Regulatory Text: 
Oklahoma Administrative Code.  Title 252.  Department of Environmental Quality 

Chapter 100.  Air Pollution Control (OAC 252:100)

SUBCHAPTER 39.  EMISSION OF ORGANIC MATERIALS IN NONATTAINMENT AREAS

PART 7.  SPECIFIC OPERATIONS
As adopted in the Oklahoma Register June 1, 1999 (16 Ok Reg 1774) effective June 11, 1999.
Approved by EPA December 29, 2008 (73 FR 79400) effective February 27, 2009 (OKd06).


Sections:
252:100-39-40.  Cutback asphalt (paving), OKd06
252:100-39-41.  Storage, loading and transport/delivery of VOCs, OKd06
252:100-39-42.  Metal cleaning, OKd06
252:100-39-43.  Graphic arts systems, OKd06
252:100-39-44.  Manufacture of pneumatic rubber tires, OKd06
252:100-39-45.  Petroleum (solvent) dry cleaning, OKd06
252:100-39-46.  Coating of parts and products, OKd06
252:100-39-47.  Control of VOC emissions from aerospace industries coatings operations, OKd06
252:100-39-49.  Manufacturing of fiberglass reinforced plastic products, OKd06


252:100-39-40.  Cutback asphalt (paving)

     (a)  Definitions.  "Cutback asphalt" means a basic asphalt or asphaltic concrete containing a petroleum distillate.

     (b)  Requirements.  No owner, operator and/or contractor shall prepare or apply cutback liquefied asphalt without the prior written consent of the Division Director.  Such consent may be granted during Oklahoma's non-oxidant season, i.e., November 1 through March 31.


252:100-39-41.  Storage, loading and transport/delivery of VOCs

     (a)  Storage of VOCs in vessels with storage capacities greater than 40,000 gallons.  Each vessel with a capacity greater than 40,000 gal (151 m³) which stores gasoline or any VOC shall be a pressure vessel capable of maintaining working pressures that prevent the loss of VOC vapor or gas to the atmosphere or shall be equipped with one or more of the following vapor control devices.
          (1)  An external floating roof, that consists of a pontoon-type or double-deck type cover or a fixed roof with an internal-floating cover.  The cover shall rest on the surface of the liquid contents at all times (i.e. off the leg supports), except during initial fill, when the storage vessel is completely empty, or during refilling.  When the cover is resting on the leg supports, the process of filling, emptying, or refilling shall be continuous and shall be accomplished as rapidly as possible.  The floating roof shall be equipped with a closure seal, or seals, to close the space between the cover edge and vessel wall.  Floating roofs are not appropriate control devices if the VOCs have a vapor pressure of 11.1 psia (76.6 kPa) or greater under actual conditions.  All gauging and sampling devices shall be gas-tight except when gauging or sampling is taking place.  Closure seals for fixed roof vessels with an internal-floating cover shall meet the requirements of 252:100-39-30(c)(1)(B)(i) and (ii).  Closure seals for vessels with external floating roofs shall meet the requirements of 252:100-39-30(c)(1)(B)(i), (ii), and (iii).
          (2)  A vapor-recovery system that consists of a vapor-gathering system capable of collecting 90 percent by weight or more of the uncontrolled VOCs that would otherwise be emitted to the atmosphere and a vapor-disposal system capable of processing VOCs to prevent emissions in excess of 6.68 x 10^-4 lb/gal (80 mg/l) of VOCs transferred.  All vessel gauging and sampling devices shall be gas-tight except when gauging or sampling is taking place.
          (3)  Other equipment or methods that are of equal efficiency for purposes of air pollution control may be used when approved by the Division Director and in concert with federal guidelines.

