emission of air pollutants from numerous sources located over a wide geographic area. Such sources include, but are not limited to, major and minor stationary sources, mobile sources, and area sources.
"Secondary emissions" means emissions that occur as a result of the construction or operation of an existing stationary facility but do not come from the existing stationary facility. Secondary emissions may include, but are not limited to, emissions from ships or trains coming to or from the existing stationary facility.
"State operating permit" means a permit issued under the Article 5 (9VAC5-80-800 et seq.) of Part II of 9VAC5-80, Permits for Stationary Sources.
"State operating permit program" means the permit program established by and codified in Article 5 (9VAC5-80-800 et seq.) of Part II of 9VAC5-80, Permits for Stationary Sources.
"Visibility-impairing pollutants" means sulfur dioxide (SO2), nitrogen oxides (NOX), and particulate matter. PM10 may be used as an indicator for particulate matter. Volatile organic compounds (VOCs) and ammonia and ammonia compounds may be considered to be visibility-impairing pollutants if the board determines that emissions of these pollutants may have an impact on visibility impairment in an area.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7580. Standard for regional haze pollutants.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any visibility-impairing pollutants in excess of emission limitations representing BART, as reflected in any term or condition that may be placed upon a permit for the facility.
B. State operating permits may be issued at the discretion of the board containing such terms and conditions, including schedules for compliance, as may be necessary to implement a BART determination under 9VAC5-40-7590 for the emissions of any visibility-impairing pollutant that may be emitted from the affected facility.
C. A permit may be issued under subsection B of this section regardless of any other permits in force provided that it does not contravene any more restrictive provision of any of the other permits.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7590. Criteria and procedures for making BART determinations.
The criteria and procedures for making BART determinations shall be as follows.
1. The determination of BART shall be based on an analysis of the best system of continuous emission control technology available and associated emission reductions achievable for each BART-eligible source that is subject to BART. In this analysis, the board will take into consideration the technology available, the costs of compliance, the energy and nonair quality environmental impacts of compliance, any pollution control equipment in use at the source, and the remaining useful life of the source, and the degree of improvement in visibility that may reasonably be anticipated to result from the use of such technology.
2. The determination of BART for fossil-fuel fired power plants having a total generating capacity greater than 750 megawatts shall be made pursuant to the guidelines in Appendix Y of 40 CFR Part 51 (see 9VAC5-20-21).
3. If the board determines in establishing BART that technological or economic limitations on the applicability of measurement methodology to a particular source would make the imposition of an emission standard infeasible, it may instead prescribe a design, equipment, work practice, or other operational standard, or combination thereof, to require the application of BART. Such standard, to the degree possible, is to set forth the emission reduction to be achieved by implementation of such design, equipment, work practice or operation, and must provide for compliance by means that achieve equivalent results.
4. Each source subject to BART shall install and operate BART as expeditiously as practicable, but in no event later than August 1, 2012.
5. Each source subject to BART shall maintain the control equipment required by this article and establish procedures to ensure such equipment is properly operated and maintained.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7600. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this part apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7610. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this part apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7620. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this part apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7630. Standard for toxic pollutants.
The provisions of Article 4 (9VAC5-60-200 et seq.) of Part II of 9VAC5-60, Hazardous Air Pollutant Sources, apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7640. Compliance.
The provisions of 9VAC5-40-20, Compliance, apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7650. Compliance schedules.
A. Owners shall comply with the emission standards in this article as expeditiously as possible but in no event later than August 1, 2012.
B. Owners of affected facilities shall comply with the provisions of subsection A of this section by adhering to the increments of progress contained in a permit issued under 9VAC5-30-7580 B.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7660. Test methods and procedures.
The provisions of 9VAC5-40-30, Emission testing, apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7670. Monitoring.
The provisions of 9VAC5-40-40, Monitoring, apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7680. Notifications, records and reporting.
The provisions of 9VAC5-40-50, Notification, records and reporting, apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7690. Registration.
The provisions of 9VAC5-20-160, Registration, apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7700. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180, Facility and control equipment maintenance or malfunction, apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
9VAC5-40-7710. Permits.
A permit may be required prior to beginning any of the activities specified below if the provisions of 9VAC5-50, New and Modified Sources, and 9VAC5-80, Permits for Stationary Sources, apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (re-startup) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172 and 182 of the Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 23, Issue 21, eff. August 1, 2007.
Article 53
Emission Standards for Lithographic Printing Processes (Rule 4-53)
9VAC5-40-7800. Applicability and designation of affected facility.
Article 53
Emission Standards for Lithographic Printing Processes (Rule 4-53)
A. Except as provided in subsections C, D, and E of this section, the affected facility to which the provisions of this article apply is each lithographic printing process that uses a substrate other than a textile.
B. The provisions of this article apply only to sources of volatile organic compounds in volatile organic compound emissions control areas designated in 9VAC5-20-206.
C. Exempted from the provisions of this article are offset lithographic printing operations in the Northern Virginia Volatile Organic Compound Emissions Control Area. Provisions applicable to offset lithographic printing operations in the Northern Virginia Volatile Organic Compound Emissions Control Area are provided in Article 56.1 (9VAC5-40-8420 et seq.) of this part.
D. Exempted from the provisions of this article are facilities in all volatile organic compound emissions control areas, other than the Northern Virginia Volatile Organic Compound Emissions Control Area, whose potential to emit is less than 100 tons per year of volatile organic compounds, provided the emission rates are determined in a manner acceptable to the board. All volatile organic compound emissions from printing inks, coatings, cleaning solutions, and fountain solutions shall be considered in applying the exemption levels specified in this subsection.
E. The provisions of this article do not apply to the following:
1. Printing processes used exclusively for determination of product quality and commercial acceptance provided:
a. The operation is not an integral part of the production process;
b. The emissions from all product quality printing processes do not exceed 400 pounds in any 30-day period; and
c. The exemption is approved by the board.
2. Photoprocessing, typesetting, or imagesetting equipment using water-based chemistry to develop silver halide images.
3. Platemaking equipment using water-based chemistry to remove unhardened image-producing material from an exposed plate.
4. Equipment used to make blueprints.
5. Any sheet-fed offset lithographic press with a cylinder width of 26 inches or less.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006; Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-7810. Definitions.
A. For the purpose of these regulations and subsequent amendments or any orders issued by the board, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meanings given them in 9VAC5 Chapter 10 (9VAC5-10-10 et seq.), unless otherwise required by context.
C. Terms defined.
"Alcohol" means any of the following compounds when used as a fountain solution additive: ethanol, n-propanol, and isopropanol.
"Alcohol substitute" means any nonalcohol additive that contains volatile organic compounds and is used in the fountain solution.
"Batch" means a supply of fountain solution that is prepared and used without alteration until completely used or removed from the printing process.
"Cleaning solution" means any blanket or roller wash used to remove ink and debris from the operating surface of a printing press.
"Composite partial vapor pressure" means the sum of the partial pressures of the compounds defined as volatile organic compounds. Composite partial vapor pressure is calculated as follows:
where:
Wi = Weight of the "i"th VOC compound, in grams.
Ww = Weight of water, in grams.
We = Weight of exempt compound, in grams.
MWi = Molecular weight of the "i"th VOC compound, in g/g-mole
MWw = Molecular weight of water, in g/g-mole
MWe = Molecular weight of exempt compound, in g/g-mole
PPc = VOC composite partial pressure at 20°C, in mm Hg.
VPi = Vapor pressure of the "i"th VOC compound at 20°C, in mm Hg.
"Fountain solution" means any mixture of water, volatile and nonvolatile chemicals, and additives applied to a lithographic plate to repel ink from the non-image area on the plate.
"Heatset" means a lithographic printing process in which heat from a dryer is used to evaporate ink oils from the substrate.
"Lithographic printing" means a planographic printing process in which the image and nonimage areas are chemically differentiated with the image area being oil-receptive and the nonimage area being water-receptive.
"Non-heatset" means a lithographic printing process in which the printing inks are set and dried by absorption or oxidation rather than heat. For the purposes of this article, UV-cured and electron beam-cured inks are considered non-heatset.
"Press" means a printing production assembly composed of one or more units to produce a printed substrate (sheet or web).
"Printing" means a photomechanical process in which a transfer of text, designs, and images occurs through contact of an image carrier with a substrate.
"Printing process" means any operation or system wherein printing ink or a combination of printing ink and surface coating is applied, dried or cured and which is subject to the same emission standard. May include any equipment which applies, conveys, dries or cures inks or surface coatings, including, but not limited to, flow coaters, flashoff areas, air dryers, drying areas and ovens. It is not necessary for a printing process to have an oven, flashoff area or drying area to be included in this definition.
"Sheet-fed" means a lithographic printing process in which individual sheets of substrate are fed into the press sequentially.
"Unit" means the smallest complete printing component, composed of an inking and dampening system, of a printing press.
"Web" means a continuous roll of printing substrate.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-7820. Standard for volatile organic compounds.
A. No owner or other person shall use or permit the use of any lithographic printing process employing a fountain solution containing volatile organic compounds unless the fountain solution as applied to each lithographic press meets the following requirements:
1. For each heatset web press:
a. When the fountain solution contains alcohol:
(1) The fountain solution shall contain no more than a daily average of 1.6% volatile organic compounds by weight; or
(2) The temperature of the fountain solution shall be maintained at or below 60°F and the fountain solution shall contain no more than a daily average of 3.0° volatile organic compounds by weight; or
b. When the fountain solution contains no alcohol, the fountain solution shall contain no more than a daily average of 5.0° volatile organic compounds by weight.
2. For each non-heatset web press and each newspaper press, the fountain solution shall contain no alcohol and shall contain no more than a daily average 5.0° volatile organic compounds by weight.
3. For each sheet-fed press:
a. The fountain solution shall contain no more than a daily average of 5.0% volatile organic compounds by weight; or
b. The temperature of the fountain solution shall be maintained at or below 60°F and the fountain solution shall contain no more than a daily average of 8.5% volatile organic compounds by weight.
B. No owner or other person shall use or permit the use of any heatset web offset lithographic printing process unless:
1. A system is installed which achieves an emission reduction from the press dryer exhaust vent of 90% by weight of volatile organic compounds (minus methane and ethane); or
2. The maximum dryer exhaust outlet concentration is maintained at 50 ppmv as carbon (minus methane and ethane).
C. No owner or other person shall use or permit the use of any lithographic printing process employing a cleaning solution containing volatile organic compounds unless:
1. The daily average of the cleaning solution as applied contains no more than 30% volatile organic compounds by weight; or
2. The daily average of the volatile organic compound portion of the cleaning solution as applied has a composite partial vapor pressure of 10 millimeters of mercury or less at 68°F (20°C).
D. All printing inks, fountain solutions, cleaning solutions, and other products containing 25% or more volatile organic compounds by weight shall be disposed of by one of the following methods:
1. Reclamation, either in-house or by outside services; or
2. Incineration.
E. All cleaning solution and applicators shall be stored in covered containers or machines with remote reservoirs when not in use.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-7830. [Reserved].
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-7840. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) shall not apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-7850. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) shall not apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-7860. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-7870. Standard for toxic pollutants.
The provisions of Article 3 (9VAC5-40-160 et seq.) of this chapter (Emission Standards for Toxic Pollutants, Rule 4-3) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-7880. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. All affected facilities in the Northern Virginia and Richmond VOC Emissions Control Areas shall be in compliance with the provisions of this rule by April 1, 1998.
C. All affected facilities in VOC emission control areas, other than the Northern Virginia and Richmond VOC Emissions Control Areas, shall be in compliance with the provisions of this rule by October 4, 2007.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110 and 182 of the Clean Air Act; 40 CFR Part 51.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996; amended, Virginia Register Volume 22, Issue 26, eff. October 4, 2006.
9VAC5-40-7890. Test methods and procedures.
A. The provisions of 9VAC5-40-30 (Emission testing) apply.
B. For the purpose of demonstrating compliance with the emission control requirements of this rule, the affected facility shall be run under typical operating conditions and flow rates compatible with scheduled production during any emission testing.
C. Emissions tests shall include an initial test within 90 days of start-up when the control device is installed and operating that demonstrates compliance with the emission standard in 9VAC5-40-7820.
D. The following reference methods (cited in 40 CFR Part 60, Appendix A) shall be used to demonstrate compliance with the emission limit or percent reduction efficiency requirement in 9VAC5-40-7820. Alternate methods may be used with the approval of the board.
1. Reference Method 1 or 1A, as appropriate, shall be used to select the sampling sites. The control device sampling sites for determining efficiency in reducing volatile organic compounds (excluding methane and ethane) from the dryer exhaust shall be placed before the control device inlet (after the dryer) and at the outlet of the control device.
2. Reference Method 2, 2A, 2C, or 2D, as appropriate, shall be used to determine the velocity and volumetric flow rate of the exhaust stream.
3. Reference Method 18, 25, or 25A shall be used to determine the volatile organic compound concentration of the exhaust stream entering and exiting the control device. Good judgment is required in determining the best applicable volatile organic compound test method for each situation. The method selected shall be based on consideration of the diversity of organic species present and their total concentration and on consideration of the potential presence of interfering gases. Because of the different response factors for the many organic compounds formed during the combustion process, only Reference Method 25, which measures volatile organic compounds as a carbon, shall be used; except in cases where the expected outlet volatile organic compound concentration of the control device is less than 100 ppmv as carbon, in which case Reference Method 25A shall be used.
a. If average, nonmethane volatile organic compound concentrations in the outlet of a thermal or catalytic oxidizer measured by Reference Method 25A are found to be greater than 100 ppmv as carbon, the board may request a repeat test to be conducted using Reference Method 18 or 25.
b. A test shall consist of three separate runs, each lasting a minimum of 60 minutes, unless the board determines that process variables dictates shorter sampling times.
c. Reference Method 25 specifies a minimum probe and temperature of 265°F. To prevent condensation, the probe should be heated to at least the gas stream temperature, typically close to 350°F.
E. The volatile organic compound content of each batch of fountain solution shall be determined by one of the following procedures:
1. Analysis by Reference Method 24 of a sample of the batch of fountain solution; or
2. Calculation which combines Reference Method 24 analytical volatile organic compound content data for the concentrated materials used to prepare the press-ready batch based on records of the proportions in which they are mixed to make the batch. The analysis of the concentrated materials may be performed by the supplier of the materials. Mix proportions may be used to determine the volatile organic compound content of the fountain solution as a substitute for Method 24 if the supplier has provided Method 24 information for the volatile organic compound content of the concentrates.
F. A thermometer or other temperature detection device capable of reading to 0.5°F shall be used to ensure that any refrigerated fountain solution recirculating reservoirs are maintained at or below 60°F at all times.
G. The volatile organic compound or volatile organic compound partial vapor pressure of each cleaning solution shall be determined by one of the following procedures:
1. Analysis by Reference Method 24 for volatile organic compound content or by an appropriate method for composite partial vapor pressure of a sample of the cleaning solution; or
2. Calculation for volatile organic compound content which combines Reference Method 24 analytical volatile organic compound content data for the concentrated materials used to prepare the press-ready batch based on records of the proportions in which they are mixed to make the batch. The analysis of the concentrated materials may be performed by the supplier of the material. Mix proportions may be used to determine the volatile organic compound content of the cleaning solution as a substitute for Method 24 if the supplier has provided Method 24 information for the volatile organic compound content of the concentrates.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-7900. Monitoring.
A. The provisions of 9VAC5-40-40 (Monitoring) apply.
B. Add-on dryer exhaust control device.
1. The owner of a subject heatset web offset lithographic printing press shall install, calibrate, maintain, and operate a temperature monitoring device according to the manufacturer's instructions at the outlet of the control device. The monitoring temperature shall be set during the testing required to demonstrate compliance with the emission standard in 9VAC5-40-7820 B. Monitoring shall be performed only when the unit is operational.
2. The temperature monitoring device shall be equipped with a continuous recorder. Both the temperature monitoring device and the continuous recorder shall have an accuracy of 0.5°F.
3. The dryer pressure shall be maintained lower than the pressroom air pressure so that air flows into the dryer at all times when the press is operating. A 100% emissions capture efficiency for the dryer shall be established using an air flow direction indicator, such as a smoke stick or aluminum ribbons.
C. Fountain solution volatile organic compound concentration.
1. The purpose of monitoring the volatile organic compound concentration in the fountain is to provide data that can be correlated to the amount of material used when the fountain solution contains alcohol and complies with the limits listed in 9VAC5-40-7820. The following methods may be used to determine the concentration of alcohol in the fountain solution in lieu of calculating the alcohol concentration using the protocol of 9VAC5-40-7890 E. The monitoring requirements of subdivisions 1 a through c of this subsection shall be required only if noncompliance with 9VAC5-40-7820 A is established.
a. The owner of any offset lithographic printing press shall monitor the alcohol concentration of the fountain solution with a refractometer that is corrected for temperature at least once for each eight-hour shift or once per batch, whichever is longer. The refractometer shall have a visual, analog, or digital readout with an accuracy of 0.5%. A standard solution shall be used to calibrate the refractometer for the type of alcohol used in the fountain. Alternatively, the refractometer shall be standardized against measurements performed to determine compliance according to the procedures described in 9VAC5-40-7890 D.
b. Alternatively, the owner of any offset lithographic printing press shall monitor fountain solution alcohol concentration with a hydrometer equipped with a temperature correction at least once for each eight-hour shift or once per batch, whichever is longer. The hydrometer shall have a visual, analog, or digital readout with an accuracy of 0.5%. A standard solution shall be used to calibrate the hydrometer for the type of alcohol used in the fountain. Alternatively, the hydrometer shall be standardized against measurements performed to determine compliance according to the procedures described in 9VAC5-40-7890 D.
c. The volatile organic compound content of the fountain solution may be monitored with a conductivity meter if it is determined that a refractometer or hydrometer cannot be used for monitoring the type of volatile organic compounds in the fountain solution. The conductivity meter reading for the fountain solution shall be referenced to the conductivity of the incoming water.
2. If, through recordkeeping for a period of six months or more, the printing process is shown to consistently meet the requirements in 9VAC5-40-7890 D, the monitoring requirement may be waived or extended to a longer period of time.
D. Fountain solution temperature.
1. The owner of any offset lithographic printing press using refrigeration equipment on the fountain shall install, maintain, and continuously operate a temperature monitor of the fountain solution reservoir.
2. The temperature on the temperature monitor shall be read and recorded at least once per operating day to verify that the refrigeration system is operating properly.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-7910. Notification, records and reporting.
A. The provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
B. The owner of any offset lithographic printing press shall record and report the following key parameters on a monthly basis:
1. The type of control device operating on the heatset offset lithographic printing press and the operating parameters specified in 9VAC5-40-7900 B;
2. The equipment standard selected to comply with the requirements listed in 9VAC5-40-7820 B;
3. The volatile organic compound content of the fountain and cleaning solutions, to comply with 9VAC5-40-7820;
4. The temperature of the fountain solution, to comply with the requirements listed in 9VAC5-40-7820 A, if applicable;
5. For manual cleaning, the amount of cleaning solution concentrate and water per batch of cleaning solution mixed;
6. For automatic cleaning, the flow rates of cleaning solution concentrate and water, as specified in 9VAC5-40-7820 C; and
7. Corrective actions taken when exceedances of any parameters monitored according to the requirements of 9VAC5-40-7890 and 9VAC5-40-7900 occur.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-7920. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-7930. Facility and control equipment maintenance of malfunction.
The provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
9VAC5-40-7940. Permits.
A permit may be required prior to beginning any of the activities specified below and the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 12, Issue 11, eff. April 1, 1996.
Article 54
Emission Standards for Large Municipal Waste Combustors (Rule 4-54)
9VAC5-40-7950. Applicability and designation of affected facility.
Article 54
Emission Standards for Large Municipal Waste Combustors (Rule 4-54)
A. Except as provided in subsections D and E of this section, the affected facility to which the provisions of this article apply is each municipal waste combustor unit with a combustion capacity greater than 250 tons per day of municipal solid waste for which construction was commenced on or before September 20, 1994.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
C. Air curtain incinerators that meet the capacity specifications in subsection A of this section and that combust municipal solid waste other than yard waste are subject to all provisions of this article.
D. Exempted from the provisions of this article are the following:
1. Any waste combustion unit that is capable of combusting more than 250 tons per day of municipal solid waste and is subject to a federally enforceable permit limiting the maximum amount of municipal solid waste that may be combusted in the unit to less than or equal to 11 tons per day is not subject to this article if the owner:
a. Notifies the board of an exemption claim;
b. Provides a copy of the federally enforceable permit that limits the firing of municipal solid waste to less than 11 tons per day; and
c. Keeps records of the amount of municipal solid waste fired on a daily basis.
2. Physical or operational changes made to an existing municipal waste combustor unit primarily for the purpose of complying with this article are not considered in determining whether the unit is a modified or reconstructed facility under subpart Ea or subpart Eb of 40 CFR Part 60.
3. A qualifying small power production facility, as defined in § 3(17)(C) of the Federal Power Act (16 USC § 796(17)(C)), that burns homogeneous waste (such as automotive tires or used oil, but not including refuse-derived fuel) for the production of electric energy is not subject to this article if the owner of the facility notifies the board of this exemption and provides data documenting that the facility qualifies for this exemption.
4. A qualifying cogeneration facility, as defined in § 3(18)(B) of the Federal Power Act (16 §USC 796(18)(B)), that burns homogeneous waste (such as automotive tires or used oil, but not including refuse-derived fuel) for the production of electric energy and steam or forms of useful energy (such as heat) that are used for industrial, commercial, heating, or cooling purposes, is not subject to this article if the owner of the facility notifies the board of this exemption and provides data documenting that the facility qualifies for this exemption.
5. Any unit combusting a single-item waste stream of tires is not subject to this article if the owner of the unit notifies the board of an exemption claim, and provides data documenting that the unit qualifies for this exemption.
6. Any cofired combustor located at a plant that meets the capacity specifications in subsection A of this section is not subject to this article if the owner of the cofired combustor:
a. Notifies the board of an exemption claim;
b. Provides a copy of the federally enforceable permit (specified in the definition of cofired combustor in 9VAC5-40-7960); and
c. Keeps a record on a calendar quarter basis of the weight of municipal solid waste combusted at the cofired combustor and the weight of all other fuels combusted at the cofired combustor.
7. Air curtain incinerators that meet the capacity specifications in subsection A of this section and that combust a fuel stream composed of 100% yard waste are exempt from all provisions of this article except the opacity limit under 9VAC5-40-8060 C, the testing procedures under 9VAC5-40-8140, and the reporting and recordkeeping provisions under 9VAC5-40-8160.
8. Pyrolysis/combustion units that are an integrated part of a plastics/rubber recycling unit are not subject to this article if the owner of the plastics/rubber recycling unit keeps records of:
a. The weight of plastics, rubber, and rubber tires, or a combination thereof, processed on a calendar quarter basis;
b. The weight of chemical plant feedstocks and petroleum refinery feedstocks produced and marketed on a calendar quarter basis; and
c. The name and address of the purchaser of the feedstocks. The combustion of gasoline, diesel fuel, jet fuel, fuel oils, residual oil, refinery gas, petroleum coke, liquefied petroleum gas, propane, or butane produced by chemical plants or petroleum refineries that use feedstocks produced by plastics/rubber recycling units are not subject to this article.
E. The provisions of this article do not apply to the following:
1. Any unit required to have a permit under § 3005 of the Solid Waste Disposal Act (42 USC § 6901 et seq.).
2. Any materials recovery facility (including primary or secondary smelters) that combusts waste for the primary purpose of recovering metals.
3. Any cement kiln firing municipal solid waste.
F. The provisions of 40 CFR Part 60 cited in this article are applicable only to the extent that they are incorporated by reference in Article 5 (9VAC5-50-400 et seq.) of Part II of 9VAC5 Chapter 50.
G. The requirement of subdivision E 1 of this section with regard to obtaining a permit under § 3005 of the Solid Waste Disposal Act (42 USC § 6901 et seq.) may be met by obtaining a permit from the department as required by 9VAC20 Chapter 60.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003.
9VAC5-40-7960. Definitions.
A. For the purpose of applying this article in the context of the Regulations for the Control and Abatement of Air Pollution and related uses, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined herein shall have the meanings given them in 9VAC5 Chapter 10, unless otherwise required by context.
C. Terms defined.
"Air curtain incinerator" means an incinerator that operates by forcefully projecting a curtain of air across an open chamber or pit in which burning occurs. Incinerators of this type can be constructed above or below ground and with or without refractory walls and floor.
"Batch municipal waste combustor" means a municipal waste combustor unit designed so that it cannot combust municipal solid waste continuously 24 hours per day because the design does not allow waste to be fed to the unit or ash to be removed while combustion is occurring.
"Bubbling fluidized bed combustor" means a fluidized bed combustor in which the majority of the bed material remains in a fluidized state in the primary combustion zone.
"Calendar quarter" means a consecutive three-month period (nonoverlapping) beginning on January 1, April 1, July 1, and October 1.
"Calendar year" means the period including 365 days (or 336 consecutive days in leap years) starting January 1 and ending on December 31.
"Chief facility operator" means the person in direct charge and control of the operation of a municipal waste combustor and who is responsible for daily onsite supervision, technical direction, management, and overall performance of the facility.
"Circulating fluidized bed combustor" means a fluidized bed combustor in which the majority of the fluidized bed material is carried out of the primary combustion zone and is transported back to the primary zone through a recirculation loop.
"Clean wood" means untreated wood or untreated wood products including clean untreated lumber, tree stumps (whole or chipped), and tree limbs (whole or chipped). Clean wood does not include yard waste, which is defined elsewhere in this section, or construction, renovation, and demolition wastes (including but not limited to railroad ties and telephone poles), which are exempt from the definition of municipal solid waste in this section.
"Cofired combustor" means a unit combusting municipal solid waste with nonmunicipal solid waste fuel (e.g., coal, industrial process waste) and subject to a federally enforceable permit limiting the unit to combusting a fuel feed stream, 30% or less of the weight of which is comprised, in aggregate, of municipal solid waste as measured on a calendar quarter basis.
"Commenced" means that an owner has undertaken a continuous program of construction or modification or that an owner has entered into a contractual obligation to undertake and complete, within a reasonable time, a continuous program of construction or modification.
"Compliance schedule" means a legally enforceable schedule specifying a date or dates by which a source or category of sources must comply with specific emission standards contained in a plan or with any increments of progress to achieve such compliance.
"Construction" means fabrication, erection, or installation of an affected facility.
"Continuous emission monitoring system" means a monitoring system for continuously measuring the emissions of a pollutant from an affected facility.
"Dioxin/furan" means tetra- through octa- chlorinated dibenzo-p-dioxins and dibenzofurans.
"First calendar half" means the period starting on January 1 and ending on June 30 in any year.
"Four-hour block average" means the average of all hourly emission concentrations when the affected facility is operating and combusting municipal solid waste measured over four-hour periods of time from midnight to 4 a.m., 4 a.m. to 8 a.m., 8 a.m. to noon, noon to 4 p.m., 4 p.m. to 8 p.m., and 8 p.m. to midnight.
"Increments of process" means steps to achieve compliance which must be taken by an owner of an affected facility, including:
1. Submittal of a final control plan for the affected facility to the board;
2. Awarding of contracts for emission control systems or for process modifications or issuance of orders for the purchase of component parts to accomplish emission control or process modification;
3. Initiation of on-site construction or installation of emission control equipment or process change;
4. Completion of on-site construction or installation or emission control equipment or process change; and
5. Final compliance.
"Mass burn refractory municipal waste combustor" means a field-erected combustor that combusts municipal solid waste in a refractory wall furnace. Unless otherwise specified, this includes combustors with a cylindrical rotary refractory wall furnace.
"Mass burn rotary waterwall municipal waste combustor" means a field-erected combustor that combusts municipal solid waste in a cylindrical rotary waterwall furnace or on a tumbling-tile grate.
"Mass burn waterwall municipal waste combustor" means a field-erected combustor that combusts municipal solid waste in a waterwall furnace.
"Materials separation plan" means a plan that identifies both a goal and an approach to separate certain components of municipal solid waste for a given service area in order to make the separated materials available for recycling. A materials separation plan may include elements such as dropoff facilities, buy-back or deposit-return incentives, curbside pickup programs, or centralized mechanical separation systems. A materials separation plan may include different goals or approaches for different subareas in the service area, and may include no materials separation activities for certain subareas or, if warranted, an entire service area.
"Maximum demonstrated municipal waste combustor unit load" means the highest four-hour arithmetic average municipal waste combustor unit load achieved during four consecutive hours during the most recent dioxin/furan emission test demonstrating compliance with the applicable limit for municipal waste combustor organics specified under 9VAC5-40-8040.
"Maximum demonstrated particulate matter control device temperature" means the highest four-hour arithmetic average flue gas temperature measured at the particulate matter control device inlet during four consecutive hours during the most recent dioxin/furan emission test demonstrating compliance with the applicable limit for municipal waste combustor organics specified under 9VAC5-40-8040.
