Ala. Admin. Code r. 335-3-6-.37

Current through Register Vol. 42, No. 8, May 31, 2024

Section 335-3-6-.37 - Test Methods And Procedures

(1)Determination of Volatile Organic Compound Content of Surface Coatings.

(a) This method shall apply to ink, paint, varnish, lacquer, and other surface coatings.

(b) For the purposes of this method, a representative sample of the surface coating shall be obtained at the point of delivery to the coater or any other point in the process that the Director approves.

(c) The volatile organic compound content of the sample shall be determined using the test procedures found in 40 CFR 60 (except that references to Administrator are changed to Director) and one of the following methods:

1. Reference Method 24.

2. Reference Method 24A.

3. The Director may accept, instead of the coating analysis methods required under subparagraphs (c)1. and 2. of this paragraph, a certification by the coating manufacturer of the composition of the coating if supported by actual batch formulation records. Also, the manufacturer's certification shall be consistent with EPA's document number 450/3-84-019, titled "Procedures for Certifying Quantity of Volatile Organic Compounds Emitted by Paint, Ink, and Other Coatings."

(d) A person proposing to conduct a VOC emissions test shall notify the Director of the intent to test not less than thirty (30) days before the proposed initiation of the tests so the Director may at his option observe the test. The notification shall contain the information required by, and be in a format approved by, the Director.

(2)Test Procedure for Determination of VOC Emissions from Bulk Gasoline Terminals.

(a)Applicability. This method shall be applicable to determining VOC emission rates at tank truck and trailer gasoline loading terminals employing vapor collection systems and either continuous or intermittent vapor control systems. This method is applicable to motor tank truck and trailer loading only as per Rule 335-3-6-.29.

(b)Test Methods and Procedures. The Volatile Organic Compound emissions from Bulk Gasoline Terminals shall be determined by one of the following methods:

1. Test methods and procedures required in 40 CFR 60.503, Subpart XX.

2. Reference Method 25.

3. Reference Method 25A.

4. Reference Method 25B.

(c) A person proposing to conduct a VOC emissions test shall notify the Director of the intent to test not less than thirty (30) days before the proposed initiation of the tests so the Director may at his option observe the test. The notification shall contain the information required by, and be in a format approved by, the Director.

(3)Determination of Volatile Organic Compound Emission Control System Efficiency.

(a) The provisions of this Rule shall be applicable to any test method employed to determine the collection or control efficiency of any device or system designed, installed, and operated for the purpose of reducing volatile organic compound emissions.

(b) An efficiency demonstration shall include, but not be limited to, the following methods and procedures:

1. The volatile organic compound containing material shall be sampled and analyzed by EPA approved methods and procedures under Appendix A of 40 CFR 60 such that the emissions that could result from the use of the material can be quantified. For paints, inks, and other related coatings, the test methods and procedures shall be in accordance with paragraph (1) of this Rule.

2. The efficiency of any capture system used to capture and transport the volatile organic compound emissions from their point of origination to the control equipment shall be determined in accordance with the test methods and procedures in paragraph (13) of this Rule.

3. Samples of the volatile organic compound containing gas streams shall be taken simultaneously at the fugitives emission points from the permanent or temporary total enclosures, inlet and outlet of the emissions control device, and at least one centrally located point outside the permanent or temporary total enclosures and between the natural draft openings (background concentration).

4. The total combustible carbon content of the samples shall be determined by one of the following methods:

(i) Reference Method 25.

(ii) Reference Method 25A.

(iii) Reference Method 25B.

(iv) Reference Method 18.

5. the efficiency of the control device shall be expressed as the fraction of total combustible carbon content reduction achieved; and

6. the volatile organic compound mass emission rate shall be the sum of emissions from the control device, emissions not collected by the capture system, and capture system losses.

(c) A person proposing to conduct a VOC emission control system efficiency test shall notify the Director of the intent to test not less than thirty (30) days before the proposed initiation of the tests so the Director may at his option observe the test. The notification shall contain the information required by, and in a format approved by, the Director.