     (b)  Storage of VOCs in vessels with storage capacities of 400-40,000 gallons.
          (1)  Each gasoline or other VOC storage vessel with a nominal capacity greater than 400 gal (1.5 m³) and less than 40,000 gal (151 m³) shall be equipped with a submerged fill pipe or be bottom filled.
          (2)  The displaced vapors from each storage vessel with an average daily throughput of 30,000 gal (113,562 l) or greater which stores gasoline or other VOCs shall be processed by a system that has a total collection efficiency no less than 90 percent by weight of total VOCs in the vapors.
               (A)  The vapor recovery system shall include:
                    (i)  a vapor-tight return line from the storage vessel to the delivery vessel and a system that will ensure that the vapor return line is connected before gasoline or VOCs can be transferred into the storage vessel; or,
                    (ii)  other equipment that has a total collection efficiency no less than 90 percent by weight of the total VOCs in the displaced vapor if approval is obtained from the Division Director prior to start of construction.
               (B)  The requirements for vapor collection of displaced vapors shall not apply to operations that are not major sources.

     (c)  Loading of VOCs.
          (1)  Each VOC loading facility with an annual throughput of 120,000 gal (454,249 l) or greater or storage capacity greater than 10,000 gal (38 m³) shall be equipped with a vapor-collection and/or disposal system.
          (2)  While VOCs are loaded through the hatches of a transport vessel, a pneumatic, hydraulic or mechanical means shall be provided to ensure a vapor-tight seal at the hatch.
          (3)  A means shall be provided to prevent VOC drainage from the loading device when it is removed from the transport vessel, or to accomplish complete drainage before removal.
          (4)  When loading is by means other than hatches, all loading and vapor lines shall be equipped with fittings that make vapor-tight connections and which close automatically when disconnected.
          (5)  The vapor collection and/or disposal portion of the system shall consist of one or more of the elements listed in 252:100-39-41(c)(5)(A) through 252:100-39-42(c)(5)(C) in addition to bottom loading or submerged fill of transport vessels.  Storage vessels at service stations and bulk plants may be used for intermediate storage prior to recovery/disposal of vapors as specified in 252:100-39-41(c)(5)(A) through 252:100-39-41(c)(5)(C) if they are designed to prevent the release of vapors during use.
               (A)  An absorption/adsorption system or condensation system that has a minimum recovery efficiency of 90 percent by weight of all the VOC vapors and gases entering such disposal system.
               (B)  A vapor handling system which directs all vapors to a fuel gas incineration system with a minimum disposal efficiency of 95 percent.
               (C)  Other equipment that has at least a 90 percent efficiency, provided plans for such equipment are approved by the Division Director.
          (6)  Subsection 252:100-39-41(c) shall apply to any facility that loads VOCs into any transport vessel designed for transporting VOCs.

     (d)  Transport/delivery.
          (1)  The vapor-laden delivery vessel shall meet one of the following requirements.
               (A)  The delivery vessel must be designated and operated to be vapor tight except when sampling, gauging, or inspecting.
               (B)  The delivery vessel must be equipped and operated to deliver the VOC vapors to a vapor recovery/disposal system.
          (2)  No owner or operator shall allow a delivery vessel to be filled at a facility unable to receive displaced VOC vapors nor service vessels unable to deliver displaced vapors except for vessels and facilities exempted in 252:100-39-41(b) and 252:100-39-41(c).
          (3)  Testing of the tank trucks for compliance with the vapor tightness requirements must be consistent with Appendix "B" EPA Guideline Series Document, "Control of Volatile Organic Compound Leaks from Gasoline Tank Trucks and Vapor Collection Systems," EPA 450/2-78-051, or an equivalent method as determined by the Division Director.