"Modification" or "modified municipal waste combustor unit" means a municipal waste combustor unit to which changes have been made after June 19, 1996, if (i) the cumulative cost of the changes, over the life of the unit, exceed 50% of the original cost of construction and installation of the unit (not including the cost of any land purchased in connection with such construction or installation) updated to current costs or (ii) any physical change in the municipal waste combustor unit or change in the method of operation of the municipal waste combustor unit increases the amount of any air pollutant emitted by the unit for which standards have been established under § 129 or § 111 of the federal Clean Air Act. Increases in the amount of any air pollutant emitted by the municipal waste combustor unit are determined at 100% physical load capability and downstream of all air pollution control devices, with no consideration given for load restrictions based on permits or other nonphysical operational restrictions.
"Modular excess-air municipal waste combustor" means a combustor that combusts municipal solid waste and that is not field-erected and has multiple combustion chambers, all of which are designed to operate at conditions with combustion air amounts in excess of theoretical air requirements.
"Modular starved-air municipal waste combustor" means a combustor that combusts municipal solid waste and that is not field-erected and has multiple combustion chambers in which the primary combustion chamber is designed to operate at substoichiometric conditions.
"Municipal solid waste" or "municipal-type solid waste" means household, commercial/retail, and institutional waste, or a combination thereof. Household waste includes material discarded by single and multiple residential dwellings, hotels, motels, and other similar permanent or temporary housing establishments or facilities. Commercial/retail waste includes material discarded by stores, offices, restaurants, warehouses, nonmanufacturing activities at industrial facilities, and other similar establishments or facilities. Institutional waste includes material discarded by schools, nonmedical waste discarded by hospitals, material discarded by nonmanufacturing activities at prisons and government facilities, and material discarded by other similar establishments or facilities. Household, commercial/retail, and institutional waste does not include used oil; sewage sludge; wood pallets; construction, renovation, and demolition wastes (which includes but is not limited to railroad ties and telephone poles); clean wood; industrial process or manufacturing wastes; medical waste; or motor vehicles (including motor vehicle parts or vehicle fluff). Household, commercial/retail, and institutional wastes include (i) yard waste, (ii) refuse-derived fuel, and (iii) motor vehicle maintenance materials limited to vehicle batteries and tires except as specified in 9VAC5-40-7950 D 5.
"Municipal waste combustor" or "municipal waste combustor unit" means any setting or equipment that combusts solid, liquid, or gasified municipal solid waste including, but not limited to, field-erected incinerators (with or without heat recovery), modular incinerators (starved-air or excess-air), boilers (i.e., steam generating units), furnaces (whether suspension-fired, grate-fired, mass-fired, air curtain incinerators, or fluidized bed-fired), and pyrolysis/combustion units. Municipal waste combustors do not include pyrolysis/combustion units located at a plastics/rubber recycling unit (as specified in 9VAC5-40-7950 D 8). Municipal waste combustors do not include cement kilns firing municipal solid waste (as specified in 9VAC5-40-7950 E 3). Municipal waste combustors do not include internal combustion engines, gas turbines, or other combustion devices that combust landfill gases collected by landfill gas collection systems.
The boundaries of a municipal solid waste combustor are defined as follows. The municipal waste combustor unit includes, but is not limited to, the municipal solid waste fuel feed system, grate system, flue gas system, bottom ash system, and the combustor water system. The municipal waste combustor boundary starts at the municipal solid waste pit or hopper and extends through:
1. The combustor flue gas system, which ends immediately following the heat recovery equipment or, if there is no heat recovery equipment, immediately following the combustion chamber;
2. The combustor bottom ash system, which ends at the truck loading station or similar ash handling equipment that transfer the ash to final disposal, including all ash handling systems that are connected to the bottom ash handling system; and
3. The combustor water system, which starts at the feed water pump and ends at the piping exiting the steam drum or superheater.
The municipal waste combustor unit does not include air pollution control equipment, the stack, water treatment equipment, or the turbine-generator set.
"Municipal waste combustor acid gases" means all acid gases emitted in the exhaust gases from municipal waste combustor units including, but not limited to, sulfur dioxide and hydrogen chloride gases.
"Municipal waste combustor metals" means metals and metal compounds emitted in the exhaust gases from municipal waste combustor units.
"Municipal waste combustor organics" means organic compounds emitted in the exhaust gases from municipal waste combustor units and includes tetra- through octa- chlorinated dibenzo-p-dioxins and dibenzofurans.
"Municipal waste combustor plant" means one or more affected facilities (as specified in 9VAC5-40-7950) at the same location.
"Municipal waste combustor unit capacity" means the maximum charging rate of a municipal waste combustor unit expressed in tons per day of municipal solid waste combusted, calculated according to the procedures under 9VAC5-40-8100 C. 9VAC5-40-8100 C includes procedures for determining municipal waste combustor unit capacity for continuous and batch feed municipal waste combustors.
"Municipal waste combustor unit load" means the steam load of the municipal waste combustor unit measured as specified in 9VAC5-40-8150 C 6.
"Particulate matter" means total particulate matter emitted from municipal waste combustor units as measured by Reference Method 5 (see 9VAC5-40-8140 B).
"Plastics/rubber recycling unit" means an integrated processing unit where plastics, rubber, and rubber tires, or a combination thereof, are the only feed materials (incidental contaminants may be included in the feed materials) and they are processed into a chemical plant feedstock or petroleum refinery feedstock, where the feedstock is marketed to and used by a chemical plant or petroleum refinery as input feedstock. The combined weight of the chemical plant feedstock and petroleum refinery feedstock produced by the plastics/rubber recycling unit on a calendar quarter basis shall be more than 70% of the combined weight of the plastics, rubber, and rubber tires processed by the plastics/rubber recycling unit on a calendar quarter basis. The plastics, rubber, or rubber tire feed materials to the plastics/rubber recycling unit may originate from the separation or diversion of plastics, rubber, or rubber tires from MSW or industrial solid waste, and may include manufacturing scraps, trimmings, and off-specification plastics, rubber, and rubber tire discards. The plastics, rubber, and rubber tire feed materials to the plastics/rubber recycling unit may contain incidental contaminants (e.g., paper labels on plastic bottles, metal rings on plastic bottle caps, etc.).
"Potential hydrogen chloride emission concentration" means the hydrogen chloride emission concentration that would occur from combustion of municipal solid waste in the absence of any emission controls for municipal waste combustor acid gases.
"Potential mercury emission concentration" means the mercury emission concentration that would occur from combustion of municipal solid waste in the absence of any mercury emissions control.
"Potential sulfur dioxide emissions" means the sulfur dioxide emission concentration that would occur from combustion of municipal solid waste in the absence of any emission controls for municipal waste combustor acid gases.
"Pulverized coal/refuse-derived fuel mixed fuel-fired combustor" means a combustor that fires coal and refuse-derived fuel simultaneously, in which pulverized coal is introduced into an air stream that carries the coal to the combustion chamber of the unit where it is fired in suspension. This includes both conventional pulverized coal and micropulverized coal.
"Pyrolysis/combustion unit" means a unit that produces gases, liquids, or solids through the heating of municipal solid waste, and the gases, liquids, or solids produced are combusted and emissions vented to the atmosphere.
"Reconstruction" means rebuilding a municipal waste combustor unit for which the reconstruction commenced after June 19, 1996, and the cumulative costs of the construction over the life of the unit exceed 50% of the original cost of construction and installation of the unit (not including any cost of land purchased in connection with such construction or installation) updated to current costs (current dollars).
"Refractory unit" or "refractory wall furnace" means a combustion unit having no energy recovery (e.g., via a waterwall) in the furnace (i.e., radiant heat transfer section) of the combustor.
"Refuse-derived fuel" means a type of municipal solid waste produced by processing municipal solid waste through shredding and size classification. This includes all classes of refuse-derived fuel including low-density fluff refuse-derived fuel through densified refuse-derived fuel and pelletized refuse-derived fuel.
"Refuse-derived fuel stoker" means a steam generating unit that combusts refuse-derived fuel in a semisuspension firing mode using air-fed distributors.
"Same location" means the same or contiguous property that is under common ownership or control including properties that are separated only by a street, road, highway, or other public right-of-way. Common ownership or control includes properties that are owned, leased, or operated by the same entity, parent entity, subsidiary, subdivision, or any combination thereof including any municipality or other governmental unit, or any quasi-governmental authority (e.g., a public utility district or regional waste disposal authority).
"Second calendar half" means the period starting July 1 and ending on December 31 in any year.
"Shift supervisor" means the person who is in direct charge and control of the operation of a municipal waste combustor and who is responsible for onsite supervision, technical direction, management, and overall performance of the facility during an assigned shift.
"Spreader stoker coal/refuse-derived fuel mixed fuel-fired combustor" means a combustor that fires coal and refuse-derived fuel simultaneously, in which coal is introduced to the combustion zone by a mechanism that throws the fuel onto a grate from above. Combustion takes place both in suspension and on the grate.
"Standard conditions" means a temperature of 20 degrees Centigrade and a pressure of 101.3 kilopascals.
"Total mass dioxin/furan" or "total mass" means the total mass of tetra- through octa- chlorinated dibenzo-p-dioxins and dibenzofurans, as determined using Reference Method 23 and the procedures specified under 9VAC5-40-8140 F.
"Tumbling-tile" means a grate tile hinged at one end and attached to a ram at the other end. When the ram extends, the grate tile rotates around the hinged edge.
"Twenty-four-hour daily average" means either the arithmetic mean or geometric mean (as specified) of all hourly emission concentrations when the affected facility is operating and combusting municipal solid waste measured over a 24-hour period between midnight and the following midnight.
"Untreated lumber" means wood or wood products that have been cut or shaped and include wet, air-dried, and kiln-dried wood products. Untreated lumber does not include wood products that have been painted, pigment-stained, or "pressure-treated." Pressure-treating compounds include, but are not limited to, chromate copper arsenate, pentachlorophenol, and creosote.
"Waterwall furnace" means a combustion unit having energy (heat) recovery in the furnace (i.e., radiant heat transfer section) of the combustor.
"Yard waste" means grass, grass clippings, bushes, shrubs, and clippings from bushes and shrubs that are generated by residential, commercial/retail, institutional, and industrial sources, or combination thereof, as part of maintenance activities associated with yards or other private or public lands. Yard waste does not include construction, renovation, and demolition wastes, which are exempt from the definition of municipal solid waste in this section. Yard waste does not include clean wood, which is exempt from the definition of municipal solid waste in this section.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003.
9VAC5-40-7970. Standard for particulate matter.
No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any gases that contain particulate matter in excess of 27 milligrams per dry standard cubic meter, corrected to 7.0% oxygen.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999.
9VAC5-40-7980. Standard for carbon monoxide.
No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any gases that contain carbon monoxide in excess of the following limits:
1. For mass burn waterwall units: 100 parts per million by volume, corrected to 7.0% oxygen, dry basis, calculated as an arithmetic average (four-hour average).
2. For mass burn refractory units: 100 parts per million by volume, corrected to 7.0% oxygen, dry basis, calculated as an arithmetic average (four-hour average).
3. For mass burn rotary refractory units: 100 parts per million by volume, corrected to 7.0% oxygen, dry basis, calculated as an arithmetic average (24-hour average).
4. For mass burn rotary waterwall units: 250 parts per million by volume, corrected to 7.0% oxygen, dry basis, calculated as an arithmetic average (24-hour average).
5. For modular starved air units: 50 parts per million by volume, corrected to 7.0% oxygen, dry basis, calculated as an arithmetic average (four-hour average).
6. For modular excess air units: 50 parts per million by volume, corrected to 7.0% oxygen, dry basis, calculated as an arithmetic average (four-hour average).
7. For refuse-derived fuel stokers: 200 parts per million by volume, corrected to 7.0% oxygen, dry basis, calculated as an arithmetic average (24-hour average).
8. For bubbling fluidized bed combustors: 100 parts per million by volume, corrected to 7.0% oxygen, dry basis, calculated as an arithmetic average (four-hour average).
9. For circulating fluidized bed combustors: 100 parts per million by volume, corrected to 7.0% oxygen, dry basis, calculated as an arithmetic average (four-hour average).
10. For pulverized coal/refuse-derived fuel mixed fuel-fired combustors: 150 parts per million by volume, corrected to 7.0% oxygen, dry basis, calculated as an arithmetic average (four-hour average).
11. For spreader stoker coal/refuse-derived fuel mixed fuel-fired combustors: 200 parts per million by volume, corrected to 7.0% oxygen, dry basis, calculated as an arithmetic average (24-hour average).
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999.
9VAC5-40-7990. Standard for cadmium.
No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any gases that contain cadmium in excess of 0.040 milligrams per dry standard cubic meter, corrected to 7.0% oxygen.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999.
9VAC5-40-8000. Standard for lead.
No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any gases that contain lead in excess of 0.44 milligrams per dry standard cubic meter, corrected to 7.0% oxygen.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999.
9VAC5-40-8010. Standard for mercury.
No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any gases that contain mercury in excess of 0.080 milligrams per dry standard cubic meter or 15% of the potential mercury emission concentration (85% reduction by weight), corrected to 7.0% oxygen, whichever is less stringent.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999.
9VAC5-40-8020. Standard for sulfur dioxide.
No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any gases that contain sulfur dioxide in excess of 29 parts per million by volume or 25% of the potential sulfur dioxide emission concentration (75% reduction by weight or volume), corrected to 7.0% oxygen (dry basis), whichever is less stringent. Compliance with this emission limit is based on a 24-hour daily geometric mean.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999.
9VAC5-40-8030. Standard for hydrogen chloride.
No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any gases that contain hydrogen chloride in excess of 29 parts per million by volume or 5.0% of the potential hydrogen chloride emission concentration (95% reduction by weight or volume), corrected to 7.0% oxygen (dry basis), whichever is less stringent.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999.
9VAC5-40-8040. Standard for dioxin/furan.
No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any gases that contain municipal waste combustor organics, expressed as total mass dioxins/furans, in excess of the following limits:
1. For facilities that employ an electrostatic precipitator-based emission control system, 60 nanograms per dry standard cubic meter (total mass), corrected to 7.0% oxygen.
2. For facilities that do not employ an electrostatic precipitator-based emission control system, 30 nanograms per dry standard cubic meter (total mass), corrected to 7.0% oxygen.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999.
9VAC5-40-8050. Standard for nitrogen oxides.
No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any gases that contain nitrogen oxides in excess of the following limits:
1. For facilities not engaged in an emissions averaging plan as described in 9VAC5-40-8100 D:
a. For mass burn waterwall units: 205 parts per million by volume corrected to 7.0% oxygen, dry basis.
b. For mass burn rotary waterwall units: 250 parts per million by volume corrected to 7.0% oxygen, dry basis.
c. For refuse-derived fuel combustors: 250 parts per million by volume corrected to 7.0% oxygen, dry basis.
d. For fluidized bed combustors: 180 parts per million by volume corrected to 7.0% oxygen, dry basis.
e. For mass burn refractory combustors: no limit.
2. For facilities engaged in an emissions averaging plan as described in 9VAC5-40-8100 D:
a. For mass burn waterwall units: 185 parts per million by volume, corrected to 7.0% oxygen, dry basis.
b. For mass burn rotary waterwall units: 220 parts per million by volume, corrected to 7.0% oxygen, dry basis.
c. For refuse-derived fuel combustors: 230 parts per million by volume, corrected to 7.0% oxygen, dry basis.
d. For fluidized bed combustors: 165 parts per million by volume, corrected to 7.0% oxygen, dry basis.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999.
9VAC5-40-8060. Standard for visible emissions.
A. The provisions of Article 1 (9VAC5-40-60 et seq.) of 9VAC5 Chapter 40 (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply except that the provisions in subsections B and C of this section apply instead of 9VAC5-40-80.
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any affected facility any gases that exhibit greater than 10% opacity (6-minute average).
C. The owner of an air curtain incinerator with the capacity to combust greater than 250 tons per day of municipal solid waste and that combusts a fuel feed stream composed of 100% yard waste and no other municipal solid waste materials shall at no time cause to be discharged into the atmosphere from that incinerator any gases that exhibit greater than 10% opacity (6-minute average), except that an opacity level of up to 35% (6-minute average) is permitted during startup periods during the first 30 minutes of operation of the unit.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999.
9VAC5-40-8070. Standard for fugitive dust/emissions.
A. The provisions of Article 1 (9VAC5-40-60 et seq.) of 9VAC5 Chapter 40 (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply except as provided in subsections B through D of this section.
B. No owner or other person shall cause to be discharged to the atmosphere visible emissions of combustion ash from an ash conveying system (including conveyor transfer points) in excess of 5.0% of the observation period (i.e., 9 minutes per 3-hour period), as determined by Reference Method 22 observations as specified in 9VAC5-40-8140 H, except as provided in subsections C and D of this section.
C. The emission limit specified in subsection B of this section shall not cover visible emissions discharged inside buildings or enclosures of ash conveying systems; however, the emission limit specified in subsection B of this section shall cover visible emissions discharged to the atmosphere from buildings or enclosures of ash conveying systems.
D. The provisions specified in subsection B of this section shall not apply during maintenance and repair of ash conveying systems.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999.
9VAC5-40-8080. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of 9VAC5 Chapter 40 (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999.
9VAC5-40-8090. Standard for toxic pollutants.
The provisions of Article 4 (9VAC5-60-200 et seq.) of 9VAC5 Chapter 60 (Emission Standards for Toxic Pollutants, Rule 6-4) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003.
9VAC5-40-8100. Compliance.
A. The provisions governing compliance shall be as follows:
1. With regard to the emissions standards in 9VAC5-40-8080 and 9VAC5-40-8090, the provisions of 9VAC5-40-20 (Compliance), apply.
2. With regard to the emission limits in 9VAC5-40-7970 through 9VAC5-40-8070, the following provisions apply:
a. 9VAC5-40-20 B, C, D, and E.
b. 40 CFR 60.11.
c. Subsections B through F of this section.
B. The provisions for startup, shutdown, and malfunction in subdivisions 1 and 2 of this subsection apply. Test methods and procedures for determining compliance shall be performed as specified in 9VAC5-40-8140.
1. Except as provided by 9VAC5-40-8060 C, the standards under this article apply at all times except during periods of startup, shutdown, or malfunction. Duration of startup, shutdown, or malfunction periods are limited to three hours per occurrence, except as provided in subdivision 1 c of this subsection.
a. The startup period commences when the affected facility begins the continuous burning of municipal solid waste and does not include any warmup period when the affected facility is combusting fossil fuel or other nonmunicipal solid waste fuel, and no municipal solid waste is being fed to the combustor.
b. Continuous burning is the continuous, semicontinuous, or batch feeding of municipal solid waste for purposes of waste disposal, energy production, or providing heat to the combustion system in preparation for waste disposal or energy production. The use of municipal solid waste solely to provide thermal protection of the grate or hearth during the startup period when municipal solid waste is not being fed to the grate is not considered to be continuous burning.
c. For the purpose of compliance with the carbon monoxide emission limits in 9VAC5-40-7980, if a loss of boiler water level control (e.g., boiler waterwall tube failure) or a loss of combustion air control (e.g., loss of combustion air fan, induced draft fan, combustion grate bar failure) is determined to be a malfunction, the duration of the malfunction period is limited to 15 hours per occurrence.
2. The opacity limits for air curtain incinerators specified in 9VAC5-40-8060 apply at all times as specified under 9VAC5-40-8060 except during periods of malfunction. Duration of malfunction periods are limited to three hours per occurrence.
C. The procedures specified in subdivisions 1 and 2 of this subsection shall be used for calculating municipal waste combustor unit capacity.
1. For municipal waste combustor units capable of combusting municipal solid waste continuously for a 24-hour period, municipal waste combustor unit capacity shall be calculated based on 24 hours of operation at the maximum charging rate. The maximum charging rate shall be determined as specified in subdivisions 1 a and 1 b of this subsection as applicable.
a. For combustors that are designed based on heat capacity, the maximum charging rate shall be calculated based on the maximum design heat input capacity of the unit and a heating value of 12,800 kilojoules per kilogram for combustors firing refuse-derived fuel and a heating value of 10,500 kilojoules per kilogram for combustors firing municipal solid waste that is not refuse-derived fuel.
b. For combustors that are not designed based on heat capacity, the maximum charging rate shall be the maximum design charging rate.
2. For batch feed municipal waste combustor units, municipal waste combustor unit capacity shall be calculated as the maximum design amount of municipal solid waste that can be charged per batch multiplied by the maximum number of batches that could be processed in a 24-hour period. The maximum number of batches that could be processed in a 24-hour period is calculated as 24 hours divided by the design number of hours required to process one batch of municipal solid waste, and may include fractional batches (e.g., if one batch requires 16 hours, then 24/16, or 1.5 batches, could be combusted in a 24-hour period). For batch combustors that are designed based on heat capacity, the design heating value of 12,800 kilojoules per kilogram for combustors firing refuse-derived fuel and a heating value of 10,500 kilojoules per kilogram for combustors firing municipal solid waste that is not refuse-derived fuel.
D. Nitrogen oxides emissions averaging is allowed as specified in this subsection.
1. The owner of a municipal waste combustor plant may elect to implement a nitrogen oxides emissions averaging plan for the affected facilities that are located at that plant and that are subject to this article, except as specified in subdivisions 1 a and 1 b of this subsection.
a. Municipal waste combustor units subject to subpart Ea or subpart Eb of 40 CFR Part 60 cannot be included in the emissions averaging plan.
b. Mass burn refractory municipal waste combustor units and other municipal waste combustion technologies not listed in 9VAC5-40-8050 B cannot be included in the emissions averaging plan.
2. The affected facilities included in the nitrogen oxides emissions averaging plan must be identified in the initial compliance report specified in 9VAC5-40-8160 J or in the annual report specified in 9VAC5-40-8160 D, as applicable, prior to implementing the averaging plan. The affected facilities being included in the averaging plan may be redesignated each calendar year. Partial year redesignation is allowable with board approval.
3. To implement the emissions averaging plan, the average daily (24-hour) nitrogen oxides emission concentration level for gases discharged from the affected facilities being included in the emissions averaging plan must be no greater than the levels specified in 9VAC5-40-8050 B.
4. Under the emissions averaging plan, the average daily nitrogen oxides emissions specified in 9VAC5-40-8050 B shall be calculated using the following equation. Affected facilities that are offline shall not be included in calculating the average daily nitrogen oxides emission level.
For Compliance, see Virginia Administrative Code print product.
5. For any day in which any affected facility included in the emissions averaging plan is offline, the owner of the municipal waste combustor plant must demonstrate compliance according to either subdivision 5 a of this subsection or both subdivisions 5 b and 5 c of this subsection.
a. Compliance with the applicable limits specified in 9VAC5-40-8050 B shall be demonstrated using the averaging procedure specified in subdivision 4 of this subsection for the affected facilities that are online.
b. For each of the affected facilities included in the emissions averaging plan, the nitrogen oxides emissions on a daily average basis shall be calculated and shall be equal to or less than the maximum daily nitrogen oxides emission level achieved by that affected facility on any of the days during which the emissions averaging plan was achieved with all affected facilities online during the most recent calendar quarter. The requirements of this subsection do not apply during the first quarter of operation under the emissions averaging plan.
c. The average nitrogen oxides emissions (kilograms per day) calculated according to subdivision 5 c (2) of this subsection shall not exceed the average nitrogen oxides emissions (kilograms per day) calculated according to subdivision 5 c (1) of this subsection.
(1) For all days during which the emissions averaging plan was implemented and achieved and during which all affected facilities were online, the average nitrogen oxides emissions shall be calculated. The average nitrogen oxides emissions (kilograms per day) shall be calculated on a calendar year basis according to subdivisions 5 c (1) (a) through 5 c (1) (c) of this subsection.
(a) For each affected facility included in the emissions averaging plan, the daily amount of nitrogen oxides emitted (kilograms per day) shall be calculated based on the hourly nitrogen oxides data specified under 9VAC5-40-8140 G 5, the flue gas flow rate determined using Table 19-1 of Reference Method 19 or a board-approved method, and the hourly average steam or feedwater flow rate.
(b) The daily total nitrogen oxides emissions shall be calculated as the sum of the daily nitrogen oxides emissions from each affected facility calculated under subdivision 5 c (1) (a) of this subsection.
(c) The average nitrogen oxides emissions (kilograms per day) on a calendar year basis shall be calculated as the sum of all daily total nitrogen oxides emissions calculated under subdivision 5 c (1) (b) of this subsection divided by the number of calendar days for which a daily total was calculated.
(2) For all days during which one or more of the affected facilities under the emissions averaging plan was offline, the average nitrogen oxides emissions shall be calculated. The average nitrogen oxides emissions (kilograms per day) shall be calculated on a calendar year basis according to subdivisions 5 c (2) (a) through 5 c (2) (c) of this subsection.
(a) For each affected facility included in the emissions averaging plan, the daily amount of nitrogen oxides emitted (kilograms per day) shall be calculated based on the hourly nitrogen oxides data specified under 9VAC5-40-8140 G 5, the flue gas flow rate determined using Table 19-1 of Reference Method 19, and the hourly average steam or feedwater flow rate.
(b) The daily total nitrogen oxides emissions shall be calculated as the sum of the daily nitrogen oxides emissions from each affected facility calculated under subdivision 5 c (2) (a) of this subsection.
(c) The average nitrogen oxides emissions (kilograms per day) on a calendar year basis shall be calculated as the sum of all daily total nitrogen oxides emissions calculated under subdivision 5 c (2) (b) of this subsection divided by the number of calendar days for which a daily total was calculated.
E. Owners of municipal waste combustor plants may engage in trading of nitrogen oxides emission credits. A trading program must be approved by the board before implementation.
F. The initial emission test shall be completed within 180 days after the final compliance date specified in 9VAC5-40-8110 A.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003.
9VAC5-40-8110. Compliance schedules.
A. The compliance schedule provisions of 40 CFR 62.14108 (40 CFR, July 1, 2002) and 40 CFR 62.14109(e) through (m) (40 CFR, July 1, 2002) apply.
B. All affected sources shall comply with the municipal waste combustor operator training and certification requirements under 9VAC5-40-8130 according to the schedule specified in subdivisions 1 and 2 of this subsection.
1. Affected facilities shall comply with the municipal waste combustor operator training and certification requirements specified in 9VAC5-40-8130 A through D by August 4, 2000.
2. Affected facilities shall comply with the requirements specified in 9VAC5-40-8130 E through H no later than August 4, 2000.
a. The requirement specified in 9VAC5-40-8130 E does not apply to chief facility operators, shift supervisors, and control room operators who have obtained full certification from the American Society of Mechanical Engineers on or before the effective date of this article.
b. The owner of an affected facility may request that the board waive the requirement specified in 9VAC5-40-8130 E for chief facility operators, shift supervisors, and control room operators who have obtained provisional certification from the American Society of Mechanical Engineers on or before the effective date of this article.
c. The initial training requirements specified in 9VAC5-40-8130 G 1 shall be completed no later than the date specified in subdivision 2 c (1) or 2 c (2) of this subsection, whichever is later.
(1) August 4, 2000; or
(2) The date prior to the day when the person assumes responsibilities affecting municipal waste combustor unit operation.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003.
9VAC5-40-8120. Operating practices.
A. No owner of an affected facility shall cause such facility to operate at a load level greater than 110% of the maximum demonstrated municipal waste combustor unit load, except as specified in subdivisions 1 and 2 of this subsection. The averaging time is specified under 9VAC5-40-8150 C.
1. During the annual dioxin/furan emission test and the two weeks preceding the annual dioxin/furan emission test, no municipal waste combustor unit load limit is applicable.
2. The municipal waste combustor unit load limit may be waived in accordance with permission granted by the board for the purpose of evaluating system performance, testing new technology or control technologies, diagnostic testing, or related activities for the purpose of improving facility performance or advancing the state-of-the-art for controlling facility emissions.
B. No owner of an affected facility shall cause such facility to operate at a temperature, measured at the particulate matter control device inlet, exceeding 17 degrees Centigrade above the maximum demonstrated particulate matter control device temperature as defined in 9VAC5-40-7960, except as specified in subdivisions 1 and 2 of this subsection. The averaging time is specified under 9VAC5-40-8150 C. The requirements specified in this subsection apply to each particulate matter control device utilized at the affected facility.
1. During the annual dioxin/furan emission test and the two weeks preceding the annual dioxin/furan emission test, no particulate matter control device temperature limitations are applicable.
2. The particulate matter control device temperature limits may be waived in accordance with permission granted by the board for the purpose of evaluating system performance, testing new technology or control technologies, diagnostic testing, or related activities for the purpose of improving facility performance or advancing the state-of-the-art for controlling facility emissions.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003.
9VAC5-40-8130. Operator training and certification.
A. Each chief facility operator and shift supervisor of an affected facility shall obtain and maintain a current provisional operator training certification from the American Society of Mechanical Engineers as provided in the "Standard for the Qualification and Certification of Resource Recovery Facility Operators" (see 9VAC5-20-21) or a board-approved certification program.
B. Each chief facility operator and shift supervisor of an affected facility shall have completed full certification or scheduled a full certification exam with either the American Society of Mechanical Engineers as provided in the "Standard for the Qualification and Certification of Resource Recovery Facility Operators" (see 9VAC5-20-21) or a board-approved certification program.