(d) The written results of any capture or control efficiency testing shall be submitted to the Director in an approved format within thirty (30) days after the date of the test. The written results shall also be retained at the location of the tested source for at least three (3) years after the date of the test.

(4)Determination of Solvent Metal Cleaning Volatile Organic Compound Emissions.

(a) This method shall be applicable to determining volatile organic compound emissions from solvent metal cleaning equipment.

(b) The purpose of this method is to quantify, by material balance, the amount of solvent input into a solvent metal cleaner over a sufficiently long period of time so that an average emission rate can be computed.

(c) The test methods and procedures shall be performed in accordance with those specified in EPA's control technique guideline document (EPA-450/2-77-.022) "Control of Volatile Organic Emissions from Solvent Metal Cleanings."

(5)Test Methods and Procedures for Perchloroethylene Dry Cleaning Systems.

(a) The provisions of this paragraph shall be applicable to any Perchloroethylene Dry Cleaning System.

(b) Test procedures to determine compliance with Rule 335-3-6-.40 shall be consistent with one of the following guideline methods:

1. EPA Guideline Series document, "Measurement of Volatile Organic Compounds," EPA-450/2-78-041;

2. Appendix B of "Control of Volatile Organic Emissions from Perchloroethylene Dry Cleaning Systems," EPA-450/2-78-050; or

3. American National Standards Institute paper, "Standard Method of Test for Dilution of Gasoline Engine Crankcase Oils."

(6)Test Methods and Procedures for Graphic Arts.

(a) The owner or operator of a VOC source shall, at his own expense, demonstrate compliance with Rule 335-3-6-.43 by the methods in subparagraph (c) of this paragraph. All tests shall be conducted by, or under the direction of, a person qualified by training and/or experience in the field of air pollution testing.

(b) A person proposing to conduct a VOC emissions test shall notify the Director of the intent to test not less than thirty (30) days before the proposed initiation of the tests so the Director may at his option observe the test. The notification shall contain the information required by, and be in a format approved by, the Director.

(c) Test procedures to determine compliance with Rule 335-3-6-.43 shall be consistent with one of the following methods and procedures:

1. EPA Guideline Series document, "Measurement of Volatile Organic Compounds," EPA-450/2-78-041;

2. Method 24A; or

3.40 CFR 60.433, "Performance Test and Compliance Provisions," except compliance shall be determined on a daily time period.

4. For add-on control equipment, the VOC mass emission rate shall be determined using the test procedures found in 40 CFR 60 (except that references to Administrator are changed to Director) and a method consistent with one of the following test methods:

(i) Reference Method 25.

(ii) Reference Method 25A.

(iii) Reference Method 25B.

(d) The Director may accept, instead of ink solvent analysis, a certification by the ink manufacturer of the composition of the ink solvent, if supported by actual batch formulation records. Also, the manufacturer's certification shall be consistent with EPA document 450/3-84-019, titled "Procedures for Certifying Quantity of VOC Emitted by Paint, Ink, and Other Coatings." Sufficient data to determine as-applied formulation must be provided if the as-applied formulation is different from the as-purchased ink.

(7)Test Methods and Procedures for Surface Coating of Miscellaneous Metal Parts and Products.

(a) The owner or operator of a VOC source required to comply with Rule 335-3-6-.32(11) shall, at his own expense, demonstrate compliance by the methods of subparagraph (c) of this paragraph. All tests shall be conducted by, or under the direction of, a person qualified by training and/or experience in the field of air pollution testing.

(c) Test procedures to determine compliance with Rule 335-3-6-.32(11) shall be consistent with one of the following methods and procedures:

1. EPA Guideline Series document, "Measurement of Volatile Organic Compounds," EPA-450/2-78-041;

2. Reference Method 24; or

3. Reference Method 24A.

(i) Reference Method 25.

(ii) Reference Method 25A.

(iii) Reference Method 25B.