C. No owner of an affected facility shall allow the facility to be operated at any time unless a person is on duty who is responsible for the proper operation of the facility and has a license from the Board for Waste Management Facility Operators in the correct classification. No provision of this article shall relieve any owner from the responsibility to comply in all respects with the requirements of Chapter 22.1 (§ 54.1-2209 et seq.) of Title 54.1 of the Code of Virginia, and with 18VAC155 Chapter 20.
D. No owner of an affected facility shall allow the facility to be operated at any time unless one of the following persons is on duty and at the affected facility: a fully certified chief facility operator, a provisionally certified chief facility operator who is scheduled to take the full certification exam according to the schedule specified in 9VAC5-40-8110 B 1, a fully certified shift supervisor, or a provisionally certified shift supervisor who is scheduled to take the full certification exam according to the schedule specified in 9VAC5-40-8110 B 1.
If one of the persons listed in this subsection must leave the affected facility during that person's operating shift, a provisionally certified control room operator who is onsite at the affected facility may fulfill the requirement in this subsection.
E. All chief facility operators, shift supervisors, and control room operators at affected facilities must complete the board-approved municipal waste combustor operator training course.
F. The owner of an affected facility shall develop and update on a yearly basis a site-specific operating manual that shall, at a minimum, address the elements of municipal waste combustor unit operation specified in this subsection.
1. A summary of the applicable standards under this article;
2. A description of basic combustion theory applicable to a municipal waste combustor unit;
3. Procedures for receiving, handling, and feeding municipal solid waste;
4. Municipal waste combustor unit startup, shutdown, and malfunction procedures;
5. Procedures for maintaining proper combustion air supply levels;
6. Procedures for operating the municipal waste combustor unit within the standards established under this article;
7. Procedures for responding to periodic upset or off-specification conditions;
8. Procedures for minimizing particulate matter carryover;
9. Procedures for handling ash;
10. Procedures for monitoring municipal waste combustor unit emissions; and
11. Reporting and recordkeeping procedures.
G. The owner of an affected facility shall establish a training program to review the operating manual according to the schedule specified in this subsection with each person who has responsibilities affecting the operation of an affected facility including, but not limited to, chief facility operators, shift supervisors, control room operators, ash handlers, maintenance personnel, and crane/load handlers.
1. Each person specified in this subsection shall undergo initial training no later than the date specified in subdivision 1 a or 1 b of this subsection, whichever is later.
a. The date prior to the day the person assumes responsibilities affecting municipal waste combustor unit operation; or
b. August 4, 2000.
2. Each person specified in this subsection shall undergo initial training annually, following the initial review required by subdivision 1 of this subsection.
H. The operating manual required by subsection F of this section shall be kept in a readily accessible location for all persons required to undergo training under subsection G of this section. The operating manual and records of training shall be available for inspection by the board upon request.
I. The requirements of subsections A and B of this section with regard to obtaining operator training certification through a program approved by the board may be met by obtaining a license from the Board for Waste Management Facility Operators. All training and licensing shall be conducted in accordance with Chapter 22.1 (§ 54.1-2209 et seq.) of Title 54.1 of the Code of Virginia, and with 18VAC155 Chapter 20.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999; amended, Virginia Register Volume 18, Issue 7, eff. February 1, 2002; Volume 19, Issue 17, eff. July 1, 2003.
9VAC5-40-8140. Test methods and procedures.
A. The provisions governing test methods and procedures shall be as follows:
1. With regard to the emissions standards in 9VAC5-40-8080 and 9VAC5-40-8090, the provisions of 9VAC5-40-30 (Emission testing) apply.
2. With regard to the emission limits in 9VAC5-40-7970 through 9VAC5-40-8070, the following provisions apply:
a. 9VAC5-40-30 D and G.
b. 40 CFR 60.8, with the exception of paragraph (a).
c. 40 CFR 60.11 and 40 CFR 60.13.
d. Subsections B through J of this section.
B. The procedures and test methods specified in this subsection shall be used to determine compliance with the emission limits for particulate matter and opacity under 9VAC5-40-7970 and 9VAC5-40-8060.
1. Reference Method 1 shall be used to select sampling site and number of traverse points.
2. Reference Method 3, 3A, or 3B, as applicable, shall be used for gas analysis.
3. Reference Method 5 shall be used for determining compliance with the particulate matter emission limit. The minimum sample volume shall be 1.7 cubic meters. The probe and filter holder heating systems in the sample train shall be set to provide a gas temperature no greater than 160 ± 14 degrees Centigrade. An oxygen or carbon dioxide measurement shall be obtained simultaneously with each Reference Method 5 run.
4. The owner of an affected facility may request that compliance with the particulate matter emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7.0% oxygen. The relationship between oxygen and carbon dioxide levels for the affected facility shall be established as specified in 9VAC5-40-8150 B 6.
5. As specified in 40 CFR 60.8, all emission tests shall consist of three test runs. The average of the particulate matter emission concentrations from the three test runs is used to determine compliance.
6. In accordance with subdivisions 7 and 10 of this subsection, Reference Method 9 shall be used for determining compliance with the opacity limit except as provided in 40 CFR 60.11(e).
7. The owner of an affected facility shall conduct an initial emission test for particulate matter emissions and opacity as required in 9VAC5-40-8100.
8. The owner of an affected facility shall install, calibrate, maintain, and operate a continuous opacity monitoring system for measuring opacity and shall follow the methods and procedures specified in subdivisions 8 a through 8 d of this subsection.
a. The output of the continuous opacity monitoring system shall be recorded on a 6-minute average basis.
b. The continuous opacity monitoring system shall be installed, evaluated, and operated in accordance with 40 CFR 60.13.
c. The continuous opacity monitoring system shall conform to Performance Specification 1 in Appendix B of 40 CFR Part 60.
d. The initial performance evaluation shall be completed as specified in 9VAC5-40-8100.
9. Following the date that the initial emission test for particulate matter is completed or is required to be completed in 9VAC5-40-8100 for an affected facility, the owner shall conduct an emission test for particulate matter on an annual basis (no more than 12 calendar months following the previous emission test).
10. Following the date that the initial emission test for opacity is completed or is required to be completed in 9VAC5-40-8100 for an affected facility, the owner shall conduct an emission test for opacity on an annual basis (no more than 12 calendar months following the previous emission test) using the test method specified in subdivision 6 of this subsection.
C. The procedures and test methods specified in this subsection shall be used to determine compliance with the emission limits for cadmium, lead, and mercury under 9VAC5-40-7990, 9VAC5-40-8000, and 9VAC5-40-8010.
1. The procedures and test methods specified in subdivisions 1 a through 1 g of this subsection shall be used to determine compliance with the emission limits for cadmium and lead under 9VAC5-40-7990 and 9VAC5-40-8000.
a. Reference Method 1 shall be used for determining the location and number of sampling points.
b. Reference Method 3, 3A, or 3B, as applicable, shall be used for flue gas analysis.
c. Reference Method 29 shall be used for determining compliance with the cadmium and lead emission limits.
d. An oxygen or carbon dioxide measurement shall be obtained simultaneously with each Reference Method 29 test run for cadmium and lead required under subdivision 1 c of this subsection.
e. The owner of an affected facility may request that compliance with the cadmium or lead emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7.0% oxygen. The relationship between oxygen and carbon dioxide levels for the affected facility shall be established as specified in 9VAC5-40-8150 B 6.
f. All emission tests shall consist of a minimum of three test runs conducted under representative full load operating conditions. The average of the cadmium or lead emission concentrations from three test runs or more shall be used to determine compliance.
g. Following the date of the initial emission test or the date on which the initial emission test is required to be completed in 9VAC5-40-8100, the owner of an affected facility shall conduct an emission test for compliance with the emission limits for cadmium and lead on an annual basis (no more than 12 calendar months following the previous emission test).
2. The procedures and test methods specified in subdivisions 2 a through 2 j of this subsection shall be used to determine compliance with the mercury emission limit under 9VAC5-40-8010.
a. Reference Method 1 shall be used for determining the location and number of sampling points.
b. Reference Method 3, 3A, or 3B, as applicable, shall be used for flue gas analysis.
c. Reference Method 29 shall be used to determine the mercury emission concentration. The minimum sample volume when using Reference Method 29 for mercury shall be 1.7 cubic meters.
d. An oxygen (or carbon dioxide) measurement shall be obtained simultaneously with each Reference Method 29 test run for mercury required under subdivision 2 c of this subsection.
e. The percent reduction in the potential mercury emissions (% pHg) is computed using the following equation:
where:
%PHg = percent reduction of the potential mercury emissions achieved.
Ei = potential mercury emission concentration measured at the control device inlet, corrected to 7.0% oxygen (dry basis).
EO = controlled mercury emission concentration measured at the mercury control device outlet, corrected to 7.0% oxygen (dry basis).
f. All emission tests shall consist of a minimum of three test runs conducted under representative full load operating conditions. The average of the mercury emission concentrations or percent reductions from three test runs or more is used to determine compliance.
g. The owner of an affected facility may request that compliance with the mercury emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7.0% oxygen. The relationship between oxygen and carbon dioxide levels for the affected facility shall be established as specified in 9VAC5-40-8150 B 6.
h. The owner of an affected facility shall conduct an initial emission test for mercury emissions as required in 9VAC5-40-8100.
i. Following the date that the initial emission test for mercury is completed or is required to be completed in 9VAC5-40-8100, the owner of an affected facility shall conduct an emission test for mercury emissions on an annual basis (no more than 12 calendar months from the previous emission test).
j. The owner of an affected facility where activated carbon injection is used to comply with the mercury emission limit shall follow the procedures specified in subsection J of this section for measuring and calculating carbon usage.
D. The procedures and test methods specified in this subsection shall be used for determining compliance with the sulfur dioxide emission limit under 9VAC5-40-8020.
1. Reference Method 19, section 4.3, shall be used to calculate the daily geometric average sulfur dioxide emission concentration.
2. Reference Method 19, section 5.4, shall be used to determine the daily geometric average percent reduction in the potential sulfur dioxide emission concentration.
3. The owner of an affected facility may request that compliance with the sulfur dioxide emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7.0% oxygen. The relationship between oxygen and carbon dioxide levels for the affected facility shall be established as specified in 9VAC5-40-8150 B 6.
4. The owner of an affected facility shall conduct an initial emission test for sulfur dioxide emissions as required in 9VAC5-40-8100. Compliance with the sulfur dioxide emission limit (concentration or percent reduction) shall be determined by using the continuous emission monitoring system specified in subdivision 5 of this subsection to measure sulfur dioxide and calculating a 24-hour daily geometric average emission concentration or a 24-hour daily geometric average percent reduction using Reference Method 19, sections 4.3 and 5.4, as applicable.
5. The owner of an affected facility shall install, calibrate, maintain, and operate a continuous emission monitoring system for measuring sulfur dioxide emissions discharged to the atmosphere and record the output of the system.
6. Following the date that the initial emission test for sulfur dioxide is completed or is required to be completed in 9VAC5-40-8100, compliance with the sulfur dioxide emission limit shall be determined based on the 24-hour daily geometric average of the hourly arithmetic average emission concentrations using continuous emission monitoring system outlet data if compliance is based on an emission concentration, or continuous emission monitoring system inlet and outlet data if compliance is based on a percent reduction.
7. At a minimum, valid continuous monitoring system hourly averages shall be obtained as specified in subdivisions 7 a and 7 b of this subsection for 75% of the operating hours per day for 90% of the operating days per calendar quarter that the affected facility is combusting municipal solid waste.
a. At least two data points per hour shall be used to calculate each one-hour arithmetic average.
b. Each sulfur dioxide one-hour arithmetic average shall be corrected to 7.0% oxygen on an hourly basis using the one-hour arithmetic average of the oxygen (or carbon dioxide) continuous emission monitoring system data.
8. The one-hour arithmetic averages required under subdivision 6 of this subsection shall be expressed in parts per million corrected to 7.0% oxygen (dry basis) and used to calculate the 24-hour daily geometric average emission concentrations and daily geometric average emission percent reductions. The one-hour arithmetic averages shall be calculated using the data points required in 40 CFR 60.13(e)(2).
9. All valid continuous emission monitoring system data shall be used in calculating average emission concentrations and percent reductions even if the minimum continuous emission monitoring system data requirements of subdivision 7 of this subsection are not met.
10. The procedures in 40 CFR 60.13 shall be followed for installation, evaluation, and operation of the continuous emission monitoring system.
11. The initial performance evaluation shall be completed as specified in 9VAC5-40-8100.
12. The continuous emission monitoring system shall be operated according to Performance Specification 2 in Appendix B of 40 CFR Part 60.
a. During each relative accuracy test run of the continuous emission monitoring system required by Performance Specification 2 in Appendix B of 40 CFR Part 60, sulfur dioxide and oxygen (or carbon dioxide) data shall be collected concurrently (or within a 30- to 60-minute period) by both the continuous emission monitors and the test methods specified in subdivisions 12 a (1) and 12 a (2) of this subsection.
(1) For sulfur dioxide, Reference Method 6, 6A, or 6C shall be used.
(2) For oxygen (or carbon dioxide), Reference Method 3, 3A, or 3B, as applicable, shall be used.
b. The span value of the continuous emissions monitoring system at the inlet to the sulfur dioxide control device shall be 125% of the maximum estimated hourly potential sulfur dioxide emissions of the municipal waste combustor unit. The span value of the continuous emission monitoring system at the outlet of the sulfur dioxide control device shall be 50% of the maximum estimated hourly potential sulfur dioxide emissions of the municipal waste combustor unit.
13. Quarterly accuracy determinations and daily calibration drift tests shall be performed in accordance with procedure 1 in Appendix F of 40 CFR Part 60.
14. When sulfur dioxide emissions data are not obtained because of continuous emission monitoring system breakdowns, repairs, calibration checks, and zero and span adjustments, emissions data shall be obtained by using other monitoring systems as approved by the board or Reference Method 19 to provide, as necessary, valid emissions data for a minimum of 75% of the hours per day that the affected facility is operated and combusting municipal solid waste for 90% of the days per calendar quarter that the affected facility is operated and combusting municipal solid waste.
E. The procedures and test methods specified in this subsection shall be used for determining compliance with the hydrogen chloride emission limit under 9VAC5-40-8030.
1. Reference Method 26 or 26A, as applicable, shall be used to determine the hydrogen chloride emission concentration. The minimum sampling time for Reference Method 26 shall be one hour.
2. An oxygen (or carbon dioxide) measurement shall be obtained simultaneously with each Reference Method 26 test run for hydrogen chloride required by subdivision 1 of this subsection.
3. The percent reduction in potential hydrogen chloride emissions (%PHCl) is computed using the following equation:
where:
%PHCl = percent reduction of the potential hydrogen chloride emissions achieved.
Ei = potential hydrogen chloride emission concentration measured at the control device inlet, corrected to 7.0% oxygen (dry basis).
EO = controlled hydrogen chloride emission concentration measured at the control device outlet, corrected to 7.0% oxygen (dry basis).
4. The owner of an affected facility may request that compliance with the hydrogen chloride emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7.0% oxygen. The relationship between oxygen and carbon dioxide levels for the affected facility shall be established as specified in 9VAC5-40-8150 B 6.
5. As specified in 40 CFR 60.8, all emission tests shall consist of three test runs. The average of the hydrogen chloride emission concentrations or percent reductions from the three test runs is used to determine compliance.
6. The owner of an affected facility shall conduct an initial emission test for hydrogen chloride as required in 9VAC5-40-8100.
7. Following the date that the initial emission test for hydrogen chloride is completed or is required to be completed in 9VAC5-40-8100, the owner of an affected facility shall conduct an emission test for hydrogen chloride emissions on an annual basis (no more than 12 calendar months following the previous emission test).
F. The procedures and test methods specified in this subsection shall be used to determine compliance with the limits for dioxin/furan emissions under 9VAC5-40-8040.
1. Reference Method 1 shall be used for determining the location and number of sampling points.
2. Reference Method 3, 3A, or 3B, as applicable, shall be used for flue gas analysis.
3. Reference Method 23 shall be used for determining the dioxin/furan emission concentration.
a. The minimum sample time shall be four hours per test run.
b. An oxygen (or carbon dioxide) measurement shall be obtained simultaneously with each Reference Method 23 test run for dioxins/furans.
4. The owner of an affected facility shall conduct an initial emission test for dioxin/furan emissions in accordance with subdivision 3 of this subsection, as required in 9VAC5-40-8100.
5. Following the date that the initial emission test for dioxins/furans is completed or is required to be completed in 9VAC5-40-8100, the owner of an affected facility shall conduct emission tests for dioxin/furan emissions in accordance with subdivision 3 of this subsection, according to one of the schedules specified in subdivision 5 a or 5 b of this subsection.
a. For affected facilities, emission tests shall be conducted on an annual basis (no more than 12 calendar months following the previous emission test).
b. Where all emission tests over a two-year period indicate that dioxin/furan emissions are less than or equal to 15 nanograms per dry standard cubic meter (total mass) for all affected facilities located within a municipal waste combustor plant, the owner of the municipal waste combustor plant may elect to conduct annual emission tests for one affected facility (i.e., unit) per year at the municipal waste combustor plant. At a minimum, an emission test for dioxin/furan emissions shall be conducted annually (no more than 12 months following the previous emission test) for one affected facility at the municipal waste combustor plant. Each year a different affected facility at the municipal waste combustor plant shall be tested, and the affected facilities at the plant shall be tested in sequence (e.g., unit 1, unit 2, unit 3, as applicable). If each annual emission test continues to indicate a dioxin/furan emission level less than or equal to 15 nanograms per dry standard cubic meter (total mass), the owner may continue conducting an emission test on only one affected facility per year. If any annual emission test indicates a dioxin/furan emission level greater than 15 nanograms per dry standard cubic meter (total mass), emission tests thereafter shall be conducted annually on all affected facilities at the plant until and unless all annual emission tests for all affected facilities at the plant over a two-year period indicate a dioxin/furan emission level less than or equal to 15 nanograms per dry standard cubic meter (total mass).
6. The owner of an affected facility that selects to follow the emission testing schedule specified in subdivision 5 a or 5 b of this subsection shall follow the procedures specified in 9VAC5-40-8160 D 4 for reporting the selection of this schedule.
7. The owner of an affected facility where activated carbon is used to comply with the dioxin/furan emission limits specified in 9VAC5-40-8040 or the dioxin/furan emission level specified in subdivision 5 a or 5 b of this subsection shall follow the procedures specified in subsection J of this section for measuring and calculating the carbon usage rate.
8. The owner may request that compliance with the dioxin/furan emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7.0% oxygen. The relationship between oxygen and carbon dioxide levels for the affected facility shall be established as specified in 9VAC5-40-8150 B 6.
9. As specified in 40 CFR 60.8, all emission tests shall consist of three test runs. The average of the dioxin/furan emission concentrations from the three test runs is used to determine compliance.
G. The procedures and test methods specified in this subsection shall be used to determine compliance with the nitrogen oxides emission limit for affected facilities under 9VAC5-40-8050.
1. Reference Method 19, section 4.1, shall be used for determining the daily arithmetic average nitrogen oxides emission concentration.
2. The owner of an affected facility may request that compliance with the nitrogen oxides emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7.0% oxygen. The relationship between oxygen and carbon dioxide levels for the affected facility shall be established as specified in 9VAC5-40-8150 B 6.
3. The owner of an affected facility subject to the nitrogen oxides limit under 9VAC5-40-8050 shall conduct an initial emission test for nitrogen oxides as required in 9VAC5-40-8100. Compliance with the nitrogen oxides emission limit shall be determined by using the continuous emission monitoring system specified in subdivision 4 of this subsection for measuring nitrogen oxides and calculating a 24-hour daily arithmetic average emission concentration using Reference Method 19, section 4.1.
4. The owner of an affected facility subject to the nitrogen oxides emission limit under 9VAC5-40-8050 shall install, calibrate, maintain, and operate a continuous emission monitoring system for measuring nitrogen oxides discharged to the atmosphere, and record the output of the system.
5. Following the date that the initial emission test for nitrogen oxides is completed or is required to be completed in 9VAC5-40-8100, compliance with the emission limit for nitrogen oxides required under 9VAC5-40-8050 shall be determined based on the 24-hour daily arithmetic average of the hourly emission concentrations using continuous emission monitoring system outlet data.
6. At a minimum, valid continuous emission monitoring system hourly averages shall be obtained as specified in subdivisions 6 a and 6 b of this subsection for 75% of the operating hours per day for 90% of the operating days per calendar quarter that the affected facility is combusting municipal solid waste.
a. At least two data points per hour shall be used to calculate each one-hour arithmetic average.
b. Each nitrogen oxides one-hour arithmetic average shall be corrected to 7.0% oxygen on an hourly basis using the one-hour arithmetic average of the oxygen (or carbon dioxide) continuous emission monitoring system data.
7. The one-hour arithmetic averages required by subdivision 5 of this subsection shall be expressed in parts per million by volume (dry basis) and used to calculate the 24-hour daily arithmetic average concentrations. The one-hour arithmetic averages shall be calculated using the data points required in 40 CFR 60.13(e)(2).
8. All valid continuous emission monitoring system data must be used in calculating emission averages even if the minimum continuous emission monitoring system data requirements of subdivision 6 of this subsection are not met.
9. The procedures in 40 CFR 60.13 shall be followed for installation, evaluation, and operation of the continuous emission monitoring system. The initial performance evaluation shall be completed as specified in 9VAC5-40-8100.
10. The owner of an affected facility shall operate the continuous emission monitoring system according to Performance Specification 2 in Appendix B of 40 CFR Part 60 and shall follow the procedures and methods specified in subdivisions 10 a and 10 b of this subsection.
a. During each relative accuracy test run of the continuous emission monitoring system required by Performance Specification 2 of Appendix B of 40 CFR Part 60, nitrogen oxides and oxygen (or carbon dioxide) data shall be collected concurrently (or within a 30- to 60-minute period) by both the continuous emission monitors and the test methods specified in subdivisions 10 a (1) and 10 a (2) of this subsection.
(1) For nitrogen oxides, Reference Method 7, 7A, 7C, 7D, or 7E shall be used.
(2) For oxygen (or carbon dioxide), Reference Method 3, 3A, or 3B, as applicable, shall be used.
b. The span value of the continuous emission monitoring system shall be 125% of the maximum estimated hourly potential nitrogen oxide emissions of the municipal waste combustor unit.
11. Quarterly accuracy determinations and daily calibration drift tests shall be performed in accordance with procedure 1 in Appendix F of 40 CFR Part 60.
12. When nitrogen oxides continuous emissions data are not obtained because of continuous emission monitoring system breakdowns, repairs, calibration checks, and zero and span adjustments, emissions data shall be obtained using other monitoring systems as approved by the board or Reference Method 19 to provide, as necessary, valid emissions data for a minimum of 75% of the hours per day for 90% of the days per calendar quarter the unit is operated and combusting municipal solid waste.
H. The procedures specified in this subsection shall be used for determining compliance with the fugitive ash emission limit under 9VAC5-40-8070.
1. Reference Method 22 shall be used for determining compliance with the fugitive ash emission limit under 9VAC5-40-8070. The minimum observation time shall be a series of three one-hour observations. The observation period shall include times when the facility is transferring ash from the municipal waste combustor unit to the area where ash is stored or loaded into containers or trucks.
2. The average duration of visible emissions per hour shall be calculated from the three one-hour observations. The average shall be used to determine compliance with 9VAC5-40-8070.
3. The owner of an affected facility shall conduct an initial emission test for fugitive ash emissions as required in 9VAC5-40-8100.
4. Following the date that the initial emission test for fugitive ash emissions is completed or is required to be completed in 9VAC5-40-8100 for an affected facility, the owner shall conduct an emission test for fugitive ash emissions on an annual basis (no more than 12 calendar months following the previous emission test).
I. The procedures specified in this subsection shall be used to determine compliance with the opacity limit for air curtain incinerators under 9VAC5-40-8060 C.
1. Reference Method 9 shall be used for determining compliance with the opacity limit.
2. The owner of the air curtain incinerator shall conduct an initial emission test for opacity as required in 9VAC5-40-8100.
3. Following the date that the initial emission test is completed or is required to be completed in 9VAC5-40-8100, the owner of the air curtain incinerator shall conduct an emission test for opacity on an annual basis (no more than 12 calendar months following the previous emission test).
J. The owner of an affected facility where activated carbon injection is used to comply with the mercury emission limit under 9VAC5-40-8010, or the dioxin/furan emission limits under 9VAC5-40-8040, or the dioxin/furan emission level specified in subdivision F 5 b of this section shall follow the procedures specified in this subsection.
1. During the emission tests for dioxins/furans and mercury, as applicable, the owner shall estimate an average carbon mass feed rate based on carbon injection system operating parameters such as the screw feeder speed, hopper volume, hopper refill frequency, or other parameters appropriate to the feed system being employed, as specified in subdivisions 1 a and 1 b of this subsection.
a. An average carbon mass feed rate in kilograms per hour or pounds per hour shall be estimated during the initial emission test for mercury emissions and each subsequent emission test for mercury emissions.
b. An average carbon mass feed rate in kilograms per hour or pounds per hour shall be estimated during the initial emission test for dioxin/furan emissions and each subsequent emission test for dioxin/furan emissions.
2. During operation of the affected facility, the carbon injection system operating parameter(s) that are the primary indicator(s) of the carbon mass feed rate (e.g., screw feeder setting) must equal or exceed the level(s) documented during the emission tests specified under subdivisions 1 a and 1 b of this subsection.
3. The owner of an affected facility shall estimate the total carbon usage of the plant (kilograms or pounds) for each calendar quarter by two independent methods, according to the procedures in subdivisions 3 a and 3 b of this subsection.
a. The weight of carbon delivered to the plant.
b. Estimate the average carbon mass feed rate in kilograms per hour or pounds per hour for each hour of operation for each affected facility based on the parameters specified under subdivision 1 of this subsection, and sum the results for all affected facilities at the plant for the total number of hours of operation during the calendar quarter.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003.
9VAC5-40-8150. Monitoring.
A. The provisions governing monitoring shall be as follows:
1. With regard to the emissions standards in 9VAC5-40-8080 and 9VAC5-40-8090, the provisions of 9VAC5-40-40 (Monitoring) apply.
2.With regard to the emission limits in 9VAC5-40-7970 through 9VAC5-40-8070, the following provisions apply:
a. 9VAC5-40-40 A and F.
b. 40 CFR 60.13.
c. Subsections B and C of this section.
B. The owner of an affected facility shall install, calibrate, maintain, and operate a continuous emission monitoring system and record the output of the system for measuring the oxygen or carbon dioxide content of the flue gas at each location where carbon monoxide, sulfur dioxide, or nitrogen oxides emissions are monitored and shall comply with the test procedures and test methods specified in this subsection.
1. The span value of the oxygen (or carbon dioxide) monitor shall be 25% oxygen (or carbon dioxide).
2. The monitor shall be installed, evaluated, and operated in accordance with 40 CFR 60.13.
3. The initial performance evaluation shall be completed prior to the initial emission test as specified in 9VAC5-40-8100.
4. The monitor shall conform to Performance Specification 3 in Appendix B of 40 CFR Part 60 except for section 2.3 (relative accuracy requirement).
5. The quality assurance procedures of Appendix F of 40 CFR Part 60 except for section 5.1.1 (relative accuracy test audit) shall apply to the monitor.
6. If carbon dioxide is selected for use in diluent corrections, the relationship between oxygen and carbon dioxide levels shall be established during the initial emission test according to the procedures and methods specified in subdivisions 6 a through 6 d of this subsection. This relationship may be reestablished during performance compliance tests.
a. The fuel factor equation in Reference Method 3B shall be used to determine the relationship between oxygen and carbon dioxide at a sampling location. Reference method 3, 3A, or 3B, as applicable, shall be used to determine the oxygen concentration at the same location as the carbon dioxide monitor.
b. Samples shall be taken for at least 30 minutes in each hour.
c. Each sample shall represent a one-hour average.
d. A minimum of three runs shall be performed.
7. The relationship between carbon dioxide and oxygen concentrations that is established in accordance with subdivision 6 of this subsection shall be submitted to the board as part of the initial emission test report and, if applicable, as part of the annual test report if the relationship is reestablished during the annual emission test.
C. The procedures specified in this subsection shall be used for determining compliance with the operating requirements under 9VAC5-40-8120.
1. Compliance with the carbon monoxide emission limits in 9VAC5-40-7980 shall be determined using a four-hour block arithmetic average for all types of affected facilities except mass burn rotary waterwall municipal waste combustors and refuse-derived fuel stokers.
2. For affected mass burn rotary waterwall municipal waste combustors and refuse-derived fuel stokers, compliance with the carbon monoxide emission limits in 9VAC5-40-7980 shall be determined using a 24-hour daily arithmetic average.
3. The owner of an affected facility shall install, calibrate, maintain, and operate a continuous emission monitoring system for measuring carbon monoxide at the combustor outlet and record the output of the system and shall follow the procedures and methods specified in subdivisions 3 a through 3 c of this subsection.
a. The continuous emission monitoring system shall be operated according to Performance Specification 4A in Appendix B of 40 CFR Part 60.
b. During each relative accuracy test run of the continuous emission monitoring system required by Performance Specification 4A in Appendix B of 40 CFR Part 60, carbon monoxide and oxygen (or carbon dioxide) data shall be collected concurrently (or within a 30- to 60-minute period) by both the continuous emission monitors and the test methods specified in subdivisions 3 b (1) and 3 b (2) of this subsection.