(d) The Director may accept, instead of the coating analysis required in subparagraph (c)2. of this paragraph, a certification by the manufacturer of the composition of the coatings, if supported by actual batch formulation records. Also, the manufacturer's certification shall be consistent with EPA document 450/3-84-019, titled "Procedures for Certifying Quantity of VOC Emitted by Paint, Ink, and Other Coatings." Sufficient data to determine as-applied formulation must be provided if the as-applied formulation is different from the as-purchased coating.

(8)Test Methods and Procedures for Petroleum Liquid Storage in Floating Roof Tanks.

(a) The owner or operator of any VOC source required to comply with Rule 335-3-6-.44 shall, at his own expense, demonstrate compliance by the methods of this paragraph. All tests shall be conducted by, or under the direction of, a person qualified by training and/or experience in the field of air pollution testing.

(c) Compliance with Rule 335-3-6-.44 shall be determined by the methods and procedures in EPA Guideline Series document (EPA-450/2-78-047) "Control of Volatile Organic Emissions from Petroleum Liquid Storage in External Floating Roof Tanks."

(9)Reserved.

(10)Test Methods and Procedures for the Manufacture of Synthesized Pharmaceutical Products.

(a) The owner or operator of any VOC source required to comply with Rule 335-3-6-.39 shall, at his own expense, demonstrate compliance by the methods of subparagraph (c) of this paragraph or an alternative method approved by the Director. All tests shall be conducted, or under the direction of, a person qualified by training and/or experience in the field of air pollution testing.

(b) A person proposing to conduct a VOC emissions test shall notify the Director of the intent to test not less than thirty (30) days before the proposed initiation of the tests so the Director may, at his option, observe the test. The notification shall contain the information required by, and in a format approved by, the Director.

(c) Test procedures to determine compliance with Rule 335-3-6-.39 shall be consistent with EPA Guideline Series document, "Measurement of Volatile Organic Compounds," (EPA-450/2-78-041) and "Control of Volatile Organic Emissions from Manufacture of Synthesized Pharmaceutical Products" (EPA-450/2-78-029).

(d) If add-on control equipment is used, continuous monitors of the following parameters shall be installed, periodically calibrated, and operated at all times that the associated control equipment is operating:

1. exhaust gas temperature of all incinerators;

2. temperature rise across a catalytic incinerator bed;

3. breakthrough of VOC on a carbon adsorption unit; and

4. any other continuous monitoring or recording device required by the Director.

(11)Test Methods and Procedures for the Surface Coating of Flatwood Paneling.

(a) The owner or operator of a VOC source required to comply with Rule 335-3-6-.32(10) shall, at his own expense, demonstrate compliance by the methods of subparagraph (c) of this paragraph. All tests shall be conducted, or under the direction of, a person qualified by training and/or experience in the field of air pollution testing.

(b) A person proposing to conduct a VOC emissions test shall notify the Director of the intent to test not less than thirty (30) days before the proposed initiation of the tests so the Director may, at his option, observe the test. The notification shall contain the information required by, and be in a format approved by, the Director.

(c) Test procedures to determine compliance with Rule 335-3-6-.32(10) shall be consistent with one of the following methods and procedures:

1. EPA Guideline Series document, "Measurement of Volatile Organic Compounds," EPA-450/2-78-041 and "Control of Volatile Organic Emissions from Existing Stationary Sources, Vol. VII: Factory Surface Coating of Flat Wood Paneling," EPA-450/2-78-032;

2. Reference Method 24;

3. Reference Method 24A; or

(i) Reference Method 25.

(ii) Reference Method 25A.

(iii) Reference Method 25B.

(iv) Reference Method 18.

(d) The Director may accept, instead of the coating analysis required by subparagraph (c)2. of this paragraph, a certification by the coating manufacturer of the composition of the coating, if supported by actual batch formulation records. Also, the manufacturer's certification shall be consistent with EPA document 450/3-84-019, titled "Procedures for Certifying Quantity of VOC Emitted by Paint, Ink, and Other Coatings." Sufficient data to determine as-applied formulation must be provided if the as-applied formulation is different from the as-purchased coating.