(1) For carbon monoxide, Reference Method 10, 10A, or 10B shall be used.
(2) For oxygen (or carbon dioxide), Reference Method 3, 3A, or 3B, as applicable, shall be used.
c. The span value of the continuous emission monitoring system shall be 125% of the maximum estimated hourly potential carbon monoxide emissions of the municipal waste combustor unit.
4. The four-hour block and 24-hour daily arithmetic averages specified in subdivisions 1 and 2 of this subsection shall be calculated from one-hour arithmetic averages expressed in parts per million by volume corrected to 7.0% oxygen (dry basis). The one-hour arithmetic averages shall be calculated using the data points generated by the continuous emission monitoring system. At least two data points shall be used to calculate each one-hour arithmetic average.
5. The owner of an affected facility may request that compliance with the carbon monoxide emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7.0% oxygen. The relationship between oxygen and carbon dioxide levels for the affected facility shall be established as specified in subdivision B 6 of this section.
6. The procedures specified in subdivisions 6 a through 6 d of this subsection shall be used to determine compliance with load level requirements under 9VAC5-40-8120 A.
a. The owner of an affected facility with steam generation capability shall install, calibrate, maintain, and operate a steam flow meter or a feedwater flow meter; measure steam (or feedwater) flow in kilograms per hour (or pounds per hour) on a continuous basis; and record the output of the monitor. Steam (or feedwater) flow shall be calculated in four-hour block arithmetic averages.
b. The method included in section 4 of the American Society of Mechanical Engineers publication, "Power Test Codes: Steam Generating Units" (see 9VAC5-20-21) shall be used for calculating the steam (or feedwater) flow required under subdivision 6 a of this subsection. The recommendations in chapter 4 of the American Society of Mechanical Engineers publication, "Interim Supplement 19.5 on Instruments and Apparatus: Application, Part II of Fluid Meters" (see 9VAC5-20-21) shall be followed for design, construction, installation, calibration, and use of nozzles and orifices except as specified in subdivision 6 c of this subsection.
c. Measurement devices such as flow nozzles and orifices are not required to be recalibrated after they are installed.
d. All signal conversion elements associated with steam (or feedwater flow) measurements must be calibrated according to the manufacturer's instructions before each dioxin/furan emission test, and at least once per year.
7. To determine compliance with the maximum particulate matter control device temperature requirements under 9VAC5-40-8120 B, the owner of an affected facility shall install, calibrate, maintain, and operate a device for measuring on a continuous basis the temperature of the flue gas stream at the inlet to each particulate matter control device utilized by the affected facility. Temperature shall be calculated in four-hour block arithmetic averages.
8. The maximum demonstrated municipal waste combustor unit load shall be determined during the initial emission test for dioxins/furans and each subsequent emission test during which compliance with the dioxin/furan emission limit specified in 9VAC5-40-8040 is achieved. The maximum demonstrated municipal waste combustor unit load shall be the highest four-hour arithmetic average load achieved during four consecutive hours during the most recent test during which compliance with the dioxin/furan emission limit was achieved.
9. For each particulate matter control device employed at the affected facility, the maximum demonstrated particulate matter control device temperature shall be determined during the initial emission test for dioxins/furans and each subsequent emission test during which compliance with the dioxin/furan emission limit specified in 9VAC5-40-8040 is achieved. The maximum demonstrated particulate matter control device temperature shall be the highest four-hour arithmetic average temperature achieved at the particulate matter control device inlet during four consecutive hours during the most recent test during which compliance with the dioxin/furan limit was achieved.
10. At a minimum, valid continuous emission monitoring system hourly averages shall be obtained as specified in subdivisions 10 a and 10 b of this subsection for 75% of the operating hours per day for 90% of the operating days per calendar quarter that the affected facility is combusting municipal solid waste.
a. At least two data points per hour shall be used to calculate each one-hour arithmetic average.
b. At a minimum, each carbon monoxide one-hour arithmetic average shall be corrected to 7.0% oxygen on an hourly basis using the one-hour arithmetic average of the oxygen (or carbon dioxide) continuous emission monitoring system data.
11. All valid continuous emission monitoring system data must be used in calculating the parameters specified under this section even if the minimum data requirements of subdivision 10 of this subsection are not met. When carbon monoxide continuous emission data are not obtained because of continuous emission monitoring system breakdowns, repairs, calibration checks, and zero and span adjustments, emissions data shall be obtained using other monitoring systems as approved by the board or Reference Method 10 to provide, as necessary, the minimum valid emission data.
12. Quarterly accuracy determinations and daily calibration drift tests for the carbon monoxide continuous emission monitoring system shall be performed in accordance with procedure 1 in Appendix F of 40 CFR Part 60.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999; amended, Virginia Register Volume 18, Issue 7, eff. February 1, 2002; Volume 19, Issue 17, eff. July 1, 2003.
9VAC5-40-8160. Notification, records and reporting.
A. The provisions governing notification, records and reporting shall be as follows:
1. With regard to the emissions standards in 9VAC5-40-8080 and 9VAC5-40-8090, the provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
2. With regard to the emission limits in 9VAC5-40-7970 through 9VAC5-40-8070, the following provisions apply:
a. 9VAC5-40-50 F and H.
b. 40 CFR 60.7.
c. Subsections B through J of this section.
B. The owner of an affected facility shall maintain records of the information specified in this subsection, as applicable, for each affected facility for a period of at least five years.
1. The calendar date of each record.
2. The emission concentrations and parameters measured using continuous monitoring systems as specified under subdivisions 2 a and 2 b of this subsection.
a. The measurements specified in subdivisions 2 a (1) through 2 a (4) of this subsection shall be recorded and be available for submittal to the board or review onsite by an inspector.
(1) All six-minute average opacity levels as specified under 9VAC5-40-8140 B.
(2) All one-hour average sulfur dioxide emission concentrations as specified under 9VAC5-40-8140 D.
(3) All one-hour average nitrogen oxides emission concentrations as specified under 9VAC5-40-8140 G.
(4) All one-hour average carbon monoxide emission concentrations, municipal waste combustor unit load measurements, and particulate matter control device inlet temperatures as specified under 9VAC5-40-8150 C.
b. The average concentrations and percent reductions, as applicable, specified in subdivisions 2 b (1) through 2 b (4) of this subsection shall be computed and recorded, and shall be available for submittal to the board or review on-site by an inspector.
(1) All 24-hour daily geometric average sulfur dioxide emission concentrations and all 24-hour daily geometric average percent reductions in sulfur dioxide emissions as specified under 9VAC5-40-8140 D.
(2) All 24-hour daily arithmetic average nitrogen oxides emission concentrations as specified under 9VAC5-40-8140 G.
(3) All four-hour block or 24-hour daily arithmetic average carbon monoxide emission concentrations, as applicable, as specified under 9VAC5-40-8150 C.
(4) All four-hour block arithmetic average municipal waste combustor unit load levels and particulate matter control device inlet temperatures as specified under 9VAC5-40-8150 C.
3. Identification of the calendar dates when any of the average emission concentrations, percent reductions, or operating parameters recorded under subdivisions 2 b (1) through 2 b (4) of this subsection, or the opacity levels recorded under subdivision 2 a (1) of this subsection are above the applicable limits, with reasons for such exceedances and a description of corrective actions taken.
4. For affected facilities that apply activated carbon for mercury or dioxin/furan control, the records specified in subdivisions 4 a through 4 e of this subsection.
a. The average carbon mass feed rate (in kilograms per hour or pounds per hour) estimated as required under 9VAC5-40-8140 J 1 a during all annual emission tests for mercury emissions, with supporting calculations.
b. The average carbon mass feed rate (in kilograms per hour or pounds per hour) estimated as required under 9VAC5-40-8140 J 1 b during all annual emission tests for dioxin/furan, with supporting calculations.
c. The average carbon mass feed rate (in kilograms per hour or pounds per hour) estimated for each hour of operation as required under 9VAC5-40-8140 J 3 b, with supporting calculations.
d. The total carbon usage for each calendar quarter estimated as specified by 9VAC5-40-8140 J 3, with supporting calculations.
e. Carbon injection system operating parameter data for the parameter(s) that are the primary indicator(s) of carbon feed rate (e.g., screw feeder speed).
5. Identification of the calendar dates for which the minimum number of hours of any of the data specified in subdivisions 5 a through 5 e of this subsection have not been obtained including reasons for not obtaining sufficient data and a description of corrective actions taken.
a. Sulfur dioxide emissions data;
b. Nitrogen oxides emissions data;
c. Carbon monoxide emissions data;
d. Municipal waste combustor unit load data; and
e. Particulate matter control device temperature data.
6. Identification of each occurrence that sulfur dioxide emissions data, nitrogen oxides emissions data, or operational data (i.e., carbon monoxide emissions, unit load, and particulate matter control device temperature) have been excluded from the calculation of average emission concentrations or parameters, and the reasons for excluding the data.
7. The results of daily drift tests and quarterly accuracy determinations for sulfur dioxide, nitrogen oxides (large municipal waste combustors only), and carbon monoxide continuous emission monitoring systems, as required under Appendix F of 40 CFR Part 60, procedure 1.
8. The test reports documenting the results of all annual emission tests listed in subdivisions 8 a and 8 b of this subsection shall be recorded along with supporting calculations.
a. The results of all annual emission tests conducted to determine compliance with the particulate matter, opacity, cadmium, lead, mercury, dioxins/furans, hydrogen chloride, and fugitive ash emission limits.
b. For all dioxin/furan emission tests recorded under subdivision 8 a of this subsection, the maximum demonstrated municipal waste combustor unit load and maximum demonstrated particulate matter control device temperature (for each particulate matter control device).
9. The records specified in subdivisions 9 a through 9 c of this subsection.
a. Records showing the names of the municipal waste combustor chief facility operator, shift supervisors, and control room operators who have been provisionally certified by the American Society of Mechanical Engineers or an equivalent board-approved certification program as required by 9VAC5-40-8130 A, including the dates of initial and renewal certifications and documentation of current certification.
b. Records showing the names of the municipal waste combustor chief facility operator, shift supervisors, and control room operators who have been fully certified by the American Society of Mechanical Engineers or an equivalent board-approved certification program as required by 9VAC5-40-8130 B, including the dates of initial and renewal certifications and documentation of current certification.
c. Records showing the names of the municipal waste combustor chief facility operator, shift supervisors, and control room operators who have completed the EPA municipal waste combustor operator training course or a board-approved equivalent course as required by 9VAC5-40-8130 E, including documentation of training completion.
10. Records showing the names of persons who have completed a review of the operating manual as required by 9VAC5-40-8130 G, including the date of the initial review and subsequent annual reviews.
11. For affected facilities that apply activated carbon for mercury or dioxin/furan control, identification of the calendar dates when the average carbon mass feed rates recorded under subdivision 4 c of this subsection were less than either of the hourly carbon feed rates estimated during emission tests for mercury or dioxin/furan emissions and recorded under subdivisions 4 a and 4 b of this subsection, respectively, with reasons for such feed rates and a description of corrective actions taken.
12. For affected facilities that apply activated carbon for mercury or dioxin/furan control, identification of the calendar dates when the carbon injection system operating parameter(s) that are the primary indicator(s) of carbon mass feed rate (e.g., screw feeder speed) recorded under subdivision 4 d of this subsection are below the level(s) estimated during the emission tests as specified in 9VAC5-40-8140 J 1 a and 9VAC5-40-8140 J 1 b, with reasons for such occurrences and a description of corrective actions taken.
C. The owner of an air curtain incinerator subject to the opacity limit under 9VAC5-40-8060 shall maintain records of results of the opacity emission tests required by 9VAC5-40-8140 I for a period of at least five years.
D. The owner of an affected facility shall submit an annual report including the information specified in this subsection, as applicable, no later than February 1 of each year following the calendar year in which the data were collected (once the unit is subject to permitting requirements in a federal operating permit, the owner of an affected facility must submit these reports semiannually).
1. A summary of data collected for all pollutants and parameters regulated under this article, which includes the information specified in subdivisions 1 a through 1 e of this subsection.
a. A list of the particulate matter, opacity, cadmium, lead, mercury, dioxins/furans, hydrogen chloride, and fugitive ash emission levels achieved during the emission tests recorded under subdivision B 8 of this section.
b. A list of the highest emission level recorded for sulfur dioxide, nitrogen oxides, carbon monoxide, municipal waste combustor unit load level, and particulate matter control device inlet temperature based on the data recorded under subdivisions B 2 b (1) through B 2 b (4) of this section.
c. List the highest opacity level measured, based on the data recorded under subdivision B 2 a (1) of this section.
d. The total number of days that the minimum number of hours of data for sulfur dioxide, nitrogen oxides, carbon monoxide, municipal waste combustor unit load, and particulate matter control device temperature data were not obtained based on the data recorded under subdivision B 5 of this section.
e. The total number of hours that data for sulfur dioxide, nitrogen oxides, carbon monoxide, municipal waste combustor unit load, and particulate matter control device temperature were excluded from the calculation of average emission concentrations or parameters based on the data recorded under subdivision B 6 of this section.
2. The summary of data reported under subdivision 1 of this subsection shall also provide the types of data specified in subdivision 1 of this subsection for the calendar year preceding the year being reported, in order to provide the board with a summary of the performance of the affected facility over a two-year period.
3. The summary of data including the information specified in subdivisions 1 and 2 of this subsection shall highlight any emission or parameter levels that did not achieve the emission or parameter limits specified under this article.
4. A notification of intent to begin the reduced dioxin/furan emission testing schedule specified in 9VAC5-40-8140 F 5 b during the following calendar year.
E. The owner of an affected facility shall submit a semiannual report that includes the information specified in subdivisions 1 through 5 of this subsection for any recorded pollutant or parameter that does not comply with the pollutant or parameter limit specified under this article, according to the schedule specified under subdivision 6 of this subsection.
1. The semiannual report shall include information recorded under subdivision B 3 of this section for sulfur dioxide, nitrogen oxides, carbon monoxide, municipal waste combustor unit load level, particulate matter control device inlet temperature, and opacity.
2. For each date recorded as required by subdivision B 3 of this section and reported as required by subdivision 1 of this subsection, the semiannual report shall include the sulfur dioxide, nitrogen oxides, carbon monoxide, municipal waste combustor unit load level, particulate matter control device inlet temperature, or opacity data, as applicable, recorded under subdivisions B 2 b (1) through B 2 b (4) and B 2 a (1) of this section, as applicable.
3. If the test reports recorded under subdivision B 8 of this section document any particulate matter, opacity, cadmium, lead, mercury, dioxins/furans, hydrogen chloride, and fugitive ash emission levels that were above the applicable pollutant limits, the semiannual report shall include a copy of the test report documenting the emission levels and the corrective actions taken.
4. The semiannual report shall include the information recorded under subdivision B 12 of this section for the carbon injection system operating parameter(s) that are the primary indicator(s) of carbon mass feed rate.
5. For each operating date reported as required by subdivision 4 of this subsection, the semiannual report shall include the carbon feed rate data recorded under subdivision B 4 c of this section.
6. Semiannual reports required by this subsection shall be submitted according to the schedule specified in subdivisions 6 a and 6 b of this subsection.
a. If the data reported in accordance with subdivisions 1 through 5 of this subsection were collected during the first calendar half, then the report shall be submitted by August 1 following the first calendar half.
b. If the data reported in accordance with subdivisions 1 through 5 of this subsection were collected during the second calendar half, then the report shall be submitted by February 1 following the second calendar half.
F. The owner of an air curtain incinerator subject to the opacity limit under 9VAC5-40-8060 shall submit the results of all annual emission tests for opacity recorded under subsection C of this section. Annual emission tests shall be submitted by February 1 of the year following the year of the emission test.
G. All reports specified under subsections D, E, and F of this section shall be submitted as a paper copy, postmarked on or before the submittal dates specified under these subsections, and maintained onsite as a paper copy for a period of five years.
H. All records specified under subsections B and C of this section shall be maintained onsite in either paper copy or computer-readable format, unless an alternative format is approved by the board.
I. If the owner of an affected facility would prefer to select a different annual or semiannual date for submitting the periodic reports required by subsections D, E, and F of this section, then the dates may be changed by mutual agreement between the owner and the board.
J. The owner of an affected facility shall submit the information specified in subdivisions 1 through 6 of this subsection in the initial emission test report.
1. The initial performance test data as recorded under subdivisions B 2 b (1) through (4) of this section for the initial emission test for sulfur dioxide, nitrogen oxides, carbon monoxide, MWC combustor unit load level, and particulate matter control device inlet temperature.
2. The test report documenting the initial emission test recorded under subdivision B 8 of this section for particulate matter, opacity, cadmium, lead, mercury, dioxins/furans, hydrogen chloride, and fugitive ash emissions.
3. The performance evaluation of the continuous emission monitoring system using the applicable performance specifications in Appendix B of 40 CFR Part 60.
4. The maximum demonstrated MWC unit load and maximum demonstrated particulate matter control device inlet temperatures established during the initial dioxin/furan emission test as recorded in subdivision B 8 of this section.
5. For affected facilities that apply activated carbon injection for mercury control, the owner shall submit the average carbon mass feed rate recorded under subdivision B 4 a of this section.
6. For affected facilities that apply activated carbon injection for dioxin/furan control, the owner shall submit the average carbon mass feed rate recorded under subdivision B 4 b of this section.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003.
9VAC5-40-8170. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999.
9VAC5-40-8180. Facility and control equipment maintenance or malfunction.
The provisions governing facility and control equipment maintenance or malfunction shall be as follows:
1. With regard to the emissions standards in 9VAC5-40-8080 and 9VAC5-40-8090, the provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply.
2. With regard to the emission limits in 9VAC5-40-7970 through 9VAC5-40-8070, the following provisions apply:
a. 9VAC5-20-180 A, B, C, D, H, and I.
b. 9VAC5-40-8100 B.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999; amended, Virginia Register Volume 19, Issue 17, eff. July 1, 2003.
9VAC5-40-8190. Permits.
A permit may be required prior to beginning any of the activities specified below if the provisions of 9VAC5 Chapter 50 (9VAC5-50-10 et seq.) and 9VAC5 Chapter 80 (9VAC5-80-10 et seq.) apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (restart-up) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia.
Historical Notes
Derived from Virginia Register Volume 15, Issue 21, eff. August 4, 1999.
Article 55
Emission Standards for Sewage Sludge Incineration Units (Rule 4-55)
9VAC5-40-8200. Applicability and designation of affected facility.
Article 55
Emission Standards for Sewage Sludge Incineration Units (Rule 4-55)
A. The affected facilities to which the provisions of this article apply are sewage sludge incineration (SSI) units that meet all of the following criteria:
1. SSI units that commenced construction on or before October 14, 2010.
2. SSI units that meet the definition of a SSI unit as defined in 9VAC5-40-8210.
3. SSI units not exempt under subsection D of this section.
B. The provisions of this article apply throughout the Commonwealth of Virginia.
C. The following provisions govern changes to SSI units.
1. If the owner of a SSI unit makes changes that meet the definition of modification after September 21, 2011, the SSI unit becomes subject to Subpart LLLL of 40 CFR Part 60 and the provisions of this article no longer apply to that unit.
2. If the owner of a SSI unit makes physical or operational changes to a SSI unit for which construction commenced on or before September 21, 2011, primarily to comply with the provisions of this article, Subpart LLLL of 40 CFR Part 60 does not apply to that unit. Such changes do not qualify as modifications under Subpart LLLL of 40 CFR Part 60.
D. Exempt from the provisions of this article are combustion units that incinerate sewage sludge and are not located at a wastewater treatment facility designed to treat domestic sewage sludge. These units may be subject to 40 CFR Part 60 (e.g., Subpart CCCC of 40 CFR Part 60). The owner of such a combustion unit shall notify the board of an exemption claim under this subsection.
E. The provisions of 40 CFR Part 60 (other than Subpart MMMM of 40 CFR Part 60) cited in this article are applicable only to the extent that they are incorporated by reference in Article 5 (9VAC5-50-400 et seq.) of Part II of 9VAC5-50 (New and Modified Stationary Sources).
F. The provisions of Subpart MMMM (Emission Guidelines and Compliance Times for Existing Sewage Sludge Incineration Units) of 40 CFR Part 60 cited in this article are applicable only to the extent that they are incorporated by reference in 9VAC5-40-8370.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8210. Definitions.
A. For the purpose of applying this article in the context of the Regulations for the Control and Abatement of Air Pollution and related uses, the words or terms shall have the meanings given them in subsection C of this section.
B. As used in this article, all terms not defined herein shall have the meanings given them in 9VAC5-10 (General Definitions), unless otherwise required by context.
C. Terms shall have the meanings given them in 40 CFR 60.5250, except for the following:
"Administrator" means the board.
"Performance test as defined in 40 CFR 63.2" means the collection of data resulting from the execution of a test method (usually three emission test runs) used to demonstrate compliance with a relevant emission standard as specified in the performance test section of the relevant standard.
"Table 1" means 9VAC5-40-8280 A and B.
"You" means the owner of an affected SSI unit.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012; Errata, 28:25 VA.R. 2076 August 13, 2012.
9VAC5-40-8220. Emission limits and emission standards.
A. No owner or other person shall cause or permit to be discharged into the atmosphere from any SSI unit any emissions in excess of that allowed under subsection B of this section.
B. The provisions of 40 CFR 60.5165 apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8230. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of 9VAC5-40 (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply, with the exception of 9VAC5-40-90 (Standard for fugitive dust/emissions).
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8240. Standard for fugitive dust/emissions.
A. The provisions of Article 1 (9VAC5-40-60 et seq.) of 9VAC5-40 (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply, with the exception of 9VAC5-40-80 (Standard for visible emissions), 9VAC5-40-100 (Monitoring), 9VAC5-40-110 (Test methods and procedures), and 9VAC5-40-120 (Waivers).
B. No owner or other person shall cause or permit to be discharged into the atmosphere from any ash conveying system (including conveyor transfer points) any visible emissions for more than 5.0% of hourly observation period, measured at three, one-hour observation periods.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8250. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of 9VAC5-40 (Emissions Standards for Odor, Rule 4-2) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8260. Standard for toxic pollutants.
The provisions of Article 4 (9VAC5-60-200 et seq.) of 9VAC5-60 (Emissions Standards for Toxic Pollutants from Existing Sources, Rule 6-4) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8270. Operator training and certification.
The provisions of 40 CFR 60.5130, 40 CFR 60.5135, 40 CFR 60.5140, 40 CFR 60.5145, 40 CFR 60.5150, 40 CFR 60.5155, and 40 CFR 60.5160 apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012; Errata, 28:25 VA.R. 2076 August 13, 2012.
9VAC5-40-8280. Compliance schedule.
A. SSI units shall achieve final compliance or cease operation as expeditiously as practicable but not later than March 21, 2016.
B. The owner shall submit a final control plan no later than March 21, 2013.
C. The provisions of 40 CFR 60.5085, 40 CFR 60.5090, 40 CFR 60.5095, 40 CFR 60.5100, 40 CFR 60.5105, 40 CFR 60.5110, 40 CFR 60.5115, 40 CFR 60.5120, and 40 CFR 60.5125 apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8290. Operating requirements.
A. No owner or other person shall operate any SSI unit in a manner that does not comply with the provisions of subsection B of this section.
B. The provisions of 40 CFR 60.5170 and 40 CFR 60.5175 apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8300. Compliance.
A. With regard to the emissions standards in 9VAC5-40-8240 A, 9VAC5-40-8250, and 9VAC5-40-8260, the provisions of 9VAC5-40-20 (Compliance) apply.
B. With regard to the emission limits in 9VAC5-40-8220, 9VAC5-40-8240 B, and 9VAC5-40-8290, the following provisions apply:
1. 9VAC5-40-20 B, C, D, and E;
2. To the extent specified in the federal regulations cited in subdivision 3 of this subsection, 40 CFR 60.7, 40 CFR 60.8, 40 CFR 60.11, and 40 CFR 60.13; and
3. 40 CFR 60.5185, 40 CFR 60.5190, 40 CFR 60.5195, 40 CFR 60.5200, 40 CFR 60.5205, 40 CFR 60.5210, and 40 CFR 60.5215.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8310. Performance testing, monitoring, and calibration requirements.
A. With regard to the emissions standards in 9VAC5-40-8240 A, 9VAC5-40-8250, and 9VAC5-40-8260, the provisions of 9VAC5-40-30 (Emission testing) and 9VAC5-40-40 (Monitoring) apply.
B. With regard to the emission limits in 9VAC5-40-8220, 9VAC5-40-8240 B, and 9VAC5-40-8290, the following provisions apply:
1. 9VAC5-40-30 D and G;
2. 9VAC5-40-40 A and F;
3. 40 CFR 60.8(b) through (f), with the exception of paragraph (a);
4. 40 CFR 60.13; and
5. 40 CFR 60.5220 and 40 CFR 60.5225.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8320. Recordkeeping and reporting.
A. With regard to the emissions standards in 9VAC5-40-8240 A, 9VAC5-40-8250, and 9VAC5-40-8260, the provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
B. With regard to the emission limits in 9VAC5-40-8220, 9VAC5-40-8240 B, and 9VAC5-40-8290, the following provisions apply:
1. 9VAC5-40-50 F and H;
2. 40 CFR 60.7; and
3. 40 CFR 60.5230 and 40 CFR 60.5235.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8330. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8340. Facility and control equipment maintenance or malfunction.
A. With regard to the emissions standards in 9VAC5-40-8240 A, 9VAC5-40-8250, and 9VAC5-40-8260, the provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply.
B. With regard to the emission limits in 9VAC5-40-8220, 9VAC5-40-8240 B, and 9VAC5-40-8290, the following provisions apply:
1. 9VAC5-20-180 with the exception of subsections E, F, and G; and
2. 40 CFR 60.5180 and 40 CFR 60.5181.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8350. Federal (Title V) operating permits.
A. The provisions of 40 CFR 60.5240 and 40 CFR 60.5245 apply.
B. Owners to which this section applies should contact the appropriate regional office for guidance on applying for a federal (Title V) operating permit.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8360. Other permits.
A permit may be required prior to beginning any of the activities specified below if the provisions of 9VAC5-50 (New and Modified Stationary Sources) and 9VAC5-80 (Permits for Stationary Sources) apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (re-startup) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
9VAC5-40-8370. Documents incorporated by reference.
A. The United States Environmental Protection Agency (EPA) regulations promulgated at Subpart MMMM (Emission Guidelines and Compliance Times for Existing Sewage Sludge Incineration Units) of 40 CFR Part 60 and designated in subsection B of this section are incorporated by reference into this article. The 40 CFR section numbers appearing in subsection B of this section identify the specific provisions incorporated by reference. The specific version of the provisions incorporated by reference shall be that contained in the CFR in effect as specified in 9VAC5-20-21 B.
B. The following documents from the United States Environmental Protection Agency are incorporated herein by reference:
Model Rule, Increments of Progress
40 CFR 60.5085, What are my requirements for meeting increments of progress and achieving final compliance?
40 CFR 60.5090, When must I complete each increment of progress?
40 CFR 60.5095, What must I include in the notifications of achievement of increments of progress?
40 CFR 60.5100, When must I submit the notifications of achievement of increments of progress?
40 CFR 60.5105, What if I do not meet an increment of progress?
40 CFR 60.5110, How do I comply with the increment of progress for submittal of a control plan?
40 CFR 60.5115, How do I comply with the increment of progress for achieving final compliance?
40 CFR 60.5120, What must I do if I close my SSI unit and then restart it?
40 CFR 60.5125, What must I do if I plan to permanently close my SSI unit and not restart it?
Model Rule, Operator Training and Qualification
40 CFR 60.5130, What are the operator training and qualification requirements?
40 CFR 60.5135, When must the operator training course be completed?
40 CFR 60.5140, How do I obtain my operator qualification?
40 CFR 60.5145, How do I maintain my operator qualification?
40 CFR 60.5150, How do I renew my lapsed operator qualification?
40 CFR 60.5155, What if all the qualified operators are temporarily not accessible?
40 CFR 60.5160, What site-specific documentation is required and how often must it be reviewed by qualified SSI operators and other plant personnel who may operate the unit according to the provisions of 40 CFR 60.5155(a)?
Model Rule, Emission Limits, Emission Standards, and Operating Limits and Requirements
40 CFR 60.5165, What emission limits and standards must I meet and by when?
40 CFR 60.5170, What operating limits and requirements must I meet and by when?
40 CFR 60.5175, How do I establish operating limits if I do not use a wet scrubber, fabric filter, electrostatic precipitator, activated carbon injection, or afterburner, or if I limit emissions in some other manner, to comply with the emission limits?
40 CFR 60.5180, Do the emission limits, emission standards, and operating limits apply during periods of startup, shutdown, and malfunction?
40 CFR 60.5181, How do I establish affirmative defense for exceedance of an emission limit or standard during malfunction?