(12)Test Methods and Procedures for Leaks from Gasoline Tank Trucks and Vapor Collection Systems.

(a) The owner or operator of a VOC source shall, at his own expense, demonstrate compliance with Rule 335-3-6-.41 by the methods of subparagraph (c) of this paragraph or an alternative method approved by the Director. All tests shall be made by, or under the direction of, a person qualified by training and/or experience in the field of air pollution testing.

(b) The owner or operator of a gasoline tank truck subject to Chapter 6 shall notify the Director in writing of the date and location of a certification test at least ten (10) days before the anticipated test date. In order to observe a certification test, the Director may postpone or reschedule the certification test date by written notice to the owner or operator within five (5) days after receipt of certification test notification.

(c) Test methods and procedures shall be consistent with one of the following methods and procedures:

1. Reference Method 27.

2. EPA Guideline Series document, "Control of Volatile Organic Compound Leaks from Gasoline Tank Trucks and Vapor Collection Systems," EPA-450/2-78-051.

(13)Capture Efficiency Test Procedures for Volatile Organic Compound Emissions Capture and Control Systems.

(a) For the purposes of this Rule, the following definitions and abbreviations apply:

1. "Capture" means the containment or recovery of emissions from a process for direction into a duct which may be exhausted through a stack or sent to a control device.

2. "Capture System" means all equipment (including, but not limited to, hoods, ducts, fans, booths, ovens, dryers, etc.) that contains, collects, and transports an air pollutant to a control device.

3. "Capture Efficiency" means the weight per unit time of VOC entering a capture system and delivered to a control device divided by the weight per unit time of total VOC generated by a source of VOC, expressed as a percentage.

4. "Control Device" means equipment (such as an incinerator or carbon adsorber) used to reduce, by destruction or removal, the amount of air pollutant(s) in an air stream prior to discharge to the ambient air.

5. "Control System" means a combination of one or more capture system(s) and control devices working in concert to reduce discharges of pollutants to the ambient air.

6. "Destruction or Removal Efficiency" means the efficiency, expressed as a decimal fraction, of a control device in destroying or removing contaminants calculated as one minus the amount of VOC exiting the control device divided by the amount of VOC entering the control device, e.g., [1 - (10 ppm/100 ppm)] = 0.9.

7. "Gas/Gas Method" means either of two methods for determining capture which rely only on gas phase measurements. One method requires construction of a temporary total enclosure (TTE) to assure all would be fugitive emissions are measured while the other uses the room or building which houses the emission source as an enclosure.

8. "Hood" means a device used to ventilate process equipment by capturing emissions of heat or air contaminants, e.g. organic vapors or other fumes, which are then conveyed through exhaust system ductwork to a more convenient discharge point or to air pollution control equipment.

9. "Liquid/Gas Method" means either of two methods for determining capture which require both gas phase and liquid phase measurements and analysis. One liquid/gas method requires construction of a temporary total enclosure, the other uses the building or room which houses the facility as a permanent total enclosure.

10. "Overall Emission Reduction Efficiency," means the weight per unit time of VOC removed by a control device divided by the weight per unit time of VOC emitted by an emission source, expressed as a percentage. The overall emission reduction efficiency is the product of the capture efficiency and the control equipment destruction or removal efficiency.

11. "Method 204D" is the EPA-approved test procedure to determine the fugitive volatile organic compound (VOC) emissions from temporary total enclosures (TTE). It is intended to be used as a segment in the development of liquid/gas or gas/gas protocols for determining VOC capture efficiency (CE) for surface coating and printing operations. Refer to Appendix F for Method 204D.

12. "Method 204E" is the EPA-approved test procedure to determine the fugitive volatile organic compound (VOC) emissions from a building enclosure (BE). It is intended to be used as a segment in the development of liquid/gas or gas/gas protocols for determining VOC capture efficiency (CE) for surface coating and printing operations. Refer to Appendix F for Method 204E.