Model Rule, Initial Compliance Requirements
40 CFR 60.5185, How and when do I demonstrate initial compliance with the emission limits and standards?
40 CFR 60.5190, How do I establish my operating limits?
40 CFR 60.5195, By what date must I conduct the initial air pollution control device inspection and make any necessary repairs?
40 CFR 60.5200, How do I develop a site-specific monitoring plan for my continuous monitoring systems, bag leak detection system, and ash handling system, and by what date must I conduct an initial performance evaluation of my continuous monitoring systems and bag leak detection system?
Model Rule, Continuous Compliance Requirements
40 CFR 60.5205, How and when do I demonstrate continuous compliance with the emission limits and standards?
40 CFR 60.5210, How do I demonstrate continuous compliance with my operating limits?
40 CFR 60.5215, By what date must I conduct annual air pollution control device inspections and make any necessary repairs?
Model Rule, Performance Testing, Monitoring, and Calibration Requirements
40 CFR 60.5220, What are the performance testing, monitoring, and calibration requirements for compliance with the emission limits and standards?
40 CFR 60.5225, What are the monitoring and calibration requirements for compliance with my operating limits?
Model Rule, Recordkeeping and Reporting
40 CFR 60.5230, What records must I keep?
40 CFR 60.5235, What reports must I submit?
Model Rule, Title V Operating Permits
40 CFR 60.5240, Am I required to apply for and obtain a Title V operating permit for my existing SSI unit?
40 CFR 60.5245, When must I submit a Title V permit application for my existing SSI unit?
Model Rule, Definitions
40 CFR 60.5250, What definitions must I know?
TABLES
Table 2 to Subpart MMMM of 40 CFR Part 60, Model Rule, Emission Limits and Standards for Existing Fluidized Bed Sewage Sludge Incineration Units.
Table 3 to Subpart MMMM of 40 CFR Part 60, Model Rule, Emission Limits and Standards for Existing Multiple Hearth Sewage Sludge Incineration Units.
Table 4 to Subpart MMMM of 40 CFR Part 60, Model Rule, Operating Parameters for Existing Sewage Sludge Incineration Units.
Table 5 to Subpart MMMM of 40 CFR Part 60, Model Rule, Toxic Equivalency Factors.
Table 6 to Subpart MMMM of 40 CFR Part 60, Model Rule, Summary of Reporting Requirements for Existing Sewage Sludge Incineration Units.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; federal Clean Air Act (§§ 110, 111, 123, 129, 171, 172, and 182); 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 28, Issue 23, eff. August 15, 2012.
Article 56
Emission Standards for Letterpress Printing Operations in the Northern Virginia Volatile Organic Compound Emissions Control Area, 8-Hour Ozone Standard (Rule 4-56)
9VAC5-40-8380. Applicability and designation of affected facility.
Article 56
Emission Standards for Letterpress Printing Operations in the Northern Virginia Volatile Organic Compound Emissions Control Area, 8-hour Ozone Standard (Rule 4-56)
A. The affected facility to which the provisions of this article apply is any letterpress printing operation at a stationary source where the actual emissions of volatile organic compounds (VOCs) from all aspects of letterpress printing operations, including related cleaning activities, before the consideration of controls, are equal to or exceed 3.0 tons per 12-month rolling period.
B. The provisions of this article apply only to sources of VOCs located in the Northern Virginia VOC Emissions Control Area designated in subdivision 1 a of 9VAC5-20-206.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8382. Definitions.
A. For the purpose of applying this article in the context of the regulations for the control and abatement of air pollution and related uses, the words or terms shall have the meanings given them in subsection C of this section.
B. Unless otherwise required by context, all terms not defined in this section shall have the meanings given them in 9VAC5-170 (Regulation for General Administration), 9VAC5-10 (General Definitions), or commonly ascribed to them by recognized authorities, in that order of priority.
C. Terms defined.
"Cleaning materials" means any washes, cleaners, solvents, or rejuvenators that are used to remove excess printing inks, oils, and residual paper from a press, press equipment, or press parts, or used to remove dried ink from areas around a press. Cleaning materials include solvents and cleaners used for manual cleaning, and cleaning solutions used by automatic cleaning systems such as roller wash and type wash. Cleaning materials do not include cleaners used for cleaning electronic components of a press, pre-press cleaning operations (e.g., platemaking), post-press cleaning operations (e.g., binding), cleaning supplies such as detergents used to clean the floor (other than to remove dried ink from areas around a press), and cleaning performed in parts washers and cold cleaners subject to Article 47 (9VAC5-40-6820 et seq.) of Part II of 9VAC5-40 (Existing Stationary Sources).
"Composite partial vapor pressure" means the sum of the partial pressures of the compounds defined as volatile organic compounds. Composite partial vapor pressure is calculated as follows:
where:
Wi | = | Weight of the "i"th VOC compound, in grams. |
Ww | = | Weight of water, in grams. |
We | = | Weight of exempt compound, in grams. |
MWi | = | Molecular weight of the "i"th VOC compound, in grams/gram-mole. |
MWw | = | Molecular weight of water, in grams/gram-mole. |
MWe | = | Molecular weight of exempt compound, in grams/gram-mole. |
PPc | = | VOC composite partial pressure at 20°C, in millimeters of mercury (mm Hg). |
VPi | = | Vapor pressure of the "i"th VOC compound at 20°C, in mm Hg. |
"First installation date" means the date that a control device is first installed for the purpose of controlling emissions. The first installation date does not change if the control device is later moved to a new location or installed on a different press.
"Heatset" means a printing process in which heat from a dryer is used to evaporate ink oils from the substrate.
"Letterpress printing" means a printing process in which the image area is raised relative to the nonimage area and paste ink is transferred to the substrate directly from the image surface.
"Letterpress printing operation" means one or more printing processes employing letterpress printing on printing presses and the related processes necessary to directly support the operation of those presses including, but not limited to, cleaning, pre-press, and post-press operations.
"Non-heatset" means a printing process in which the printing inks are set and dried by absorption or oxidation rather than heat. For the purposes of this article, UV-cured and electron beam-cured inks are considered non-heatset.
"Press" means a printing production assembly composed of one or more units to produce a printed substrate (sheet or web).
"Printing" means a photomechanical process in which a transfer of text, designs, and images occurs through contact of an image carrier with a substrate.
"Printing process" means any operation or system wherein printing ink or a combination of printing ink and surface coating is applied, dried, or cured and that is subject to the same emission standard. A printing process may include any equipment that applies, conveys, dries, or cures inks or surface coatings, including, but not limited to, flow coaters, flashoff areas, presses, digital output devices, heaters, dryers, drying areas, and ovens.
"Sheet-fed" means a printing process in which individual sheets of substrate are fed into the press sequentially.
"Theoretical potential to emit" means for the purposes of this article the maximum capacity of a letterpress printing process to emit VOC and shall be based on emissions at design capacity or maximum production and maximum operating hours (8,760 hours/year) before add-on controls, unless the letterpress printing process is subject to state and federally enforceable permit conditions that limit production rates or hours of operation.
"12-month rolling period" means a period that is determined monthly and consists of the previous 12 consecutive calendar months.
"Unit" means, for the purposes of this article, the smallest complete printing component, composed of an inking system, of a letterpress printing press.
"VOC" means volatile organic compound.
"Web" means a continuous roll of printing substrate.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8384. Standard for volatile organic compounds.
A. No owner or other person shall use or permit the use of any letterpress printing press, letterpress printing process, or other letterpress printing operation that is subject to this article unless that press, process, or operation meets the requirements of this section.
B. The following provisions apply to each dryer on each heatset web letterpress printing process, except that these provisions do not apply to (i) any heatset web letterpress printing process with a theoretical potential to emit less than 25 tons per year of VOC (petroleum ink oil) from the dryer, prior to controls; (ii) any heatset web letterpress printing process used exclusively for book printing; or (iii) any heatset web letterpress printing process with a maximum web width of 22 inches or less. These provisions also do not apply to non-heatset web letterpress printing processes or to sheet-fed letterpress printing processes.
1. VOC emissions from the heatset web letterpress printing process dryer shall be controlled as follows:
a. The dryer shall operate at a lower air pressure than the pressroom air pressure at all times when the printing process is operating.
b. Exhaust air from the dryer shall be collected and sent to a control device that operates at all times when the printing process is operating.
c. For a control device whose first installation date is prior to February 1, 2016, the control device shall reduce VOC emissions in the dryer air exhaust by at least 90%.
d. For a control device whose first installation date is on or after February 1, 2016, the control device shall reduce VOC emissions in the dryer air exhaust by at least 95%.
2. Where the heatset web letterpress printing process control device inlet VOC concentration is too low to achieve the control device efficiency requirements specified in subdivisions 1 c and 1 d of this subsection or there is no identifiable measurable inlet, the control device shall reduce the VOC concentration of the heatset web letterpress printing process dryer exhaust air to 20 parts per million volume (ppmv) or less, as hexane on a dry basis.
3. Federally enforceable limitations on (i) the VOC (petroleum ink oil) content of inks and coatings applied prior to the dryer, (ii) the total amounts of inks and coatings applied, (iii) the press application rates of inks and coatings, or (iv) the hours of press operation may be used to meet the 25 ton per year exception to this subsection.
C. Cleaning materials used at each letterpress printing operation shall meet one of the following limits, as applied:
1. A VOC content of 70% by weight; or
2. A composite vapor pressure of 10 mm Hg at 20°C.
The use of cleaning materials not meeting the limits in subdivision 1 or 2 of this subsection is permitted provided that the quantity of cleaning material used does not exceed 110 gallons over any 12-month rolling period.
D. The following work practices shall be implemented:
1. Cleaning materials, inks, and coatings containing VOCs shall be kept in closed containers at all times unless filling, draining, or performing cleaning operations.
2. Shop towels, sponges, and other manual cleaning aids (i) that have been used for picking up excess ink and other coatings containing VOCs or (ii) that have been used with cleaning materials containing VOCs shall be kept in closed containers.
3. Spills of cleaning materials, fountain solution, inks, varnishes, and other coatings containing VOCs shall be minimized and shall be cleaned up promptly.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8386. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of Part II of 9VAC5-40 (Existing Stationary Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8388. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of Part II of 9VAC5-40 (Existing Stationary Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8390. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of Part II of 9VAC5-40 (Existing Stationary Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8394. Standard for toxic pollutants.
The provisions of Article 4 (9VAC5-60-200 et seq.) of Part II of 9VAC5-60 (Hazardous Air Pollutant Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8396. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. If requested by the board, an emission test of the control device installed on a heatset web letterpress printing process dryer shall be performed to demonstrate compliance with the provisions of 9VAC5-40-8384 B. The negative dryer pressure shall be established during the initial test using an airflow direction indicator, such as a smoke stick or aluminum ribbons, or a differential pressure gauge. The board may accept the results of an emission test conducted prior to February 1, 2016, if the owner or operator provides information and data that demonstrate that the test demonstrated compliance with the provisions of 9VAC5-40-8384 B.
C. Continuing compliance with the heatset web letterpress printing process dryer control requirements in 9VAC5-40-8384 B shall be demonstrated for the catalytic or thermal oxidation control device by monitoring the control device in accordance with 9VAC5-40-8410 B. The owner shall maintain the three-hour average of the monitored temperature at a temperature no less than 50°F below the three-hour average temperature that was recorded during the most recent performance test during which compliance was demonstrated. In the absence of performance test results acceptable to the board that provide dryer control device temperatures that demonstrate continuing compliance with the requirements in 9VAC5-40-8384 B, control device temperatures that demonstrate compliance with manufacturer recommendations may be considered by the board to demonstrate compliance with heatset web offset letterpress printing process dryer control requirements in 9VAC5-40-8384 B.
D. A portion of the volatile organic compounds contained in inks and cleaning solution is retained in the printed web and in the shop towels used for cleaning. When applicable, the following retention factors may be used in determining volatile organic compounds emissions from letterpress printing operations:
1. A 20% volatile organic compound retention factor may be used for petroleum ink oils contained in heatset inks that are printed on absorptive substrates, meaning that 80% of the VOC (petroleum ink oil) in the ink is emitted during the printing process and is available for capture and control by an add-on pollution control device.
2. A 100% volatile organic compound retention factor may be used for vegetable ink oils contained in heatset inks that are printed on absorptive substrates, meaning that none of the VOC (vegetable ink oil) in the ink is emitted during the printing process and available for capture and control by an add-on pollution control device.
3. A 95% volatile organic compound retention factor may be used for petroleum ink oils contained in sheet-fed and non-heatset web inks printed on absorptive substrates, meaning that 5.0% of the VOC (petroleum ink oil) in the ink is emitted during the printing process.
4. A 100% volatile organic compound retention factor may be used for vegetable ink oils contained in sheet-fed and non-heatset web inks printed on absorptive substrates, meaning that none of the VOC (vegetable ink oil) in the ink is emitted during the printing process.
5. A 50% volatile organic compound retention factor may be used for cleaning solution VOC in shop towels for those cleaning solutions with a volatile organic compounds composite vapor pressure of no more than 10 millimeters of mercury (Hg) at 20°C (68°F) provided that the cleaning materials and used shop towels are kept in closed containers.
E. A portion of the volatile organic compounds contained in inks is captured for control by add-on air pollution control equipment. When applicable, the following capture efficiencies may be used in determining volatile organic compounds emissions from letterpress printing operations:
1. A 100% volatile organic compound capture efficiency may be used for VOC (petroleum ink oils) from oil-based paste inks and oil-based paste varnishes (coatings) when the dryer is demonstrated to be operating at negative pressure relative to the surrounding pressroom.
2. Conventional letterpress inks and varnishes are paste-type materials. If other types of inks or coating materials are used on a letterpress press (e.g., fluid inks or coatings), capture efficiency testing shall be conducted for the VOC from these other materials if the printer wants to take into account the effect that the dryer controls have on VOC emissions from these other types of inks or coatings.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8398. Compliance schedule.
The owner shall comply with the provisions of this article as expeditiously as possible but in no case later than February 1, 2017.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8400. Test methods and procedures.
A. The provisions of 9VAC5-40-30 (Emission testing) apply.
B. The following EPA test methods shall be used to demonstrate compliance with the heatset web letterpress printing process dryer control device control requirements in 9VAC5-40-8384 B.
1. Reference Method 1 or 1A, as appropriate, shall be used to select the sampling sites.
2. Reference Method 2, 2A, 2C, or 2D, as appropriate, shall be used to determine the velocity and volumetric flow rate of the exhaust stream.
3. Reference Method 3 or 3A, as appropriate, shall be used to determine the concentration of O2 and CO2.
4. Reference Method 4 shall be used to determine moisture content.
5. Reference Methods 18, 25, or 25A shall be used to determine the VOC concentration of the dryer exhaust stream entering and exiting the control device, unless the alternate limit in 9VAC5-40-8384 B 2 is being met, in which case only the VOC concentration of the dryer exhaust control device outlet shall be determined.
6. Reference Method 25A shall be used to determine the dryer exhaust control device inlet and outlet VOC concentrations when the control device outlet concentration is less than 50 parts per million volume (ppmv) VOC as carbon.
7. If the control device is an oxidizer, the combustion chamber temperature or catalyst bed inlet temperature corresponding to destruction efficiencies that meet the requirements of 9VAC5-40-8384 B shall be recorded.
C. The VOC content of as-applied inks, coatings, and cleaning materials shall be determined using Reference Method 24.
1. The analysis of as-supplied materials may be performed by the manufacturer or the supplier. Formulation information from the manufacturer may be used in lieu of Reference Method 24 analysis unless the board or the owner has reason to believe that the formulation information provided by the manufacturer is inaccurate.
2. The owner may use VOC content information provided by the manufacturer or supplier, such as the container label, the product data sheet, or the Safety Data Sheet (SDS) to document the VOC content of the as-supplied material.
3. If cleaning materials are diluted by the owner prior to use, a calculation that combines the as-supplied VOC content information provided by the manufacturer or supplier, the VOC content of the diluent, and the proportions in which they are mixed may be used to make a determination of VOC content of the as-applied cleaning material in lieu of Reference Method 24.
4. The owner shall conduct Reference Method 24 testing of any as-applied cleaning material used for letterpress printing operations at any time at the board's request. The owner shall be prepared to sample as-applied fountain solution or cleaning materials at all times.
D. The VOC composite partial vapor pressure of cleaning solutions shall be determined using the formula provided in 9VAC5-40-8382 C or by an appropriate test method approved by the board.
1. The determination VOC composite partial vapor pressure for as-supplied cleaning solutions may be performed by the manufacturer or the supplier. The determination of as-applied composite vapor pressure based upon the manufacturer's instructions for dilution may be performed by the manufacturer or supplier.
2. The owner may use VOC composite partial vapor pressure information provided by the manufacturer or supplier, such as the container label, the product data sheet, or the Safety Data Sheet (SDS) to document the VOC composite partial vapor pressure of the as-supplied or as-applied cleaning materials.
3. The following provisions apply to the determination of VOC composite partial vapor pressure for cleaning materials that are diluted by the owner prior to use:
a. If the dilution is made according to the manufacturer's instructions, the VOC composite partial vapor pressure for the as-applied cleaning material provided by the manufacturer or supplier may be used.
b. If a dilution is made and an as-applied VOC composite partial vapor pressure has not been provided by the manufacturer or supplier, or if the dilution is not made according to the manufacturer's instructions, then the owner shall determine the VOC composite partial vapor pressure using the calculation method provided in 9VAC5-40-8382 C or by an appropriate test method approved by the board.
4. The owner shall conduct testing of any as-applied cleaning materials used for letterpress printing operations at any time at the board's request. The owner shall be prepared to sample as-applied cleaning materials at all times.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8410. Monitoring.
A. The provisions of 9VAC5-40-40 (Monitoring) apply.
B. Periodic monitoring of letterpress printing operations shall be conducted as follows:
1. The temperature of a catalytic or thermal oxidation control device shall be monitored at least once every 15 minutes while the printing process is operating, and that temperature shall be recorded by an analog or digital recording device.
a. For a catalytic oxidizer, the dryer exhaust temperature upstream of the catalyst bed shall be monitored and recorded.
b. For a thermal oxidizer, the combustion chamber temperature of the oxidizer shall be monitored and recorded.
2. Catalyst bed material in a catalytic oxidation control device shall be inspected annually for general catalyst condition and any signs of potential catalyst depletion. Sampling and evaluation of the catalyst bed material shall be conducted whenever the results of the inspection indicate signs of potential catalyst depletion or poor catalyst condition based on manufacturer's recommendations, but not less than once per year.
3. If a heatset web letterpress printing process is interlocked to ensure that the control device is operating and airflow is present when the printing process is operating, then periodic monitoring of dryer air flow is not required. If no interlock is present, then the printing process dryer air flow shall be verified and recorded once per operating day.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8412. Notification, records, and reporting.
The provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8414. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8416. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8418. Permits.
A permit may be required prior to beginning any of the activities specified in this section if the provisions of 9VAC5-50 (New and Modified Stationary Sources) and 9VAC5-80 (Permits for Stationary Sources) apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (re-startup) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
Article 56.1
Emission Standards for Offset Lithographic Printing Operations in the Northern Virginia Volatile Organic Compound Emissions Control Area, 8-Hour Ozone Standard (Rule 4-56.1)
9VAC5-40-8420. Applicability and designation of affected facility.
Article 56.1
Emission Standards for Offset Lithographic Printing Operations in the Northern Virginia Volatile Organic Compound Emissions Control Area, 8-hour Ozone Standard (Rule 4-56.1)
A. The affected facility to which the provisions of this article apply is any offset lithographic printing operation at a stationary source where the actual emissions of volatile organic compounds (VOCs) from all aspects of offset lithographic printing operations, including related cleaning activities, before the consideration of controls are equal to or exceed 3.0 tons per 12-month rolling period.
B. The provisions of this article apply only to sources of VOCs located in the Northern Virginia VOC Emissions Control Area designated in subdivision 1 a of 9VAC5-20-206.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8422. Definitions.
A. For the purpose of applying this article in the context of the regulations for the control and abatement of air pollution and related uses, the words or terms shall have the meanings given them in subsection C of this section.
B. Unless otherwise required by context, all terms not defined in this section shall have the meanings given them in 9VAC5-170 (Regulation for General Administration), 9VAC5-10 (General Definitions), or commonly ascribed to them by recognized authorities, in that order of priority.
C. Terms defined.
"Alcohol" means any of the following compounds when used as a fountain solution additive: ethanol, n-propanol, and isopropanol.
"Alcohol substitute" means any nonalcohol additive that contains volatile organic compounds and is used in the fountain solution.
"Batch" means a supply of fountain solution or cleaning solution that is prepared and used without alteration until completely used or removed from the printing process.
"Cleaning materials" means any washes, cleaners, solvents, or rejuvenators that are used to remove (i) excess printing inks, oils, and residual paper from a press, press equipment, or press parts or (ii) dried ink from areas around a press. Cleaning materials include solvents and cleaners used for manual cleaning and cleaning solutions used by automatic cleaning systems such as blanket wash, plate cleaner, metering roller cleaner, impression cylinder washes, rubber rejuvenators, and roller wash. Cleaning materials do not include cleaners used for cleaning electronic components of a press, pre-press cleaning operations (e.g., platemaking), post-press cleaning operations (e.g., binding), cleaning supplies such as detergents used to clean the floor (other than to remove dried ink from areas around a press), and cleaning performed in parts washers and cold cleaners subject to Article 47 (9VAC5-40-6820 et seq.) of Part II of 9VAC5-40 (Existing Stationary Sources).
"Composite partial vapor pressure" means the sum of the partial pressures of the compounds defined as volatile organic compounds. Composite partial vapor pressure is calculated as follows:
where:
Wi | = | Weight of the "i"th VOC compound, in grams. |
Ww | = | Weight of water, in grams. |
We | = | Weight of exempt compound, in grams. |
MWi | = | Molecular weight of the "i"th VOC compound, in grams/gram-mole. |
MWw | = | Molecular weight of water, in grams/gram-mole. |
MWe | = | Molecular weight of exempt compound, in grams/gram-mole. |
PPc | = | VOC composite partial pressure at 20°C, in millimeters of mercury (mm Hg). |
VPi | = | Vapor pressure of the "i"th VOC compound at 20°C, in mm Hg. |
"First installation date" means the date that a control device is first installed for the purpose of controlling emissions. The first installation date does not change if the control device is later moved to a new location or installed on a different press.
"Fountain solution" means any mixture of water, volatile and nonvolatile chemicals, and additives applied to a lithographic plate to repel ink from the nonimage area on the plate.
"Heatset" means a printing process in which heat from a dryer is used to evaporate ink oils from the substrate.
"Heatset web offset lithographic printing dryer" means the dryer or dryers installed as part of a heatset web offset lithographic printing process that dries inks or surface coatings.
"Lithographic printing" means a planographic printing process in which the image and nonimage areas are chemically differentiated with the image area being oil receptive and the nonimage area being water receptive. This process differs from other printing processes, where the image is a raised or recessed surface.
"Non-heatset" means a printing process in which the printing inks are set and dried by absorption or oxidation rather than heat. For the purposes of this article, UV-cured and electron beam-cured inks are considered non-heatset.
"Offset lithographic printing" means a printing process that transfers the ink film from the lithographic plate to an intermediary surface (blanket), which, in turn, transfers the ink film to the substrate.
"Offset lithographic printing operation" means one or more printing processes employing offset lithographic printing on printing presses and includes the related processes necessary to directly support the operation of those offset lithographic printing processes including, but not limited to, pre-press and post-press operations. Varnishes, glues, and other coatings that are applied by an offset lithographic printing process are part of offset lithographic printing operations and are not considered as a separate process (e.g., paper coating).
"Press" means a printing production assembly composed of one or more units to produce a printed substrate (sheet or web).
"Printing" means a photomechanical process in which a transfer of text, designs, and images occurs through contact of an image carrier with a substrate.
"Printing process" means any operation or system wherein printing ink or a combination of printing ink and surface coating is applied, dried, or cured and that is subject to the same emission standard. A printing process may include any equipment that applies, conveys, dries, or cures inks or surface coatings, including, but not limited to, flow coaters, flashoff areas, presses, digital output devices, fountain solutions, heaters, dryers, drying areas, and ovens.
"Sheet-fed" means a printing process in which individual sheets of substrate are fed into the press sequentially.
"Theoretical potential to emit" means for the purposes of this article the maximum capacity of a heatset web offset lithographic printing process to emit VOC and shall be based on emissions at design capacity or maximum production and maximum operating hours (8,760 hours/year) before add-on controls, unless the heatset web offset lithographic printing process is subject to state and federally enforceable permit conditions that limit production rates or hours of operation.
"12-month rolling period" means a period that is determined monthly and consists of the previous 12 consecutive calendar months.
"Unit" means the smallest complete printing component, composed of an inking system, of a printing press.
"VOC" means volatile organic compound.
"Web" means a continuous roll of printing substrate.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8424. Standard for volatile organic compounds.
A. No owner or other person shall use or permit the use of any offset lithographic printing press, offset lithographic printing process, or other offset lithographic printing operation that is subject to this article unless that press, process, or operation meets the requirements of this section.
B. Except as provided in subdivision 3 of this subsection, the following provisions apply to each heatset offset lithographic printing process at a facility whose potential to emit is greater than or equal to 10 tons per year of VOC, provided that the emission rates are determined in a manner acceptable to the board. All VOC emissions from printing inks, coatings, cleaning solutions, and fountain solutions shall be considered in determining the potential to emit for this subsection.
1. VOC emissions from the heatset web offset lithographic printing process dryer shall be controlled as follows:
a. The dryer shall operate at a lower air pressure than the pressroom air pressure at all times when the printing process is operating.
b. Exhaust air from the dryer shall be collected and sent to a control device that operates at all times when the printing process is operating.
c. The control device shall reduce VOC emissions in the dryer air exhaust by at least 90%.
2. Where the heatset web offset lithographic printing process control device inlet VOC concentration is too low to achieve the control device efficiency requirements specified in subdivision 1 c of this subsection or there is no identifiable measurable inlet, the control device shall reduce the VOC concentration of the heatset web offset lithographic printing process dryer exhaust air to 50 parts per million volume (ppmv) or less, as carbon (minus methane and ethane).
3. The provisions in subdivisions 1 and 2 of this subsection do not apply to the following:
a. Any heatset web offset lithographic printing process with a theoretical potential to emit of 25 tons per year of VOC (petroleum ink oil) or more from the heatset web offset lithographic printing dryer. VOC standards for heatset web offset lithographic printing process with a theoretical potential to emit of 25 tons per year of VOC (petroleum ink oil) or more are provided in subsection C of this section.
b. Printing processes used exclusively for determination of product quality and commercial acceptance provided:
(1) The operation is not an integral part of the production process;
(2) The emissions from all product quality printing processes do not exceed 400 pounds in any 30-day period; and
(3) The exemption is approved by the board.
c. Photoprocessing, typesetting, or imagesetting equipment using water-based chemistry to develop silver halide images.
d. Platemaking equipment using water-based chemistry to remove unhardened image-producing material from an exposed plate.
e. Equipment used to make blueprints.
f. Any sheet-fed offset lithographic press with a cylinder width of 26 inches or less.
C. Except as provided in subdivisions 3, 4, and 5 of this subsection, the following provisions apply to each heatset web offset lithographic printing process with a theoretical potential to emit of 25 tons per year of VOC (petroleum ink oil) or more from the dryer. These provisions do not apply to non-heatset web offset lithographic printing processes or to sheet-fed offset lithographic printing processes.
1. VOC emissions from the heatset web offset lithographic printing process dryer shall be controlled as follows:
a. The dryer shall operate at a lower air pressure than the pressroom air pressure at all times when the printing process is operating.
b. Exhaust air from the dryer shall be collected and sent to a control device that operates at all times when the printing process is operating.
c. For a control device whose first installation date is prior to February 1, 2016, the control device shall reduce VOC emissions in the dryer air exhaust by at least 90%.
d. For a control device whose first installation date is on or after February 1, 2016, the control device shall reduce VOC emissions in the dryer air exhaust by at least 95%.
2. Where the heatset web offset lithographic printing process control device inlet VOC concentration is too low to achieve the control device efficiency requirements specified in subdivisions 1 c and 1 d of this subsection or there is no identifiable measurable inlet, the control device shall reduce the VOC concentration of the heatset web offset lithographic printing process dryer exhaust air to 20 parts per million volume (ppmv) or less, as hexane on a dry basis.
3. Federally enforceable limitations on (i) the VOC (petroleum ink oil) content of inks, varnishes, and other coatings applied prior to the dryer; (ii) the total amounts of inks, varnishes, and other coatings applied; (iii) the press application rates of inks, varnishes, and other coatings; or (iv) the hours of press operation may be used to meet the 25 ton per year exception to this subsection.
4. The provisions of subdivisions 1 and 2 of this subsection do not apply to (i) any heatset web offset lithographic printing process constructed on or after February 1, 2016, and used exclusively for book printing or (ii) any heatset web offset lithographic printing process constructed on or after February 1, 2016, with a maximum web width of 22 inches or less.
5. The heatset web offset lithographic printing process dryer control device provisions of subdivision 1 d of this subsection do not apply to (i) any heatset web offset lithographic printing process used exclusively for book printing; or (ii) any heatset web offset lithographic printing process with a maximum web width of 22 inches or less.
D. The following provisions shall apply to fountain solution applied to each offset lithographic printing press, except that these provisions shall not apply to (i) sheet-fed offset lithographic printing processes with a sheet size of 11 inches by 17 inches or smaller or (ii) sheet-fed offset lithographic printing processes with a total fountain solution reservoir of less than one gallon.
1. For each heatset web press:
a. When the fountain solution contains alcohol:
(1) The fountain solution, as applied, shall contain no more than 1.6% volatile organic compounds by weight; or
(2) The temperature of the fountain solution shall be maintained at or below 60°F and the fountain solution, as applied, shall contain no more than 3.0% VOCs by weight; or
b. When the fountain solution contains no alcohol, the fountain solution, as applied, shall contain no more than 5.0% VOCs by weight.
2. For each non-heatset web press, the fountain solution, as applied, shall contain no alcohol and shall contain no more than 5.0% VOCs by weight.
3. For each sheet-fed press:
a. The fountain solution, as applied, shall contain no more than 5.0% VOCs by weight; or
b. The temperature of the fountain solution shall be maintained at or below 60°F and the fountain solution, as applied, shall contain no more than 8.5% VOCs by weight.
E. Cleaning materials used at each offset lithographic printing operation shall meet one of the following limits, as applied:
1. A VOC content of 30% by weight; or
2. A composite vapor pressure of 10 mm Hg at 20°C (68°F).
The use of cleaning materials not meeting the limits in subdivision 1 or 2 of this subsection is permitted provided that the quantity of cleaning material used does not exceed 110 gallons over any 12-month rolling period.
F. The following work practices shall be implemented.
1. Cleaning materials, fountain solution, inks, varnishes, and coatings containing VOCs shall be kept in closed containers at all times unless filling, draining, or performing cleaning operations.
2. Shop towels, sponges, and other manual cleaning aids that (i) have been used for picking up excess ink, fountain solution, varnishes, and other coatings containing VOCs or (ii) have been used with cleaning materials containing VOCs shall be kept in closed containers.
3. Spills of cleaning materials, fountain solution, inks, varnishes, and other coatings containing VOCs shall be minimized and shall be cleaned up promptly.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8426. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of Part II of 9VAC5-40 (Existing Stationary Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8428. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of Part II of 9VAC5-40 (Existing Stationary Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8430. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of Part II of 9VAC5-40 (Existing Stationary Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8432. Standard for toxic pollutants.
The provisions of Article 4 (9VAC5-60-200 et seq.) of Part II of 9VAC5-60 (Hazardous Air Pollutant Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8434. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. If requested by the board, an emission test of the control device installed on a heatset web offset lithographic printing process dryer shall be performed to demonstrate compliance with the provisions of 9VAC5-40-8424 B and C. The negative dryer pressure shall be established during the initial test using an airflow direction indicator, such as a smoke stick or aluminum ribbons, or a differential pressure gauge. The board may accept the results of an emission test conducted prior to the compliance date specified in 9VAC5-40-8436 if the owner or operator provides information and data that demonstrate that the test demonstrated compliance with the provisions of 9VAC5-40-8424 B and C.
C. Continuing compliance with the heatset web offset lithographic printing process dryer control requirements in 9VAC5-40-8424 B and C shall be demonstrated for the catalytic or thermal oxidation control device by monitoring the control device in accordance with 9VAC5-40-8440 B 3, B 4, and B 5. The owner shall maintain the three-hour average of the monitored temperature at a temperature no less than 50°F below the three-hour average temperature that was recorded during the most recent performance test during which compliance was demonstrated. In the absence of performance test results acceptable to the board that provide dryer control device temperatures that demonstrate continuing compliance with the requirements in 9VAC5-40-8424 B and C, control device temperatures that demonstrate compliance with manufacturer recommendations may be considered by the board to demonstrate compliance with heatset web offset lithographic printing process dryer control requirements in 9VAC5-40-8424 B and C.
D. A portion of the volatile organic compounds contained in inks and cleaning solution is retained in the printed web and in the shop towels used for cleaning. When applicable, the following retention factors may be used in determining volatile organic compounds emissions from offset lithographic printing operations:
1. A 20% volatile organic compound retention factor may be used for petroleum ink oils contained in heatset inks that are printed on absorptive substrates, meaning that 80% of the VOC (petroleum ink oil) in the ink is emitted during the printing process and is available for capture and control by an add-on pollution control device.
2. A 100% volatile organic compound retention factor may be used for vegetable ink oils contained in heatset inks that are printed on absorptive substrates, meaning that none of the VOC (vegetable ink oil) in the ink is emitted during the printing process and available for capture and control by an add-on pollution control device.
3. A 95% volatile organic compound retention factor may be used for petroleum ink oils contained in sheet-fed and non-heatset web inks printed on absorptive substrates, meaning that 5.0% of the VOC (petroleum ink oil) in the ink is emitted during the printing process.
4. A 100% volatile organic compound retention factor may be used for vegetable ink oils contained in sheet-fed and non-heatset web inks printed on absorptive substrates, meaning that none of the VOC (vegetable ink oil) in the ink is emitted during the printing process.
5. A 50% volatile organic compound retention factor may be used for cleaning solution VOC in shop towels for those cleaning solutions with a volatile organic compounds composite vapor pressure of no more than 10 millimeters of mercury (Hg) at 20°C (68°F) provided that the cleaning materials and used shop towels are kept in closed containers.
E. A portion of the volatile organic compounds contained in inks, fountain solutions, and automatic blanket washes is captured for control by add-on air pollution control equipment. When applicable, the following capture efficiencies may be used in determining volatile organic compounds emissions from offset lithographic printing operations:
1. A 40% volatile organic compound capture efficiency may be used for automatic blanket washing when the VOC composite vapor pressure of the cleaning material is less than 10 millimeters of mercury (Hg).
2. A 70% volatile organic compound capture efficiency may be used for alcohol substitutes in fountain solutions.
3. A 100% volatile organic compound capture efficiency may be used for VOC (petroleum ink oils) from oil-based paste inks and oil-based paste varnishes (coatings) when the dryer is demonstrated to be operating at negative pressure relative to the surrounding pressroom.
4. Conventional heatset lithographic inks and varnishes are paste-type materials. If other types of inks or coating materials are used on a heatset lithographic press (e.g., fluid inks or coatings), capture efficiency testing shall be conducted for the VOC from these other materials if the printer wants to take into account the effect that the dryer controls have on VOC emissions from these other types of inks or coatings.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8436. Compliance schedule.
The owner shall comply with the provisions of this article as expeditiously as possible but in no case later than February 1, 2017.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8438. Test methods and procedures.
A. The provisions of 9VAC5-40-30 (Emission testing) apply.
B. The following EPA test methods shall be used to demonstrate compliance with the heatset web offset lithographic printing process dryer control device control requirements in 9VAC5-40-8424 B and C.
1. Reference Method 1 or 1A, as appropriate, shall be used to select the sampling sites.
2. Reference Method 2, 2A, 2C, or 2D, as appropriate, shall be used to determine the velocity and volumetric flow rate of the exhaust stream.
3. Reference Method 3 or 3A, as appropriate, shall be used to determine the concentration of O2 and CO2.
4. Reference Method 4 shall be used to determine moisture content.
5. Reference Methods 18, 25, or 25A shall be used to determine the VOC concentration of the dryer exhaust stream entering and exiting the control device, unless the alternate limit in 9VAC5-40-8424 B 2 or C 2 is being met, in which case only the VOC concentration of the dryer exhaust control device outlet shall be determined.
6. Reference Method 25A shall be used to determine the dryer exhaust control device inlet and outlet VOC concentrations when the control device outlet concentration is less than 50 parts per million volume (ppmv) VOC as carbon.
7. If the control device is an oxidizer, the combustion chamber temperature or catalyst bed inlet temperature corresponding to destruction efficiencies that meet the requirements of 9VAC5-40-8424 B or C, as appropriate, shall be recorded.
C. The VOC content of as-applied inks, varnishes and other coatings, fountain solutions, and cleaning materials shall be determined using Reference Method 24.
1. The analysis of as-supplied materials may be performed by the manufacturer or the supplier. Formulation information from the manufacturer may be used in lieu of Reference Method 24 analysis unless the board or the owner has reason to believe that the formulation information provided by the manufacturer is inaccurate.
2. The owner may use VOC content information provided by the manufacturer or supplier, such as the container label, the product data sheet, or the Safety Data Sheet (SDS) to document the VOC content of the as-supplied material.
3. If fountain solution or cleaning materials are diluted by the owner prior to use, a calculation that combines the as-supplied VOC content information provided by the manufacturer or supplier, the VOC content of the diluent, and the proportions in which they are mixed may be used to make a determination of VOC content of the as-applied fountain solution or cleaning material in lieu of Reference Method 24.
4. The owner shall conduct Reference Method 24 testing of any as-applied fountain solution or cleaning material used for offset lithographic printing operations at any time at the board's request. The owner shall be prepared to sample as-applied fountain solution or cleaning materials at all times.
D. A thermometer or other temperature detection device capable of reading the temperature of the fountain solution to within 0.5°F shall be used to determine compliance with fountain solution temperature requirements in 9VAC5-40-8424 D.
E. The VOC composite partial vapor pressure of cleaning solutions shall be determined using the formula provided in 9VAC5-40-8422 C or by an appropriate test method approved by the board.
1. The determination VOC composite partial vapor pressure for as-supplied cleaning solutions may be performed by the manufacturer or the supplier. The determination of as-applied composite vapor pressure based upon the manufacturer's instructions for dilution may be performed by the manufacturer or supplier.
2. The owner may use VOC composite partial vapor pressure information provided by the manufacturer or supplier, such as the container label, the product data sheet, or the Safety Data Sheet (SDS), to document the VOC composite partial vapor pressure of the as-supplied or as-applied cleaning materials.
3. The following provisions apply to the determination of VOC composite partial vapor pressure for cleaning materials that are diluted by the owner prior to use:
a. If the dilution is made according to the manufacturer's instructions, the VOC composite partial vapor pressure for the as-applied cleaning material provided by the manufacturer or supplier may be used.
b. If a dilution is made and an as-applied VOC composite partial vapor pressure has not been provided by the manufacturer or supplier, or if the dilution is not made according to the manufacturer's instructions, then the owner shall determine the VOC composite partial vapor pressure using the calculation method provided in 9VAC5-40-8422 C.
4. The owner shall conduct testing of any as-applied cleaning materials used for offset lithographic printing operations at any time at the board's request. The owner shall be prepared to sample as-applied cleaning materials at all times.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8440. Monitoring.
A. The provisions of 9VAC5-40-40 (Monitoring) apply.
B. Periodic monitoring of offset lithographic printing operations shall be conducted as follows:
1. The alcohol concentration of offset lithographic printing process fountain solution shall be monitored with a hydrometer, equipped with temperature correction or with readings adjusted for temperature, and recorded at least once per shift or once per batch, whichever is longer. A standard solution shall be used to calibrate the hydrometer for the type of alcohol used in the fountain.
2. The temperature of refrigerated fountain solution shall be measured at the recirculating tank at least once per operating day.
3. The temperature of a catalytic or thermal oxidation control device shall be monitored at least once every 15 minutes while the printing process is operating, and that temperature shall be recorded by an analog or digital recording device.
a. For a catalytic oxidizer, the dryer exhaust temperature upstream of the catalyst bed shall be monitored and recorded.
b. For a thermal oxidizer, the combustion chamber temperature of the oxidizer shall be monitored and recorded.
4. Catalyst bed material in a catalytic oxidation control device shall be inspected annually for general catalyst condition and any signs of potential catalyst depletion. Sampling and evaluation of the catalyst bed material shall be conducted whenever the results of the inspection indicate signs of potential catalyst depletion or poor catalyst condition based on manufacturer's recommendations, but not less than once per year.
5. If a heatset web offset lithographic printing process is interlocked to ensure that the control device is operating and airflow is present when the printing process is operating, then periodic monitoring of dryer air flow is not required. If no interlock is present, then the printing process dryer air flow shall be verified and recorded once per operating day.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8450. Notification, records, and reporting.
The provisions of 9VAC5-40-50 (Notification, records, and reporting) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8460. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8470. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8480. Permits.
A permit may be required prior to beginning any of the activities specified in this section if the provisions of 9VAC5-50 (New and Modified Stationary Sources) and 9VAC5-80 (Permits for Stationary Sources) apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (re-startup) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
Article 57
Emission Standards for Industrial Solvent Cleaning Operations in the Northern Virginia Volatile Organic Compound Emissions Control Area, 8-Hour Ozone Standard (Rule 4-57)
9VAC5-40-8510. Applicability and designation of affected facility.
Article 57
Emission Standards for Industrial Solvent Cleaning Operations in the Northern Virginia Volatile Organic Compound Emissions Control Area, 8-hour Ozone Standard (Rule 4-57)
A. Except as provided in subsections C and D of this section, the affected facility to which the provisions of this article apply is each facility that uses organic solvent for cleaning unit operations such as mixing vessels (tanks), spray booths, and parts cleaners and that emits, before consideration of controls, at least 6.8 kilograms per day (15 pounds per day) of volatile organic compounds (VOCs). Such operations include, but are not limited to, spray gun cleaning, spray booth cleaning, large manufactured components cleaning, parts cleaning, equipment cleaning, line cleaning, floor cleaning, tank cleaning, and small manufactured components cleaning.
B. The provisions of this article apply only to affected facilities located in the Northern Virginia VOC Emissions Control Area designated in subdivision 1 a of 9VAC5-20-206.
C. Exempted from the provisions of this article are solvent cleaning operations (i) for cleaning of electrical and electronic components; (ii) for cleaning of high precision optics and cleaning of cotton swabs to remove cottonseed oil before cleaning of high precision optics; (iii) for cleaning of numismatic dies; (iv) for cleaning of resin, coating, ink, and adhesive mixing, molding, and application equipment; (v) in research and development laboratories; (vi) in manufacturing medical devices or pharmaceutical products; (vii) related to performance or quality assurance testing of coatings, inks, or adhesives.
D. The provisions of this article do not apply to the following:
1. Surface preparation and solvent cleaning operations associated with the surface coating, application of adhesive, sealants and their primers or printing operations subject to Article 26 (Large Appliance Coatings, 9VAC5-40-3560 et seq.), Article 28 (Automobile and Light Duty Truck Coating Applications, 9VAC5-40-3860 et seq.), Article 33 (Metal Furniture Coating Application Systems, 9VAC5-40-4610 et seq.), Article 34 (Miscellaneous Metal Parts/Products Coating Application, 9VAC5-40-4760), Article 35 (Flatwood Paneling Coating Application Systems, 9VAC5-40-4910 et seq.), Article 53 (Lithographic Printing Processes, 9VAC5-40-7800 et seq.), Article 56 (Letterpress Printing Operations, 9VAC5-40-8380 et seq.), Article 56.1 (Lithographic Printing Operations, 9VAC5-40-8420 et seq.), Article 58 (Miscellaneous Industrial Adhesive Application Processes, 9VAC5-40-8660 et seq.), and Article 59 (Miscellaneous Metal Parts and Products Coating Application Systems, 9VAC5-40-8810 et seq.) of 9VAC5-40 (Existing Stationary Sources).
2. The use of janitorial supplies used for cleaning offices, bathrooms, or other similar areas.
3. Stripping of cured inks, coatings, and adhesives.
4. Surface preparation and solvent cleaning operations associated with the surface coating, application of adhesive, sealants and their primers, or printing operations of the following product categories or processes: aerospace coatings, wood furniture coatings, shipbuilding and repair coatings, flexible packaging printing materials, paper film and foil coating, plastic parts coating, and fiberglass boat manufacturing materials.
5. Solvent metal cleaning operations subject to Article 47 (Emission Standards for Solvent Metal Cleaning Operations in the Northern Virginia Volatile Organic Compound Emissions Control Area, 9VAC5-40-6820 et seq.) of 9VAC5-40 (Existing Stationary Sources).
6. The use of cleaning solvent in a digital printing operation in which an electronic output device transfers variable data, in the form of an image, from a computer to a substrate.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8520. Definitions.
A. For the purpose of applying this article in the context of the regulations for the control and abatement of air pollution and related uses, the words or terms shall have the meanings given them in subsection C of this section.
B. Unless otherwise required by context, all terms not defined in this section shall have the meanings given them in 9VAC5-170 (Regulation for General Administration), 9VAC5-10 (General Definitions), or commonly ascribed to them by recognized authorities, in that order of priority.
C. Terms defined.
"Aerospace coatings" means materials that are applied to the surface of an aerospace vehicle or component to form a decorative, protective, or functional solid film, or the solid film itself at a facility that produces, reworks, or repairs in any amount any commercial, civil, or military aerospace vehicle or component.
"Electrical and electronic components" means components and assemblies of components that generate, convert, transmit, or modify electrical energy. Electrical and electronic components include, but are not limited to, wires, windings, stators, rotors, magnets, contacts, relays, printed circuit boards, printed wire assemblies, wiring boards, integrated circuits, resistors, capacitors, and transistors but does not include the cabinets in which electrical and electronic components are housed.
"Fiberglass boat manufacturing materials" means materials utilized at facilities that manufacture hulls or decks of boats from fiberglass or build molds to make fiberglass boat hulls or decks. Fiberglass boat manufacturing materials are not materials used at facilities that manufacture solely parts of boats (such as hatches, seats, or lockers) or boat trailers, but do not (i) manufacture hulls or decks of boats from fiberglass or (ii) build molds to make fiberglass boat hulls or decks.
"Flexible packaging printing materials" means materials used in the manufacture of any package or part of a package the shape of which can be readily changed. Flexible packaging includes, but is not limited to, bags, pouches, liners, and wraps utilizing paper, plastic, film, aluminum foil, metalized or coated paper or film, or any combination of these materials.
"High precision optics" means an optical element used in an electro-optical device and is designed to sense, detect, or transmit light energy, including specific wavelengths of light energy and changes in light energy levels.
"Industrial cleaning solvents" means products used to remove contaminants such as adhesives, inks, paint, dirt, soil, oil, and grease from parts, products, tools, machinery, equipment, vessels, floors, walls, and other work production related work areas for reasons such as safety, operability, and to avoid product contamination. The cleaning solvents used in these operations may be generally available bulk solvents that are used for a multitude of applications in addition to cleaning, such as for paint thinner, or as an ingredient used in the manufacture of a coating, such as paint.
"Medical device" means an instrument, apparatus, implement, machine, contrivance, implant, in vitro reagent, or other similar article, including any component or accessory that is (i) intended for use in the diagnosis of disease or other conditions, or in the cure, mitigation, treatment, or prevention of diseases; or (ii) intended to affect the structure or any function of the body.
"Paper, film, and foil coating" means coating that is applied to paper, film, or foil surfaces in the manufacturing of several major product types for the following industry sectors: pressure sensitive tape and labels (including fabric coated for use in pressure sensitive tapes and labels); photographic film; industrial and decorative laminates; abrasive products (including fabric coated for use in abrasive products); and flexible packaging (including coating of nonwoven polymer substrates for use in flexible packaging). Paper and film coating also includes coatings applied during miscellaneous coating operations for several products including: corrugated and solid fiber boxes; die-cut paper paperboard, and cardboard; converted paper and paperboard not elsewhere classified; folding paperboard boxes, including sanitary boxes; manifold business forms and related products; plastic aseptic packaging; and carbon paper and inked ribbons.
"Pharmaceutical product" means a preparation or compound, which includes any drug, analgesic, decongestant, antihistamine, cough suppressant, vitamin, mineral or herb supplement intended for human or animal consumption and used to cure, mitigate or treat disease or improve or enhance health.
"Plastic parts coating" means a coating that is applied to the surfaces of a varied range of plastic parts and products. Such parts or products are constructed either entirely or partially from metal or plastic. These parts include, but are not limited to, metal and plastic components of the following types of products as well as the products themselves: fabricated metal products, molded plastic parts, small and large farm machinery, commercial and industrial machinery and equipment, automotive or transportation equipment, interior or exterior automotive parts, construction equipment, motor vehicle accessories, bicycles and sporting goods, toys, recreational vehicles, pleasure craft (recreational boats), extruded aluminum structural components, railroad cars, heavier vehicles, lawn and garden equipment, business machines, laboratory and medical equipment, electronic equipment, steel drums, metal pipes, and numerous other industrial and household products.
"Shipbuilding and repair coating" means material that can be applied as a thin layer to a substrate and which cures to form a continuous solid film, and is used in the building, repair, repainting, converting, or alteration of ships.
"Solvent cleaning operation" means the employment of industrial cleaning solvents to remove loosely held uncured adhesives, uncured inks, uncured coatings, and contaminants, which include, but are not limited to, dirt, soil, and grease, from parts, products, tools, machinery, equipment, and general work areas and includes but is not limited to activities such as wipe cleaning, solvent flushing, or spraying. Each distinct method of cleaning in a cleaning process, which consists of a series of cleaning methods, shall constitute a separate solvent cleaning operation.
"Solvent flushing" means the use of a solvent to remove uncured adhesives, uncured inks, uncured coatings, or contaminants from the internal surfaces and passages of the equipment by flushing solvent through the equipment.
"Surface preparation" means the cleaning of surfaces prior to coating, further treatment, sale, or intended use.
"VOC" means volatile organic compound.
"Wipe cleaning" means the method of cleaning a surface by physically rubbing it with a material such as a rag, paper, sponge, or a cotton swab moistened with a solvent.
"Wood furniture coatings" means protective, decorative, or functional films applied in thin layers to a surface used in the manufacture of wood furniture or wood furniture components. Such coatings include, but are not limited to, paints, topcoats, varnishes, sealers, stains, washcoats, basecoats, enamels, inks, and temporary protective coatings.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8530. Standard for volatile organic compounds.
A. No owner or other person shall cause or permit to be discharged into the atmosphere any VOC emissions from any solvent cleaning operation employing industrial cleaning solvents in excess of both of the following limits:
1. A VOC content limit of 50 grams per liter (0.42 pounds per gallon) of industrial cleaning solvent shall apply unless emissions are controlled by an emission control system with an overall control efficiency of at least 85%; and
2. A composite vapor pressure limit of eight millimeters of mercury at 20°C.
B. VOC emissions from the use, handling, storage, and disposal of industrial cleaning solvents and shop towels shall be controlled by the following work practices:
1. Open containers and used applicators shall be covered.
2. Air circulation around cleaning operations shall be minimized.
3. Used solvent and shop towels shall be disposed of properly.
4. Equipment practices that minimize emissions (including but not limited to keeping arts cleaners covered and maintaining cleaning equipment to repair solvent leaks) shall be implemented.
C. In lieu of complying with the requirements of subsections A and B of this section, a manufacturer of coatings, inks, resin, or adhesives may comply with the following requirements:
1. Clean portable or stationary mixing vats, high dispersion mills, grinding mills, tote tanks, and roller mills by one or more of the following methods:
a. Use a cleaning solvent that either contains less than 1.67 pounds per gallon of VOC or has a composite vapor pressure no more than eight mmHg at 20°C.
b. Comply with the following work practices:
(1) Equipment being cleaned shall be maintained leak free;
(2) VOC-containing cleaning materials shall be drained from the cleaned equipment upon completion of cleaning;
(3) VOC-containing cleaning materials, including waste solvent, shall not be stored or disposed of in such a manner that will cause or allow evaporation into the atmosphere; and
(4) All VOC-containing cleaning materials shall be stored in closed containers.
c. Collect and vent the emissions from equipment cleaning to a VOC emission control system that has an overall capture and control efficiency of at least 80%, by weight, for the VOC emissions. Where such reduction is achieved by incineration, at least 90% of the organic carbon shall be oxidized to carbon dioxide.
d. Use organic solvents other than those allowed in subdivision 1 a of this subsection provided no more than 60 gallons of fresh solvent shall be used per month. Organic solvent that is reused or recycled (either on site or off site) for further use in equipment cleaning or the manufacture of coating, ink, or adhesive shall not be included in this limit. All VOC-containing cleaning materials shall be stored in closed containers.
2. When using solvent for wipe cleaning, the owner shall not (i) use open containers for the storage or disposal of cloth or paper impregnated with organic compounds that is used for cleanup, or coating, ink, or adhesive removal and (ii) store spent or fresh organic compounds to be used for cleanup or coating, ink, resin, or adhesive removal in open containers.
3. Any manufacturer of coatings, inks, resin, or adhesives that complies with subdivision 1 d of this subsection shall record the following information each month for each cleaning material and shall maintain the information at the facility for a period of five years: (i) the total volume of fresh cleaning solvent material used for equipment cleaning and (ii) the total volume of cleaning solvent material recovered for either on-site or off-site recycling.
D. The control requirements for screen printing shall be either use of solvent technology at 4.2 pounds of VOC per gallon, or the use of a product with a vapor pressure of eight mm Hg.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8540. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of Part II of 9VAC5-40 (Existing Stationary Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8550. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of Part II of 9VAC5-40 (Existing Stationary Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8560. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of Part II of 9VAC-40 (Existing Stationary Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8570. Standard for toxic pollutants.
The provisions of Article 4 (9VAC5-60-200 et seq.) of Part II of 9VAC5-60 (Hazardous Air Pollutant Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8580. Compliance.
The provisions of 9VAC5-40-20 (Compliance) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8590. Compliance schedule.
The owner shall comply with the provisions of this article as expeditiously as possible but in no case later than February 1, 2017.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8600. Test methods and procedures.
A. The provisions of 9VAC5-40-30 (Emission testing) apply.
B. The composite vapor pressure of organic compounds in cleaning materials shall be determined by quantifying the amount of each compound in the blend using ASTM "Standard Practice for Packed Column Gas Chromatography" for organics and ASTM "Standard Test Method for Water Content of Coatings by Direct Injection Into a Gas Chromatograph" for water content (see 9VAC5-20-21), as applicable, and the following equation:
where:
Ppc = VOC composite partial pressure at 20ºC, in mm Hg.
Wi = Weight of the "i"th VOC compound, in grams, as determined by
ASTM "Standard Practice for Packed Column Gas Chromatography" (see 9VAC5-20-
21).
Ww = Weight of water, in grams as determined by ASTM "Standard Test
Method for Water Content of Coatings by Direct Injection Into a Gas Chromatograph"
(see 9VAC5-20-21).
We = Weight of the "i"th exempt compound, in grams, as determined by
ASTM "Standard Practice for Packed Column Gas Chromatography" (see 9VAC5-20-21).
Mwi = Molecular weight of the "i"th VOC compound, in grams per g-mole,
as given in chemical reference literature.
Mww = Molecular weight of water, 18 grams per g-mole.
Mwe = Molecular weight of the "i"th exempt compound, in grams per g-mole,
as given in chemical reference literature.
VPi = Vapor pressure of the "i"th VOC compound at 20ºC, in mm Hg, as determined by subsection C of this section.
C. The vapor pressure of each single component compound may be determined from ASTM "Standard Test Method for Vapor Pressure-Temperature Relationship and Initial Decomposition Temperature of Liquids by Isoteniscope" (see 9VAC5-20-21), from chemical reference literature, or from additional sources acceptable to the board.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8610. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8620. Notification, records, and reporting.
The provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8630. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8640. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8650. Permits.
A permit may be required prior to beginning any of the activities specified below if the provisions of 9VAC5-50 (New and Modified Stationary Sources) and 9VAC5-80 (Permits for Stationary Sources) apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (re-startup) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8660. Applicability and designation of affected facility.
Article 58
Emission Standards for Miscellaneous Industrial Adhesive Application Processes in the Northern Virginia Volatile Organic Compound Emissions Control Area, 8-hour Ozone Standard (Rule 4-58)
A. Except as provided in subsection C of this section, the affected facility to which the provisions of this article apply is each miscellaneous industrial adhesive application process at a facility where the total actual volatile organic compound (VOC) emissions from all miscellaneous industrial adhesive application processes, including related cleaning activities and related application of adhesive primers, are, before consideration of controls, either (i) equal to or exceed 6.8 kilograms per day (15 pounds per day) or (ii) three tons per 12-month rolling period.
B. The provisions of this article apply only to sources of VOCs located in the Northern Virginia VOC Emissions Control Area designated in subdivision 1 a of 9VAC5-20-206.
C. The provisions of this article do not apply to the following.
1. Miscellaneous industrial adhesive application process operations subject to Article 6 (Rubber Tire Manufacturing Operations, 9VAC5-40-5810 et seq.), Article 26 (Large Appliance Coatings, 9VAC5-40-3560 et seq.), Article 28 (Automobile and Light Duty Truck Coating Applications, 9VAC5-40-3860 et seq.), Article 30 (Metal Coil Coating Application Systems, 9VAC5-40-4160 et seq.), Article 31 (Paper and Fabric Coating Application Systems, 9VAC5-40-4310 et seq.) Article 33 (Metal Furniture Coating Application Systems, 9VAC5-40-4610 et seq.), Article 35 (Flatwood Paneling Coating Application Systems, 9VAC5-40-4910 et seq.), Article 53 (Lithographic Printing Processes, 9VAC5-40-7800 et seq.), Article 56 (Letterpress Printing Operations, 9VAC5-40-8380 et seq.), Article 56.1 (Lithographic Printing Operations, 9VAC5-40-8420 et seq.), and Article 57 (Industrial Solvent Cleaning Operations, 9VAC5-40-8510 et seq.) of 9VAC5-40 (Existing Stationary Sources).