13. "Method 204B" is the EPA-approved test procedure to determine the volatile organic compounds (VOC) content of captured gas streams. It is intended to be used as a segment in the development of liquid/gas or gas/gas protocols for determining VOC capture efficiency (CE) for surface coating and printing operations. The procedure may not be acceptable in certain site-specific situations, e.g., when (1) direct fired heaters or other circumstances affect the quantity of VOC at the control device inlet; and (2) particulate organic aerosols are formed in the process and are present in the captured emissions. Refer to Appendix F for Method 204B.

14. "Method 204C" is the EPA-approved test Method 204o determine the volatile organic compounds (VOC) content of captured gas streams. It is intended to be used as a segment in the development of gas/gas protocol in which fugitive VOC emissions are measured for determining VOC capture efficiency (CE) for surface coating and printing operations. A dilution system is used to reduce the VOC concentration of the captured emissions to about the same concentration as the fugitive emissions. The procedure may not be acceptable in certain site-specific situations, e.g., when (1) direct fired heaters or other circumstances affect the quantity of VOC at the control device inlet; and (2) particulate organic aerosols are formed in the process and are present in the captured emissions. Refer to Appendix F for Method 204C.

15. "Method 204A and 204F" are the EPA-approved test procedure to determine the input of volatile organic compounds (VOC) to a VOC emitting process. They are intended to be used as a segment in the development of liquid/gas protocols for determining VOC capture efficiency (CE) for surface coating and printing operations. Refer to Appendix F for Methods 204A and 204F.

16. "Method 204" is the EPA-approved procedure to determine whether a permanent or temporary enclosure meets the criteria of a total enclosure. Refer to Appendix F for Method 204.

17. "F" shall be an abbreviation for the mass of VOC leaving the process as gaseous fugitive emissions.

18. "G" shall be an abbreviation for the mass of VOC captured and delivered to a control device.

19. "L" shall be an abbreviation for the mass of VOC input to the process in liquid form.

20. "PTE" shall be an abbreviation for a permanent total enclosure, which contains a process that emits VOC and meets the specifications in Method 204.

21. "TTE" shall be an abbreviation for a temporary total enclosure which is built around a process that emits VOC and meets the specifications given in Method 204.

22. "BE" shall be an abbreviation for a building or room enclosure that contains a process that emits VOC. If a BE is to serve as a PTE or TTE, the appropriate requirements given in Method 204 shall be met.

(b)Applicability.

1. The requirements of subparagraph (3)(c) of this Rule shall apply to all regulated VOC emitting processes employing a control system except as provided below.

2. If a source installs a PTE that meets EPA specifications, and which directs all VOC to a control device, the capture efficiency is assumed to be 100 percent, and the source is exempted from the requirements described in subparagraph (3)(c) of this Rule. The EPA specifications to determine whether a structure is considered a PTE are given in Method 204. This does not exempt a source from performance of any control device efficiency testing required under these or any other regulations. In addition, a source shall demonstrate that all criteria for a PTE are met during the testing for control efficiency.

3. If a source uses a control device designed to collect and recover VOC (e.g. carbon adsorber), an explicit measurement of capture efficiency is not necessary if the conditions given below are met. The overall control of the system can be determined by directly comparing the input liquid (L) to the recovered liquid VOC. The general procedure for use in this situation is given in 40 CFR 60.433 with the following additional restrictions:

(i) The source shall be able to equate solvent usage with solvent recovery on a 24-hour (daily) basis, rather than a 30-day weighted average as given in 40 CFR 60.433. This shall be done within 72 hours following each 24-hour period. In addition, one of the following two criteria shall be met:

(ii) The solvent recovery system (i.e., capture and control system) shall be dedicated to a single process line (e.g., one process line venting to a carbon adsorber system), or

(iii) If the solvent recovery system controls multiple process lines, the source shall be able to demonstrate that the overall control (i.e., the total recovered solvent VOC divided by the sum of liquid VOC input to all process lines venting to the control system) meets or exceeds the most stringent standard applicable for any process line venting to the control system.