2. Miscellaneous industrial adhesive application process operations associated with the following product categories or processes: aerospace coatings, flexible packaging printing materials, paper film and foil coating, and fiberglass boat manufacturing materials.
D. The provisions of Article 6 (Emission Standards for Adhesives and Sealants, 9VAC5-45-620 et seq.) of 9VAC5-45 (Consumer and Commercial Products) may apply. In the case of a conflict between these articles, the more restrictive provisions shall apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8670. Definitions.
A. For the purpose of applying this article in the context of the regulations for the control and abatement of air pollution and related uses, the words or terms shall have the meanings given them in subsection C of this section.
B. Unless otherwise required by context, all terms not defined in this section shall have the meanings given them in 9VAC5-170 (Regulation for General Administration), 9VAC5-10 (General Definitions), or commonly ascribed to them by recognized authorities, in that order of priority.
C. Terms defined.
"ABS welding" means any process to weld acrylonitrile-butadiene-styrene pipe.
"Adhesive" means any chemical substance that is applied for the purpose of bonding two surfaces together other than by mechanical means.
"Adhesive primer" means any product intended by the manufacturer for application to a substrate, prior to the application of an adhesive, to provide a bonding surface.
"Aerosol adhesive or adhesive primer" means an adhesive or adhesive primer packaged as an aerosol product in which the spray mechanism is permanently housed in a nonrefillable can designed for handheld application without the need for ancillary hoses or spray equipment.
"Aerospace coatings" means materials that are applied to the surface of an aerospace vehicle or component to form a decorative, protective, or functional solid film, or the solid film itself at a facility that produces, reworks, or repairs in any amount any commercial, civil, or military aerospace vehicle or component.
"Application process" means a series of one or more adhesive applicators and any associated drying area or oven in which an adhesive is applied, dried, or cured. An application process ends at the point where the adhesive is dried or cured, or prior to any subsequent application of a different adhesive. It is not necessary for an application process to have an oven or flash-off area.
"Ceramic tile installation adhesive" means any adhesive intended by the manufacturer for use in the installation of ceramic tiles.
"Chlorinated polyvinyl chloride plastic" or "CPVC plastic welding" means a polymer of the vinyl chloride monomer that contains 67% chlorine and is normally identified with a CPVC marking.
"Chlorinated polyvinyl chloride welding" or "CPVC welding" means an adhesive labeled for welding of chlorinated polyvinyl chloride plastic.
"Cleaning activities" means activities other than surface preparation and priming that use cleaning materials to remove adhesive residue or other unwanted materials from equipment related to application operations, as well as the cleaning of spray guns, transfer lines (such as tubing or piping), tanks, and the interior of spray booths.
"Contact adhesive" means an adhesive that (i) is designed for application to both surfaces to be bonded together, (ii) is allowed to dry before the two surfaces are placed in contact with each other, (iii) forms an immediate bond that is impossible, or difficult, to reposition after both adhesive-coated surfaces are placed in contact with each other, and (iv) does not need sustained pressure or clamping of surfaces after the adhesive-coated surfaces have been brought together using sufficient momentary pressure to establish full contact between both surfaces. Contact adhesive does not include rubber cements that are primarily intended for use on paper substrates or vulcanizing fluids that are designed and labeled for tire repair only.
"Cove base" means a flooring trim unit, generally made of vinyl or rubber, having a concave radius on one edge and a convex radius on the opposite edge that is used in forming a junction between the bottom wall course and the floor or to form an inside corner.
"Cove base installation adhesive" means any adhesive intended by the manufacturer to be used for the installation of cove base or wall base on a wall or vertical surface at floor level.
"Cyanoacrylate adhesive" means any adhesive with a cyanoacrylate content of at least 95% by weight.
"Fiberglass boat manufacturing facility" means a facility that manufactures hulls or decks of boats from fiberglass or builds molds to make fiberglass boat hulls or decks and does not include a facility that solely manufactures parts of boats (such as hatches, seats, or lockers) or boat trailers, that is, which does not also manufacture hulls or decks of boats from fiberglass or builds molds to make fiberglass boat hulls or decks.
"Fiberglass boat manufacturing materials" means materials utilized at fiberglass boat manufacturing facilities to manufacture hulls or decks of boats from fiberglass, and parts of boats (such as hatches, seats, or lockers), or to build molds to make fiberglass boat hulls or decks.
"Flexible packaging printing materials" means materials used in the manufacture of any package or part of a package the shape of which can be readily changed. Flexible packaging includes, but is not limited to, bags, pouches, liners, and wraps utilizing paper, plastic, film, aluminum foil, metalized or coated paper or film, or any combination of these materials.
"Flexible vinyl" means nonrigid polyvinyl chloride plastic with a 5.0% by weight plasticizer content.
"Indoor floor covering installation adhesive" means any adhesive intended by the manufacturer for use in the installation of wood flooring, carpet, resilient tile, vinyl tile, vinyl backed carpet, resilient sheet and roll, or artificial grass. Adhesives used to install ceramic tile and perimeter bonded sheet flooring with vinyl backing onto a nonporous substrate, such as flexible vinyl, are excluded from this category.
"Industrial adhesives" means adhesives used for joining surfaces in assembly and construction of a large variety of products. Adhesives may be generally classified as solution/waterborne, solvent-borne, solventless or solid (such as hot melt adhesives), pressure sensitive, hot-melt, or reactive (such as epoxy adhesives and ultraviolet-curable adhesives). Adhesives may also be generally classified according to whether they are structural or nonstructural. Structural adhesives are commonly used in industrial assembly processes and are designed to maintain product structural integrity.
"Medical equipment manufacturing" means the manufacture of medical devices, such as, but not limited to, catheters, heart valves, blood cardioplegia machines, tracheostomy tubes, blood oxygenators, and cardiatory reservoirs.
"Metal to urethane/rubber molding or casting adhesive" means any adhesive intended by the manufacturer to bond metal to high density or elastomeric urethane or molded rubber materials, in heater molding or casting processes, to fabricate products such as rollers for computer printers or other paper handling equipment.
"Motor vehicle adhesive" means an adhesive, including glass bonding adhesive, used at a facility that is not an automobile or light-duty truck assembly coating facility, applied for the purpose of bonding two vehicle surfaces together without regard to the substrates involved.
"Motor vehicle glass bonding primer" means a primer, used at a facility that is not an automobile or light-duty truck assembly coating facility, applied to windshield or other glass, or to body openings, to prepare the glass or body opening for the application of glass bonding adhesives or the installation of adhesive bonded glass. Motor vehicle glass bonding primer includes glass bonding/cleaning primers that perform both functions (cleaning and priming of the windshield or other glass, or body openings) prior to the application of adhesive or the installation of adhesive bonded glass.
"Motor vehicle weatherstrip adhesive" means an adhesive, used at a facility that is not an automobile or light-duty truck assembly coating facility, applied to weatherstripping materials for the purpose of bonding the weatherstrip material to the surface of the vehicle.
"Multipurpose construction adhesive" means any adhesive intended by the manufacturer for use in the installation or repair of various construction materials, including but not limited to drywall, subfloor, panel, fiberglass reinforced plastic (FRP), ceiling tile, and acoustical tile.
"Outdoor floor covering installation adhesive" means any adhesive intended by the manufacturer for use in the installation of floor covering that is not in an enclosure and that is exposed to ambient weather conditions during normal use.
"Paper, film, and foil coating" means coating that is applied to paper, film, or foil surfaces in the manufacturing of several major product types for the following industry sectors: pressure sensitive tape and labels (including fabric coated for use in pressure sensitive tapes and labels); photographic film; industrial and decorative laminates; abrasive products (including fabric coated for use in abrasive products); and flexible packaging (including coating of nonwoven polymer substrates for use in flexible packaging). Paper and film coating also includes coatings applied during miscellaneous coating operations for several products including: corrugated and solid fiber boxes; die-cut paper paperboard, and cardboard; converted paper and paperboard not elsewhere classified; folding paperboard boxes, including sanitary boxes; manifold business forms and related products; plastic aseptic packaging; and carbon paper and inked ribbons.
"Perimeter bonded sheet flooring installation" means the installation of sheet flooring with vinyl backing onto a nonporous substrate using an adhesive designed to be applied only to a strip of up to four inches wide around the perimeter of the sheet flooring.
"Plastic" means a synthetic material chemically formed by the polymerization of organic (carbon-based) substances. Plastics are usually compounded with modifiers, extenders, and/or reinforcers and are capable of being molded, extruded, cast into various shapes and films or drawn into filaments.
"Plastic solvent welding adhesive" means any adhesive intended by the manufacturer for use to dissolve the surface of plastic to form a bond between mating surfaces.
"Plastic solvent welding adhesive primer" means any primer intended by the manufacturer for use to prepare plastic substrates prior to bonding or welding.
"Polyvinyl chloride plastic" or "PVC" means a polymer of the chlorinated vinyl monomer that contains 57% chlorine.
"Polyvinyl chloride welding adhesive" or "PVC welding adhesive" means any adhesive intended by the manufacturer for use in the welding of PVC plastic pipe.
"Porous material" means a substance that has tiny openings, often microscopic, in which fluids may be absorbed or discharged, including, but not limited to, paper and corrugated paperboard. For the purposes of this article, porous material does not include wood.
"Reactive adhesive" means adhesive systems composed, in part, of volatile monomers that react during the adhesive curing reaction, and, as a result, do not evolve from the film during use. These volatile components instead become integral parts of the adhesive through chemical reaction. At least 70% of the liquid components of the system, excluding water, react during the process.
"Reinforced plastic composite" means a composite material consisting of plastic reinforced with fibers.
"Rubber" means any natural or manufactured rubber substrate, including but not limited to, styrene-butadiene rubber, polychloroprene (neoprene), butyl rubber, nitrile rubber, chlorosulfonated polyethylene, and ethylene propylene diene terpolymer.
"Sheet rubber lining installation" means the process of applying sheet rubber liners by hand to metal or plastic substrates to protect the underlying substrate from corrosion or abrasion. These operations also include laminating sheet rubber to fabric by hand.
"Single-ply roof membrane" means a prefabricated single sheet of rubber, normally ethylene-propylenediene terpolymer, that is field-applied to a building roof using one layer of membrane material. For the purposes of this article, single-ply roof membrane does not include membranes prefabricated from ethylene-propylenediene monomer (EPDM).
"Single-ply roof membrane adhesive primer" means any primer labeled for use to clean and promote adhesion of the single-ply roof membrane seams or splices prior to bonding.
"Single-ply roof membrane installation and repair adhesive" means any adhesive labeled for use in the installation or repair of single-ply roof membrane. Installation includes, as a minimum, attaching the edge of the membrane to the edge of the roof and applying flashings to vents, pipes, and ducts that protrude through the membrane. Repair includes gluing the edges of torn membrane together, attaching a patch over a hole and reapplying flashings to vents, pipes, or ducts installed through the membrane.
"Structural glazing" means a process that includes the application of adhesive to bond glass, ceramic, metal, stone, or composite panels to exterior building frames.
"Thin metal laminating adhesive" means any adhesive intended by the manufacturer for use in bonding multiple layers of metal to metal or metal to plastic in the production of electronic or magnetic components in which the thickness of the bond line or lines is less than 0.25 mils.
"Tire repair" means a process that includes expanding a hole, tear, fissure, or blemish in a tire casing by grinding, gouging, or applying adhesive and filling the hole or crevice with rubber.
"Undersea-based weapons systems components" means the fabrication of parts, assembly of parts or completed units of any portion of a missile launching system used on undersea ships.
"VOC" means volatile organic compound.
"Waterproof resorcinol glue" means a two-part resorcinol-resin-based adhesive designed for applications where the bond line must be resistant to conditions of continuous immersion in fresh or salt water.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8680. Standard for volatile organic compounds.
A. No owner or other person shall perform miscellaneous industrial adhesive application processes in excess of the following limits.
1. Facilities opting to meet specific emissions limits in lieu of the control efficiency in subdivision 2 of this subsection shall meet the applicable emissions limits in Table 4-58A.
| TABLE 4-58A. VOC EMISSION LIMITS FOR GENERAL AND SPECIALTY ADHESIVE APPLICATION PROCESSES | |||
| General Adhesive Application Processes | VOC Emission Limit | ||
| grams per liter (g/l) | pounds per gallon (lb/gal) | ||
| Reinforced plastic composite | 200 | 1.7 | |
| Flexible vinyl | 250 | 2.1 | |
| Metal | 30 | 0.3 | |
| Porous material (except wood) | 120 | 1.0 | |
| Rubber | 250 | 2.1 | |
| Wood | 30 | 0.3 | |
| Other substrates | 250 | 2.1 | |
|
|
| ||
| Specialty Adhesive Application Processes | VOC Emission Limit | ||
| (g/l) | (lb/gal) | ||
| Ceramic tile installation adhesive | 130 | 1.1 | |
| Contact adhesive | 250 | 2.1 | |
| Cove base installation adhesive | 150 | 1.3 | |
| Indoor floor covering installation adhesive | 150 | 1.3 | |
| Outdoor floor covering installation adhesive | 250 | 2.1 | |
| Perimeter bonded sheet floor covering installation | 660 | 5.5 | |
| Metal to urethane/rubber molding or casting adhesive | 850 | 7.1 | |
| Motor vehicle adhesive | 250 | 2.1 | |
| Motor vehicle weatherstrip adhesive | 750 | 6.3 | |
| Multipurpose construction | 200 | 1.7 | |
| ABS welding adhesive | 400 | 3.3 | |
| Plastic solvent welding (except ABS) adhesive | 500 | 4.2 | |
| Sheet rubber lining installation | 850 | 7.1 | |
| Single-ply roof membrane installation and repair adhesive (except EPDM) | 250 | 2.1 | |
| Structural glazing | 100 | 0.8 | |
| Thin metal laminating adhesive | 780 | 6.5 | |
| Tire repair | 100 | 0.8 | |
| Waterproof resorcinol glue | 170 | 1.4 | |
|
|
| ||
| Adhesive Primer Application Processes | VOC Emission Limit | ||
| (g/l) | (lb/gal) | ||
| Motor vehicle glass bonding primer | 900 | 7.5 | |
| Plastic solvent welding adhesive primer | 650 | 5.4 | |
| Single-ply roof membrane adhesive primer | 250 | 2.1 | |
| Other adhesive primer | 250 | 2.1 | |
| For the purposes of this table, emission limits are mass of VOC per volume of adhesive or adhesive primer excluding water and exempt compounds, as applied. | |||
a. The VOC content limits in Table 4-58A for adhesives applied to particular substrates shall apply as follows:
(1) If an owner or other person uses an adhesive or sealant subject to a specific VOC content limit for such adhesive or sealant in Table 4-58A, such specific limit is applicable rather than an adhesive-to-substrate limit.
(2) If an adhesive is used to bond dissimilar substrates together, the applicable substrate category with the highest VOC content shall be the limit for such use.
b. The emission limits in Table 4-58A shall be met by averaging the VOC content of materials used on a single application process unit for each day (i.e., daily within-application process unit averaging). Cross-application process unit averaging (i.e., averaging across multiple application units) shall not be used to determine these emission limits.
c. VOC content shall be determined as follows:
(1) For adhesives that are not reactive adhesives, VOC content shall be determined using Reference Method 24.
(2) For reactive adhesives, VOC content shall be determined using the procedure for reactive adhesives in Appendix A of subpart PPPP of 40 CFR Part 63.
(3) As an alternative to the methods in subdivisions (1) and (2) of this subdivision A 1 c, the manufacturer's formulation data may be used. If there is a disagreement between manufacturer's formulation data and the results of a subsequent test, the test method results shall be used unless the facility can demonstrate to the board's satisfaction that the manufacturer's formulation data are correct.
2. Facilities opting to meet a control efficiency in lieu of the specific emission limits in subdivision 1 of this subsection shall meet an overall control efficiency of 85%.
3. The following materials shall not be subject to the limits and controls found in subdivisions 1 and 2 of this subsection but shall be subject to the work practices found in subdivision B 3 of this section:
a. Adhesives or adhesive primers being tested or evaluated in any research and development, quality assurance, or analytical laboratory.
b. Adhesives or adhesive primers used in the assembly, repair, or manufacture of aerospace or undersea-based weapon systems.
c. Adhesives or adhesive primers used in medical equipment manufacturing operations.
d. Cyanoacrylate adhesive application processes.
e. Application of aerosol adhesives and adhesive primers applied with a handheld, disposable can that is pressured and that dispenses an adhesive or adhesive primer by means of a propellant. Aerosol adhesives are regulated by VOC Emission Standards for Consumer Products, subpart C of 40 CFR Part 59. Aerosol adhesive primers are regulated as "primers" under VOC Emission Standards for Aerosol Coatings, subpart E of 40 CFR Part 59.
f. Processes using polyester bonding putties to assemble fiberglass parts at fiberglass boat manufacturing facilities and at other reinforced plastic composite manufacturing facilities.
g. Processes using adhesives and adhesive primers that are supplied by the manufacturer in containers with a net volume of 16 ounces or less, or a net weight of one pound or less.
h. Cleaning materials.
B. The owner of a facility subject to this article shall implement the following control options as applicable:
1. A facility using low-VOC adhesives or adhesive primers shall use one of the following application methods:
a. Electrostatic spray;
b. HVLP spray;
c. Flow coat;
d. Roll coat or hand application, including nonspray application methods similar to hand or mechanically powered caulking gun, brush, or direct hand application;
e. Dip coat, including electrodeposition;
f. Airless spray;
g. Air-assisted airless spray; or
h. Other adhesive application method capable of achieving a transfer efficiency equivalent to or better than that achieved by HVLP spraying.
2. A facility with product performance requirements or other needs that dictate the use of higher-VOC materials than those that would meet the emission limits in Table 4-58A shall either (i) use add-on control equipment with an overall control efficiency of 85% or (ii) use a combination of adhesives and add-on control equipment on an application process unit to meet the emission limits in Table 4-58A. Add-on devices may include oxidizers, adsorbers, absorbers, and concentrators.
3. The following work practices for the application of adhesives, adhesive primers, and process-related waste materials, shall be used:
a. All VOC-containing adhesives, adhesive primers, and process-related waste materials shall be stored in closed containers.
b. Mixing and storage containers used for VOC-containing adhesives, adhesive primers, and process-related waste materials shall be kept closed at all times except when these materials are being deposited or removed.
c. Spills of VOC-containing adhesives, adhesive primers, and process-related waste materials shall be minimized.
d. VOC-containing adhesives, adhesive primers, and process-related waste materials shall be conveyed from one location to another in closed containers or pipes.
4. The following work practices for cleaning activities shall be used:
a. All VOC-containing cleaning materials and used shop towels shall be stored in closed containers.
b. Storage containers used for VOC-containing cleaning materials shall be kept closed at all times except when these materials are deposited or removed.
c. Spills of VOC-containing cleaning materials shall be minimized.
d. VOC-containing cleaning materials shall be conveyed from one location to another in closed containers or pipes.
e. VOC emissions from cleaning of application, storage, mixing, and conveying equipment shall be minimized by performing equipment cleaning without atomizing the cleaning solvent and by capturing all spent solvent in closed containers.
5. The application of adhesives and adhesive primers applied with a handheld, disposable can that is pressured and that dispenses an adhesive or adhesive primer by means of a propellant shall not be subject to the application method limits and controls found in subdivisions 1, 2, and 4 of this subsection but shall be subject to the work practices found in subdivisions 3 and 4 of this subsection.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8690. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of Part II of 9VAC5-40 (Existing Stationary Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8700. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of Part II of 9VAC5-40 (Existing Stationary Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8710. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of Part II of 9VAC-40 (Existing Stationary Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8720. Standard for toxic pollutants.
The provisions of Article 4 (9VAC5-60-200 et seq.) of Part II of 9VAC5-60 (Hazardous Air Pollutant Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8730. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. The emission standards in 9VAC5-40-4330 apply to coating by coating or to the volume weighted average of coatings where the coatings are used on a single coating application system and the coatings are the same type or perform the same function. Such averaging shall not exceed 24 hours.
C. Compliance determinations for control technologies not based on compliant coatings (i.e., coating formulation alone) shall be based on the applicable standard in terms of pounds of VOCs per gallon solids or pounds of VOCs per gallon solids applied according to the applicable procedure in 9VAC5-20-121. Compliance may also be based on transfer efficiency greater than the baseline transfer efficiency of 9VAC5-40-8680 B if demonstrated by methods acceptable to the board according to the applicable procedure in 9VAC5-20-121.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8740. Compliance schedule.
The owner shall comply with the provisions of this article as expeditiously as possible but in no case later than February 1, 2017.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8750. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission testing) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8760. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8770. Notification, records, and reporting.
The provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8780. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8790. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8800. Permits.
A permit may be required prior to beginning any of the activities specified in this section if the provisions of 9VAC5-50 (New and Modified Stationary Sources) and 9VAC5-80 (Permits for Stationary Sources) apply. Owners contemplating such action should review those provisions and contact the appropriate regional office for guidance on whether those provisions apply.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (re-startup) of a facility.
6. Operation of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
Article 59
Emission Standards for Miscellaneous Metal Parts and Products Coating Application Systems in the Northern Virginia Volatile Organic Compound Emissions Control Area, 8-Hour Ozone Standard (Rule 4-59)
9VAC5-40-8810. Applicability and designation of affected facility.
Article 59
Emission Standards for Miscellaneous Metal Parts and Products Coating Application Systems in the Northern Virginia Volatile Organic Compound Emissions Control Area, 8-hour Ozone Standard (Rule 4-59)
A. Except as provided in subsections C through H of this section, the affected facility to which the provisions of this article apply is each miscellaneous metal product and plastic parts surface coating operation at a facility where the total actual emissions of volatile organic compounds (VOCs) from all miscellaneous metal product and plastic parts surface coating operations, including related cleaning activities, at that facility are equal to or exceed 6.8 kilograms per day (15 pounds per day), or an equivalent level of 2.7 tons per 12-month rolling period, before consideration of controls.
B. The provisions of this article apply only to affected facilities located in the Northern Virginia VOC Emissions Control Area designated in subdivision 1 a of 9VAC5-20-206.
C. Facilities that coat bodies or body parts for new heavier vehicles (including all vehicles that meet the definition of the term "other motor vehicles" as defined in 40 CFR 63.3176 of the National Emission Standards for Surface Coating of Automobile and Light-Duty Trucks) may, in lieu of complying with the provisions of this article, opt to comply with Article 28 (Emission Standards for Automobile and Light Duty Truck Coating Application Systems, 9VAC5-40-3860 et seq.) of 9VAC5-40 (Existing Stationary Sources).
D. The provisions of this article do not apply to the following:
1. Miscellaneous metal product and plastic parts surface coating operations subject to Article 26 (Emissions Standards for Large Appliance Coating Application Systems, 9VAC5-40-3560 et seq.), Article 27 (Emission Standards for Magnet Wire Coating Application Systems, 9VAC5-40-3710 et seq.), Article 29 (Emission Standards for Can Coating Application Systems, 9VAC5-40-4010 et seq.), Article 30 (Emission Standards for Metal Coil Coating Application Systems, 9VAC5-40-4160), Article 31 (Emission Standards for Paper and Fabric Coating Application Systems, 9VAC5-40-4310), Article 33 (Emissions Standards for Metal Furniture Coating Application Systems, 9VAC5-40-4610 et seq.), and Article 48 (Emission Standards for Mobile Equipment Repair and Refinishing Operations, 9VAC5-40-6970 et seq.) of 9VAC5-40 (Existing Stationary Sources); and Article 5 (Emission Standards for Architectural and Industrial Maintenance Coatings, 9VAC5-45-520 et seq.) of 9VAC5-45 (Consumer and Commercial Products).
2. Coating application systems used exclusively for determination of product quality and coatings that are applied to test panels and coupons as part of research and development, quality control, or performance testing activities at paint research or manufacturing facilities.
3. Coatings applied using a handheld, pressurized, nonrefillable container that expels coatings from the container in a finely divided spray when a valve on the container is depressed.
4. Miscellaneous metal product and plastic parts surface coating operations associated with the following product categories or processes: aerospace coatings; wood furniture coatings; fiberglass boat manufacturing materials; and paper, film, and foil coatings not otherwise regulated under Article 31 (Emission Standards for Paper and Fabric Coating Application Systems, 9VAC5-40-4310) of 9VAC5-40 (Existing Stationary Sources).
5. Recommended VOC limits and application methods do not apply to aerosol coating products or powder coatings.
E. For metal coatings:
1. Recommended work practices still apply; however, the VOC limits and application methods for provisions of this article do not apply to the following:
a. Stencil coatings;
b. Safety-indicating coatings;
c Solid-film lubricants;
d. Electric-insulating and thermal conducting coatings;
e. Magnetic data storage disk coatings; and
f. Plastic extruded onto metal parts to form a coating.
2. Recommended VOC limits and work practices still apply to these coatings and coating operations; however, the application methods for provisions of this article do not apply to the following:
a. Touch-up coatings;
b. Repair coatings; and
c. Textured finishes.
F. For plastic coatings:
1. Recommended application and work practices still apply to these coatings and coating operations; however, the VOC limits for provisions of this article do not apply to the following:
a. Touch-up and repair coatings;
b. Stencil coatings applied on clear or transparent substrates;
c. Clear or translucent coatings;
d. Coatings applied at a paint manufacturing facility while conducting performance tests on the coatings;
e. Any individual coating category used in volumes less than 50 gallons in any one year, if substitute complaint coatings are not available, provided that the total usage of all such coatings does not exceed 200 gallons per year, per facility;
f. Reflective coating applied to highway cones;
g. Mask coatings that are less than 0.5 millimeter thick (dried) and the area coated is less than 25 square inches;
h. EMI/RF shielding coatings; and
i. Heparin-benzalkonium chloride (HBAC)-contained coatings applied to medical devices, provided that the total usage of all such coatings does not exceed 100 gallons per year, per facility.
2. The application methods for provisions of this article do not apply to airbrush methods using five gallons or less per year of coating; however, VOC limits and work practices do apply.
G. For automotive/transportation and business machine plastic part coatings:
1. The VOC limits for provisions of this article do not apply to the following:
a. Texture coatings;
b. Vacuum metalizing coatings;
c. Gloss reducers;
d. Texture topcoats;
e. Adhesion primers;
f. Electrostatic preparation coatings;
g. Resist coatings; and
h. Stencil coatings.
2. Recommended application and work practices still apply to these coatings and coating operations.
H. For pleasure craft surface coating operations, VOC limits and work practices do apply to extreme high gloss coatings; however, recommended application methods do not apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8820. Definitions.
A. For the purpose of this article and subsequent amendments or any orders issued by the board, the words or terms shall have the meaning given them in subsection C of this section.
B. As used in this article, all terms not defined here shall have the meaning given them in 9VAC5-10 (General Definitions), unless otherwise required by context.
C. Terms defined.
"Aerospace coatings" means materials that are applied to the surface of an aerospace vehicle or component to form a decorative, protective, or functional solid film, or the solid film itself at a facility that produces, reworks, or repairs in any amount any commercial, civil, or military aerospace vehicle or component.
"Air-dried coating" means:
1. For general use, a coating that is cured at a temperature below 90°C (194°F).
2. For automotive/transportation and business machine use, a coating that is dried by the use of air or forced warm air at temperatures up to 90°C (194°F).
"Antifoulant coating" means any coating applied to the underwater portion of a pleasure craft to prevent or reduce the attachment of biological organisms, and registered with the U.S. Environmental Protection Agency (EPA) as a pesticide under the Federal Insecticide, Fungicide, and Rodenticide Act (7 USC § 136).
"Antifouling sealer/tie coat" means any coating applied over biocidal antifouling coating for the purpose of preventing release of biocides into the environment or to promote adhesion between an antifouling and a primer or other antifoulings.
"Baked coating" means a coating that is cured at a temperature at or above 90°C (194°F).
"Biocide" means a chemical substance or microorganism that can deter, render harmless, or exert a controlling effect on any harmful organism by chemical or biological means.
"Black automotive coating" means a coating that meets both of the following criteria: (i) maximum lightness of 23 units and (ii) saturation of less than 2.8, where saturation equals the square root of A² + B². These criteria are based on Cielab color space, 0/45 geometry. For spherical geometry, specular included, maximum lightness is 33 units.
"Business machine" means a device that uses electronic or mechanical methods to process information, perform calculations, print or copy information, or convert sound into electrical impulses for transmission, including devices listed in National American Industry Classification System (NAICS) codes 333318, 334111, 339940, 334112, 334118, 334210, 334418, 334519, 334613, and photocopying equipment in 333316.
"Camouflage coating" means a coating used, principally by the military, to conceal equipment from detection.
"Clear coating" means:
1. For general use, a colorless coating that contains binders, but no pigment, and is formulated to form a transparent film.
2. For automotive/transportation and business machine use, a coating that lacks color and opacity or is transparent and that uses the undercoat as a reflectant base or undertone color.
"Coating unit" means a series of one or more coating applicators and any associated drying area or oven wherein a coating is applied, dried, or cured. A coating unit ends at the point where the coating is dried or cured, or prior to any subsequent application of a different coating. It is not necessary for a coating unit to have an oven or flash-off area.
"Drum" means any cylindrical metal shipping container larger than 12 gallons capacity but no larger than 110 gallons capacity.
"Electric dissipating coating" means a coating that rapidly dissipates a high-voltage electric charge.
"Electric-insulating varnish" means a nonconvertible-type coating applied to electric motors, components of electric motors, or power transformers to provide electrical, mechanical, and environmental protection or resistance.
"EMF/RFI shielding" means a coating used on electrical or electronic equipment to provide shielding against electromagnetic interference, radio frequency interference, or static discharge.
"Etching filler" means a coating that contains less than 23% solids by weight and at least 0.5% acid by weight and is used instead of applying a pretreatment coating followed by a primer.
"Extreme high-gloss coating" means:
1. For general use, a coating that when tested by the American Society for Testing and Materials (ASTM) Standard Test Method for Specular Gloss (see 9VAC5-20-21) shows a reflectance of 75 or more on a 60° meter.
2. For pleasure craft surface coating, any coating that achieves at least 95% reflectance on a 60° meter when tested by ASTM Standard Test Method for Specular Gloss (see 9VAC5-20-21).
"Extreme performance coating" means a coating used on a metal or plastic surface where the coated surface is, in its intended use, subject to the following:
1. Chronic exposure to corrosive, caustic, or acidic agents, chemicals, chemical fumes, chemical mixtures, or solutions;
2. Repeated exposure to temperatures in excess of 250°F; or
3. Repeated heavy abrasion, including mechanical wear and repeated scrubbing with industrial grade solvents, cleansers, or scouring agents.
Extreme performance coatings include, but are not limited to, coatings applied to locomotives, railroad cars, farm machinery, and heavy duty trucks.
"Fiberglass boat manufacturing materials" means materials utilized at facilities that manufacture hulls or decks of boats from fiberglass or build molds to make fiberglass boat hulls or decks. Fiberglass boat manufacturing materials are not materials used at facilities that manufacture solely parts of boats (i.e., hatches, seats, or lockers) or boat trailers, but do not (i) manufacture hulls or decks of boats from fiberglass or (ii) build molds to make fiberglass boat hulls or decks.
"Finish primer/surfacer" means a coating applied with a wet film thickness of less than 10 mils prior to the application of a topcoat for purposes of providing corrosion resistance, adhesion of subsequent coatings, a moisture barrier, or promotion of a uniform surface necessary for filling in surface imperfections.
"Flexible coating" means any coating that is required to comply with engineering specifications for impact resistance, mandrel bend, or elongation as defined by the original equipment manufacturer.
"Fog coat" means a coating that is applied to a plastic part for the purpose of color matching without masking a molded-in texture. A fog coat shall not be applied at a thickness of more than 0.5 mils of coating solids.
"Heat-resistant coating" means a coating that must withstand a temperature of at least 400°F during normal use.
"High bake coating" means a coating that is designed to cure only at temperatures of more than 90°C (194°F).
"High build primer/surfacer" means a coating applied with a wet film thickness of 10 mils or more prior to the application of a topcoat for purposes of providing corrosion resistance, adhesion of subsequent coatings, or a moisture barrier, or promoting a uniform surface necessary for filling in surface imperfections.
"High gloss" means any coating that achieves at least 85% reflectance on a 60° meter when tested by ASTM Standard Test Method for Specular Gloss (see 9VAC5-20-21).
"High performance architectural coating" means a coating used to protect architectural subsections and that meets the requirements of the Architectural Aluminum Manufacturer Association's publication number AAMA 2604-05 (Voluntary Specification, Performance Requirements and Test Procedures for High Performance Organic Coatings on Aluminum Extrusions and Panels) or 2605-05 (Voluntary Specification, Performance Requirements and Test Procedures for Superior Performing Organic Coatings on Aluminum Extrusions and Panels).
"High temperature coating" means a coating that is certified to withstand a temperature of 1000°F for 24 hours.
"Metallic coating" means a coating that contains more than five grams of metal particles per liter of coating as applied. "Metal particles" are pieces of a pure elemental metal or a combination of elemental metals.
"Military specification coating" means a coating that has a formulation approved by a United States military agency for use on military equipment.
"Miscellaneous metal parts and products" means a varied range of metal and plastic parts and products that are constructed either entirely or partially from metal or plastic. These miscellaneous metal products and plastic parts include, but are not limited to, metal and plastic components of the following types of products as well as the products themselves: fabricated metal products, molded plastic parts, small and large farm machinery, commercial and industrial machinery and equipment, automotive or transportation equipment, interior or exterior automotive parts, construction equipment, motor vehicle accessories, bicycles and sporting goods, toys, recreational vehicles, pleasure craft (recreational boats), extruded aluminum structural components, railroad cars, heavier vehicles (as defined in 40 CFR 63.3176), lawn and garden equipment, business machines, laboratory and medical equipment, electronic equipment, steel drums, metal pipes, and numerous other industrial and household products.
"Miscellaneous metal product and plastic parts coating" means coatings that include paints, sealants, caulks, inks, and maskants (decorative, protective, or functional materials that consist only of protective oils for metal, acids, bases, or any combination of these substances are not considered miscellaneous metal or plastic part coatings). The paints include several categories of primers, topcoats, and specialty coatings, typically defined by the coating's function. The types of coating technologies used by miscellaneous metal product and plastic part surface coating facilities include higher solids, waterborne, and powder coatings, as well as conventional solvent-borne coatings. Decorative, protective, or functional materials that consist only of protective oils for metal, acids, bases, or any combination of these substances are not considered miscellaneous metal or plastic part coatings.
"Miscellaneous metal product and plastic parts surface coating operation" means the application of surface coatings by the manufacturer of miscellaneous metal and plastic parts to the parts it produces, and by facilities that perform surface coating of miscellaneous metal and plastic parts on a contract basis.
"Mold seal coating" means the initial coating applied to a new mold or a repaired mold to provide a smooth surface that, when coated with a mold release coating, prevents products from sticking to the mold.
"Motor vehicle bedliner" means a multi-component coating, used at a facility that is not an automobile or light-duty truck assembly coating facility, applied to a cargo bed after the application of topcoat to provide additional durability and chip resistance.
"Motor vehicle cavity wax" means a coating, used at a facility that is not an automobile or light-duty truck assembly coating facility, applied into the cavities of the vehicle primarily for the purpose of enhancing corrosion protection.
"Motor vehicle deadener" means a coating, used at a facility that is not an automobile or light-duty truck assembly coating facility, applied to selected vehicle surfaces primarily for the purpose of reducing the sound of road noise in the passenger compartment.
"Motor vehicle gasket/sealing material" means a fluid, used at a facility that is not an automobile or light-duty truck assembly coating facility, applied to coat a gasket or replace and perform the same function as a gasket. Automobile and light-duty truck gasket/gasket sealing material includes room temperature vulcanization (RTV) seal material.
"Motor vehicle lubricating wax/compound" means a protective lubricating material, used at a facility that is not an automobile or light-duty truck assembly coating facility, applied to vehicle hubs and hinges.
"Motor vehicle sealer" means a high viscosity material, used at a facility that is not an automobile or light-duty truck assembly coating facility, generally, but not always, applied in the paint shop after the body has received an electrodeposition primer coating and before the application of subsequent coatings (e.g., primer-surfacer). The primary purpose of automobile and light-duty truck sealer is to fill body joints completely so that there is no intrusion of water, gases or corrosive materials into the passenger area of the body compartment. Such materials are also referred to as sealant, sealant primer, or caulk.
"Motor vehicle trunk interior coating" means a coating, used at a facility that is not an automobile or light-duty truck assembly coating facility, applied to the trunk interior to provide chip protection.
"Motor vehicle underbody coating" means a coating, used at a facility that is not an automobile or light-duty truck assembly coating facility, applied to the undercarriage or firewall to prevent corrosion or provide chip protection.
"Multi-colored coating" means a coating that exhibits more than one color when applied, and which is packaged in a single container and applied in a single coat.
"Multi-component coating" means a coating requiring the addition of a separate reactive resin, commonly known as a catalyst or hardener, before application to form an acceptable dry film.
"One-component coating" means a coating that is ready for application as it comes out of its container to form an acceptable dry film. A thinner, necessary to reduce the viscosity, is not considered a component.
"Optical coating" means a coating applied to an optical lens.
"Pan-backing coating" means a coating applied to the surface of pots, pans, or other cooking implements that are exposed directly to a flame or other heating elements.
"Paper, film, and foil coating" means coating that is applied to paper, film, or foil surfaces in the manufacturing of several major product types for the following industry sectors: pressure sensitive tape and labels (including fabric coated for use in pressure sensitive tapes and labels); photographic film; industrial and decorative laminates; abrasive products (including fabric coated for use in abrasive products); and flexible packaging (including coating of nonwoven polymer substrates for use in flexible packaging). Paper and film coating also includes coatings applied during miscellaneous coating operations for several products including: corrugated and solid fiber boxes; die-cut paper paperboard, and cardboard; converted paper and paperboard not elsewhere classified; folding paperboard boxes, including sanitary boxes; manifold business forms and related products; plastic aseptic packaging; and carbon paper and inked ribbons.
"Pleasure craft" means vessels that are manufactured or operated primarily for recreational purposes, or leased, rented, or chartered to a person or business for recreational purposes. The owner of such vessels shall be responsible for certifying that the intended use is for recreational purposes.
"Pleasure craft coating" means any marine coating, except unsaturated polyester resin (fiberglass) coatings, applied by brush, spray, roller, or other means to a pleasure craft.
"Prefabricated architectural component coatings" means coatings applied to metal parts and products that are to be used as an architectural structure.
"Pretreatment coating" means a coating that contains no more than 12% solids by weight, and at least 0.5% acid, by weight, is used to provide surface etching, and is applied directly to metal surfaces to provide corrosion resistance, adhesion, and ease of stripping.
"Pretreatment wash primer" means a coating that contains no more than 12% solids, by weight, and at least 0.5% acids, by weight; is used to provide surface etching; and is applied directly to fiberglass and metal surfaces to provide corrosion resistance and adhesion of subsequent coatings.
"Red automotive coating" means a coating that meets all of the following criteria:
1. Yellow limit: the hue of hostaperm scarlet.
2. Blue limit: the hue of monastral red-violet.
3. Lightness limit for metallics: 35% aluminum flake.
4. Lightness limit for solids: 50% titanium dioxide white.
5. Solid reds: hue angle of -11 to 38 degrees and maximum lightness of 23 to 45 units.
6. Metallic reds: hue angle of -16 to 35 degrees and maximum lightness of 28 to 45 units.
These criteria are based on Cielab color space, 0/45 geometry. For spherical geometry, specular included, the upper limit is 49 units. The maximum lightness varies as the hue moves from violet to orange. This is a natural consequence of the strength of the colorants, and real colors show this effect.
"Repair coating" means a coating used to re-coat portions of a previously coated product that has sustained mechanical damage to the coating following normal coating operations.
"Shock-free coating" means a coating applied to electrical components to protect the user from electric shock. The coating has characteristics of being of low capacitance and high resistance, and having resistance to breaking down under high voltage.
"Silicone release coating" means any coating that contains silicone resin and is intended to prevent food from sticking to metal surfaces such as baking pans.
"Solar-absorbent coating" means a coating that has as its prime purpose the absorption of solar radiation.
"Texture coating" means a coating that is applied to a plastic part that, in its finished form, consists of discrete raised spots of the coating.
"Topcoat" means any final coating applied to the interior or exterior of a pleasure craft.
"Touchup coating" means a coating used to cover minor coating imperfections appearing after the main coating operation.
"Vacuum-metalizing coating" means:
1. For general use, the undercoat applied to the substrate on which the metal is deposited or the overcoat applied directly to the metal film. Vacuum metalizing/physical vapor deposition (PVD) is the process whereby metal is vaporized and deposited on a substrate in a vacuum chamber.
2. For automotive/transportation and business machine use, topcoats and basecoats that are used in the vacuum-metalizing process.
"VOC" means volatile organic compound.
"Wood furniture coatings" means protective, decorative, or functional films applied in thin layers to a surface used in the manufacture of wood furniture or wood furniture components. Such coatings include, but are not limited to, paints, topcoats, varnishes, sealers, stains, washcoats, basecoats, enamels, inks, and temporary protective coatings.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8830. Standard for volatile organic compounds.
A. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of the limits contained in Tables 4-59A through 4-59E. The VOC content limits are mass VOC per gallon of coating less water and exempt solvents and are based on low-VOC coatings. If more than one emission limitation in this subsection applies to a specific coating, then the least-stringent emission limitation shall be applied.
TABLE 4-59A. | ||||
Coating Category | Air-dried Coating | Baked Coating | ||
kg VOC/l coating | lb VOC/gal coating | kg VOC/l coating | lb VOC/gal coating | |
General one component | 0.34 | 2.8 | 0.28 | 2.3 |
General multi-component | 0.34 | 2.8 | 0.28 | 2.3 |
Camouflage | 0.42 | 3.5 | 0.42 | 3.5 |
Electric-insulating varnish | 0.42 | 3.5 | 0.42 | 3.5 |
Etching filler | 0.42 | 3.5 | 0.42 | 3.5 |
Extreme high-gloss | 0.42 | 3.5 | 0.36 | 3.0 |
Extreme performance | 0.42 | 3.5 | 0.36 | 3.0 |
Heat-resistant | 0.42 | 3.5 | 0.36 | 3.0 |
High performance architectural | 0.74 | 6.2 | 0.74 | 6.2 |
High temperature | 0.42 | 3.5 | 0.42 | 3.5 |
Metallic | 0.42 | 3.5 | 0.42 | 3.5 |
Military specification | 0.34 | 2.8 | 0.28 | 2.3 |
Mold seal | 0.42 | 3.5 | 0.42 | 3.5 |
Pan-backing | 0.42 | 3.5 | 0.42 | 3.5 |
Prefabricated architectural multi-component | 0.42 | 3.5 | 0.28 | 2.3 |
Prefabricated architectural one-component | 0.42 | 3.5 | 0.28 | 2.3 |
Pretreatment coatings | 0.42 | 3.5 | 0.42 | 3.5 |
Repair and touch-up | 0.42 | 3.5 | 0.36 | 3.0 |
Silicone release | 0.42 | 3.5 | 0.42 | 3.5 |
Solar-absorbent | 0.42 | 3.5 | 0.36 | 3.0 |
Vacuum-metalizing | 0.42 | 3.5 | 0.42 | 3.5 |
Drum coating, new, exterior | 0.34 | 2.8 | 0.34 | 2.8 |
Drum coating, new, interior | 0.42 | 3.5 | 0.42 | 3.5 |
Drum coating, reconditioned, exterior | 0.42 | 3.5 | 0.42 | 3.5 |
Drum coating, reconditioned, interior | 0.50 | 4.2 | 0.50 | 4.2 |
TABLE 4-59B. PLASTIC PARTS AND PRODUCTS VOC CONTENT LIMITS | ||
Coating Category | kg VOC/liter coating | lbs VOC/gal coating |
General one component | 0.28 | 2.3 |
General multi-component | 0.42 | 3.5 |
Electric dissipating and shock-free | 0.80 | 6.7 |
Extreme performance | 0.42 (2-pack coatings/multi-component) | 3.5 (2-pack coatings/multi-component) |
Metallic | 0.42 | 3.5 |
Military specification | 0.34 (1 pack/1 component) 0.42 (2 pack/multi-component) | 2.8 (1 pack/1 component) 3.5 (2 pack/multi-component) |
Mold seal | 0.76 | 6.3 |
Multi-colored | 0.68 | 5.7 |
Optical | 0.80 | 6.7 |
Vacuum-metalizing | 0.80 | 6.7 |
TABLE 4-59C. AUTOMOTIVE/TRANSPORTATION AND BUSINESS MACHINE PLASTIC PARTS VOC CONTENT LIMITS | ||
Coating Category | kg VOC/liter coating | lbs VOC/gal coating |
Automotive/Transportation Coatings (For red, yellow, and black automotive coatings, except touch up and repair coatings, the recommended limit is determined by multiplying the appropriate limit in this table by 1.15.) | ||
I. High Bake Coatings - Interior and Exterior Parts | ||
Flexible | 0.54 | 4.5 |
Nonflexible | 0.42 | 3.5 |
Base coating | 0.52 | 4.3 |
Clear coating | 0.48 | 4.0 |
Non-basecoat/clear coat | 0.52 | 4.3 |
II. Low Bake/Air-dried Coatings - Exterior Parts | ||
Primers | 0.58 | 4.8 |
Base coating | 0.60 | 5.0 |
Clear coating | 0.54 | 4.5 |
Non-basecoat/clear coat | 0.60 | 5.0 |
III. Low Bake/Air-dried Coatings - Interior Parts | 0.60 | 5.0 |
IV. Touchup and Repair Coatings | 0.62 | 5.2 |
Business Machine Coatings | ||
I. Primers | 0.35 | 2.9 |
II. Topcoat | 0.35 | 2.9 |
III. Texture Coat | 0.35 | 2.9 |
IV. Fog Coat | 0.26 | 2.2 |
V. Touchup and Repair | 0.35 | 2.9 |
TABLE 4-59D. PLEASURE CRAFT SURFACE COATING VOC CONTENT LIMITS | ||
Coating Category | kg VOC/liter coating | lbs VOC/gal coating |
Extreme high-gloss topcoat | 0.60 | 5.0 |
High gloss topcoat | 0.42 | 3.5 |
Pretreatment wash primers | 0.78 | 6.5 |
Finish primer/surfacer | 0.42 | 3.5 |
High build primer/surfacer | 0.34 | 2.8 |
Aluminum substrate antifoulant coating | 0.56 | 4.7 |
Antifouling sealer/tie coat | 0.42 | 3.5 |
Other substrate antifoulant coating | 0.33 | 2.8 |
All other pleasure craft surface coatings for metal or plastic | 0.42 | 3.5 |
TABLE 4-59E. MOTOR VEHICLE MATERIALS VOC CONTENT LIMITS | ||
Coating Category | kg VOC/liter coating | lbs VOC/gal coating |
Motor vehicle cavity wax | 0.65 | 5.4 |
Motor vehicle sealer | 0.65 | 5.4 |
Motor vehicle deadener | 0.65 | 5.4 |
Motor vehicle gasket/gasket sealing material | 0.20 | 1.7 |
Motor vehicle underbody coating | 0.65 | 5.4 |
Motor vehicle trunk interior coating | 0.65 | 5.4 |
Motor vehicle bedliner | 0.20 | 1.7 |
Motor vehicle lubricating wax/compound | 0.70 | 5.8 |
B. No owner or other person shall cause or permit the discharge into the atmosphere from a coating application system any volatile organic compound in excess of the limits contained in Tables 4-59F through 4-59I. The emission rate limits are based on low-VOC coatings and add-on controls on a VOC per volume solids basis. If more than one emission limitation in this subsection applies to a specific coating, then the least stringent emission limitation shall be applied.
TABLE 4-59F. | ||||
Coating Category | Air-dried | Baked | ||
kg VOC/l solids | lb VOC/gal solids | Kg VOC/l solids | lb VOC/gal solids | |
General one component | 0.54 | 4.52 | 0.40 | 3.35 |
General multi-component | 0.54 | 4.52 | 0.40 | 3.35 |
Camouflage | 0.80 | 6.67 | 0.80 | 6.67 |
Electric-insulating varnish | 0.80 | 6.67 | 0.80 | 6.67 |
Etching filler | 0.80 | 6.67 | 0.80 | 6.67 |
Extreme high-gloss | 0.80 | 6.67 | 0.61 | 5.06 |
Extreme performance | 0.80 | 6.67 | 0.61 | 5.06 |
Heat-resistant | 0.80 | 6.67 | 0.61 | 5.06 |
High performance architectural | 4.56 | 38.0 | 4.56 | 38.0 |
High temperature | 0.80 | 6.67 | 0.80 | 6.67 |
Metallic | 0.80 | 6.67 | 0.80 | 6.67 |
Military specification | 0.54 | 4.52 | 0.40 | 3.35 |
Mold-seal | 0.80 | 6.67 | 0.80 | 6.67 |
Pan-backing | 0.80 | 6.67 | 0.80 | 6.67 |
Prefabricated architectural multi-component | 0.80 | 6.67 | 0.40 | 3.35 |
Prefabricated architectural one-component | 0.80 | 6.67 | 0.40 | 3.35 |
Pretreatment coatings | 0.80 | 6.67 | 0.80 | 6.67 |
Silicone release 0.80 | 0.80 | 6.67 | 0.80 | 6.67 |
Solar-absorbent | 0.80 | 6.67 | 0.61 | 5.06 |
Vacuum-metalizing | 0.80 | 6.67 | 0.80 | 6.67 |
Drum coating, new, exterior | 0.54 | 4.52 | 0.54 | 4.52 |
Drum coating, new, interior | 0.80 | 6.67 | 0.80 | 6.67 |
Drum coating, reconditioned, exterior | 0.80 | 6.67 | 0.80 | 6.67 |
Drum coating, reconditioned, interior | 1.17 | 9.78 | 1.17 | 9.78 |
TABLE 4-59G. | ||
Coating Category | kg VOC/liter solids | lbs VOC/gal solids |
General one component | 0.40 | 3.35 |
General multi-component | 0.80 | 6.67 |
Electric dissipating coatings and shock-free | 8.96 | 74.7 |
Extreme performance | 0.80 (2-pack coatings/multi-component) | 6.67 (2-pack coatings/multi-component) |
Metallic | 0.80 | 6.67 |
Military specification | 0.54 (1 pack/1 component) 0.80 (2 pack/multi-component | 4.52 (1 pack/1 component) 6.67 (2 pack/multi-component) |
Mold seal | 5.24 | 43.7 |
Multi-colored | 3.04 | 25.3 |
Optical | 8.96 | 74.7 |
Vacuum-metalizing | 8.96 | 74.7 |
TABLE 4-59H. | ||
Coating Category | kg VOC/liter solids | lbs VOC/gal solids |
Automotive/Transportation Coatings (For red, yellow, and black automotive coatings, except touch up and repair coatings, the recommended limit is determined by multiplying the appropriate limit in this table by 1.15.) | ||
I. High Bake Coatings - Interior and Exterior Parts | ||
Flexible primer | 1.39 | 11.58 |
Nonflexible primer | 0.80 | 6.67 |
Base coats | 1.24 | 10.34 |
Clear coat | 1.05 | 8.76 |
Non-basecoat/clear coat | 1.24 | 10.34 |
II. Low Bake/Air-dried Coatings - Exterior Parts | ||
Primers | 1.66 | 13.80 |
Basecoat | 1.87 | 15.59 |
Clear coat | 1.39 | 11.58 |
Non-basecoat/clear coat | 1.87 | 15.59 |
III. Low Bake/Air-dried Coatings - Interior Parts | 1.87 | 15.59 |
IV. Touchup and Repair Coatings | 2.13 | 17.72 |
Business Machine Coatings | ||
I. Primers | 0.57 | 4.80 |
II. Topcoat | 0.57 | 4.80 |
III. Texture Coat | 0.57 | 4.80 |
IV. Fog Coat | 0.38 | 3.14 |
V. Touchup and Repair | 0.57 | 4.80 |
TABLE 4-59I. | ||
Coating Category | kg VOC/liter solids | lbs VOC/gal solids |
Extreme high-gloss topcoat | 1.88 | 15.6 |
High gloss topcoat | 0.80 | 6.7 |
Pretreatment wash primer | 6.67 | 55.6 |
Finish primer/surfacer | 0.80 | 6.7 |
High build primer surfacer | 0.55 | 4.6 |
Aluminum substrate antifoulant coating | 1.53 | 12.8 |
Antifouling sealer/tie coat | 0.8 | 6.7 |
Other substrate antifoulant coating | 0.53 | 4.4 |
All other pleasure craft surface coatings for metal or plastic | 0.80 | 6.7 |
C. Should product performance requirements or other needs dictate the use of higher-VOC materials than those that would meet the emission limits of subsections A and B of this section, an affected facility may opt to use add-on control equipment with an overall control efficiency of 90% in lieu of using low-VOC coatings and required application methods in subsection E of this section. Add-on devices include but are not limited to oxidizers, adsorbers, absorbers, and concentrators. Add-on devices coupled with capture systems to collect the VOC being released at the affected facilities shall achieve an overall control efficiency of no less than 90%.
D. In addition to the emissions limitations described in subsections A, B, and C of this section, the following work practices for storage, mixing operations, and handling operations for coatings, thinners, and coating-related waste materials shall be utilized:
1. All VOC-containing coatings, thinners, and coating-related waste materials shall be stored in closed containers.
2. Mixing and storage containers used for VOC-containing coatings, thinners, and coating-related waste materials shall be kept closed at all times except when depositing or removing these materials.
3. Spills of VOC-containing coatings, thinners, and coating-related waste materials shall be minimized.
4. VOC-containing coatings, thinners, and coating-related waste materials shall be conveyed from one location to another in closed containers or pipes.
E. In addition to the work practices described in subsection D of this section, the following work practices for cleaning materials, used to clean surfaces before coating (surface preparation) and to clean application equipment between coating jobs, shall be utilized:
1. All VOC-containing cleaning materials and used shop towels shall be stored in closed containers.
2. Storage containers used for VOC-containing cleaning materials shall be kept closed at all times except when depositing or removing these materials.
3. Spills of VOC-containing cleaning materials shall be minimized.
4. VOC-containing cleaning materials shall be conveyed from one location to another in closed containers or pipes.
5. VOC emissions from cleaning of application, storage, mixing, and conveying equipment shall be minimized by ensuring that equipment cleaning is performed without atomizing the cleaning solvent and all spent solvent is captured in closed containers.
F. One or more of the following application techniques shall be used to apply any finish material listed in Tables 4-59A through 4-59I:
1. Flow/curtain coating;
2. Dip coating;
3. Roller coating;
4. Brush coating;
5. Electrodeposition coating;
6. High volume low pressure (HVLP) spraying;
7. Electrostatic spray;
8. Airless spray;
9. Air-assisted airless spray; or
10. Other coating application methods that achieve emission reductions equivalent to or greater than those achieved by HVLP or electrostatic spray application methods.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8840. Standard for visible emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8850. Standard for fugitive dust/emissions.
The provisions of Article 1 (9VAC5-40-60 et seq.) of this chapter (Emission Standards for Visible Emissions and Fugitive Dust/Emissions, Rule 4-1) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8860. Standard for odor.
The provisions of Article 2 (9VAC5-40-130 et seq.) of this chapter (Emission Standards for Odor, Rule 4-2) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8870. Standard for toxic pollutants.
The provisions of Article 4 (9VAC5-60-200 et seq.) of 9VAC5-60 (Hazardous Air Pollutant Sources) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8880. Compliance.
A. The provisions of 9VAC5-40-20 (Compliance) apply.
B. Compliance may be demonstrated (i) on a mass VOC per gallon of coating less water and exempt solvents basis under 9VAC5-40-8830 A, (ii) on a mass VOC per volume of solids basis under 9VAC5-40-8830 B, or (iii) the overall control basis under 9VAC5-40-8830 C.
C. The emission standards in 9VAC5-40-8830 A and 9VAC5-40-8830 B apply coating by coating or to the volume weighted average of coatings where the coatings are used on a single coating application system and the coatings are the same type or perform the same function. Such averaging shall not exceed 24 hours.
D. Compliance determinations for control technologies not based on compliant coatings (i.e., coating formulation alone) shall be based on the applicable emission standards in 9VAC5-40-8830 B and the procedures of 9VAC5-20-121.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8890. Compliance schedule.
The owner shall comply with the provisions of this article as expeditiously as possible but in no case later than February 1, 2017.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8900. Test methods and procedures.
The provisions of 9VAC5-40-30 (Emission testing) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8910. Monitoring.
The provisions of 9VAC5-40-40 (Monitoring) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8920. Notification, records, and reporting.
The provisions of 9VAC5-40-50 (Notification, records and reporting) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8930. Registration.
The provisions of 9VAC5-20-160 (Registration) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8940. Facility and control equipment maintenance or malfunction.
The provisions of 9VAC5-20-180 (Facility and control equipment maintenance or malfunction) apply.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.
9VAC5-40-8950. Permits.
A permit may be required prior to beginning any of the activities specified in this section and the provisions of 9VAC5-50 (New and Modified Stationary Sources) and 9VAC5-80 (Permits for Stationary Sources) may apply. Owners contemplating such action should contact the appropriate regional office for guidance.
1. Construction of a facility.
2. Reconstruction (replacement of more than half) of a facility.
3. Modification (any physical change to equipment) of a facility.
4. Relocation of a facility.
5. Reactivation (re-startup) of a facility.
Statutory Authority
§ 10.1-1308 of the Code of Virginia; §§ 110, 111, 123, 129, 171, 172, and 182 of the federal Clean Air Act; 40 CFR Parts 51 and 60.
Historical Notes
Derived from Virginia Register Volume 32, Issue 7, eff. February 1, 2016.