(c)Specific requirements.

1. The capture efficiency of a process line shall be measured using one of the four protocols given in subparagraph (c)3. of this paragraph.

2. Any error margin associated with a test protocol may not be incorporated into the results of a capture efficiency test.

3. The four specific capture efficiency protocols are discussed in subparagraphs (c)3.(i) through (c)3.(iv) of this paragraph below. Any affected source shall use one of these protocols to measure capture efficiency, unless a suitable alternative protocol is approved by EPA as a SIP revision.

(i)Gas/Gas Method using TTE. The EPA specifications to determine whether a temporary enclosure is considered a TTE are given in Method 204. The capture efficiency equation to be used for this Protocol is:

CE = Gw

(Gw + Fw)

where:

CE = capture efficiency, decimal fraction.

Gw = mass of VOC captured and delivered to the control device using a TTE. Method 204C is used to obtain Gw.

Fw = mass of fugitive VOC that escapes from a TTE. Method 204D is used to obtain Fw.

(ii)Liquid/Gas Method using TTE. The EPA specifications to determine whether a temporary enclosure is considered a TTE are given in Method 204. The capture efficiency equation to be used for this Protocol is:

CE = (L - F)

where:

CE = capture efficiency, decimal fraction.

L = mass of liquid VOC input to the process. Methods 204A or F are used to obtain L.

F = mass of fugitive VOC that escapes from a TTE. Method 204D is used to obtain F.

(iii)Gas/Gas Method using the building or room (BE) in which the affected source is located as the enclosure and in which G and F are measured while operating only the affected facility. All fans and blowers in the building or room shall be operated as they would under normal production. The capture efficiency equation to be used for this Protocol is:

CE = G

(G + Fb)

where:

CE = capture efficiency, decimal fraction.

G = mass of VOC captured and delivered to a control device. Method 204C is used to obtain G.

Fb = mass of fugitive VOC that escapes from the building enclosure. Method 204E is used to obtain Fb.

(iv)Liquid/Gas Method using the building or room (BE) in which the affected source is located as the enclosure and in which L and F are measured while operating only the affected facility. All fans and blowers in the building or room shall be operated as they would under normal production. The capture efficiency equation to be used for this protocol is:

CE = (L - Fb)

where:

CE = capture efficiency, decimal fraction.

L = mass of liquid VOC input to the process. Methods 204A or 204F are used to obtain L.

Fb = mass of fugitive VOC that escapes from building enclosure. Method 204E is used to obtain Fb.

(d)Recordkeeping and Reporting.

1. The owner or operator of all affected facilities shall maintain a copy of the capture efficiency protocol submitted to the Director on file. All results of appropriate test methods and CE procedures shall be reported to the Director within thirty (30) days of the test date. These records shall be retained by the owner or operator for a minimum of three (3) years after the test date.

2. Prior to making any changes to the capture or control equipment of an affected source, the owner or operator of the source shall notify the Director in writing of these changes in accordance with the permitting requirements under Rule 335-3-14-.01.

3. The owner or operator of an affected source shall notify the Director thirty (30) days prior to performing any capture efficiency test and/or control efficiency tests.

(4) An affected source utilizing a PTE shall demonstrate that this enclosure meets the requirement given in Method 204 for a PTE during any testing of a control system.

(5) An affected source utilizing a TTE shall demonstrate that its TTE meets the requirements given in Method 204 for a TTE during the test of their control system. The source shall also provide documentation that the quality assurance criteria for a TTE have been achieved.

Author:

Ala. Admin. Code r. 335-3-6-.37

Effective Date: June 9, 1987. Amended: Effective Date: September 21, 1989; July 31, 1991; October 24, 1991. Amended: Filed October 17, 1996; effective November 21, 1996.

Statutory Authority:Code of Ala. 1975, §§ 22-28-14, 22-22A-5, 22-22A-6, 22-22A-8.