     (e)  Additional requirements for Tulsa County.
          (1)  Applicability.  This subsection applies only in Tulsa County.
          (2)  Storage of VOCs.
               (A)  2,000 - 40,000 gallons capacity.  Each storage vessel with a nominal capacity greater than 2,000 gal (7.6 m³) and less than 40,000 gal (151 m³) that stores gasoline or other VOCs or each storage vessel located at a facility that dispenses more than 120,000 gal/yr of gasoline or other VOCs, in addition to being equipped with a submerged fill pipe or being bottom loading, shall be equipped with a vapor control system.  The vapor control system shall have an efficiency of no less than 90 percent by weight of the VOCs contained in the displaced vapors and shall be equipped with a pressure relief valve in the atmospheric vent system which maintains a pressure of 16 oz/in.² and l/2 oz/in.² vacuum.  The vapor recovery system shall include one or more of the following.
                    (i)  A vapor-tight return line from the storage vessel to the delivery vessel and a system that will ensure that the vapor return line is connected before gasoline or VOCs can be transferred into the storage vessel (i.e., poppeted connectors from the storage vessel to the delivery vessel.).
                    (ii)  A float vent valve assembly installed in the vapor return/vent line on new and existing dual point installations; however, for coaxial installations on existing stations, a vent sleeve extending 6 in. (15 cm) below the top of the vessel will be allowed.  Sleeves may be equipped with a 1/16 in. (0.16 cm) air bleed hole.
                    (iii)  A vapor recovery line with a cross-sectional area that is at least half of the cross-sectional area of the liquid delivery line.
                    (iv)  Other equipment that has a total collection efficiency no less than 90 percent by weight of the total VOCs in the displaced vapor if approved by Division Director prior to start of construction.
               (B)  Applicability.
                    (i)  Any vessel with a capacity greater than 2,000 gal (7.6 m³) or any vessel located at a facility that dispenses more than 120,000 gal/yr (454,249 l/yr) shall be and will always remain subject to 252:100-39-41(e)(2). (effective February 12, 1990)
                    (ii)  Exemptions to 252:100-39-41(e)(2) may be granted if the owner or operator shows to the satisfaction of the Division Director that the vessel is used exclusively for agricultural purposes.
               (C)  Emission testing.  If emission testing is conducted, the appropriate test methods selected from EPA Methods 1 through 4, 18, 21, 25, 25A and 25B shall be utilized.
               (D)  Compliance.  Compliance with 252:100-39-41(e)(2) shall be accomplished by the owner or operator of affected facilities by December 31, 1986.
               (E)  Certification.  The owner or operator of a facility shall obtain, by whatever means practicable, certification from the owner or operator of the transport/delivery vessels that all deliveries of gasoline or other VOCs made to their 400-gallon to 40,000-gallon storage facility located in Tulsa County shall be made by transport/delivery vessels that comply with the requirements contained in 252:100-39-41(e)(4).  Compliance with 252:100-39-41(e)(2) shall be accomplished by owners or operators of affected facilities no later than December 31, 1990. (Effective February 12, 1990)
          (3)  Loading of VOCs.  In addition to those requirements contained in 252:100-39-41(c), stationary loading facilities shall be checked annually in accordance with EPA Test Method 21, Leak Test.  Leaks greater than 5,000 ppmv shall be repaired within 15 days.  Facilities shall retain inspection and repair records for at least two years.
          (4)  Transport/delivery vessel requirements.  In addition to the requirements contained in 252:100-39-41(d), facilities located in Tulsa County must meet the following requirements.
               (A)  Maintenance.
                    (i)  The delivery vessel must be maintained so that it is vapor tight except when sampling, gauging, or inspecting.  These activities shall not occur while the vehicle is loading or unloading or is in a pressurized state.
                    (ii)  The delivery vessel must be equipped, maintained, and operated to receive vapors from sources identified in 252:100-39-41(b)(1) and 252:100-39-41(b)(2) and retain these and all other vapors until they are delivered into an authorized vapor recovery/disposal system.
                    (iii)  Vessels with defective equipment such as boots, seals, and hoses, or with other deficiencies that would impair the vessels' ability to retain vapors or liquid shall be repaired within 5 days.
                    (iv)  The certified testing facility must certify to the approving agency that the proper testing and repairs have occurred in accordance with 252:100-39-41(e)(4)(B)(i).  The vessel must also display on the rear panel a tag showing the date of the pressure test.
                    (v)  No owner or operator shall allow a delivery vessel to be filled at a facility unable to receive displaced VOCs nor service vessels unable to deliver displaced vapors except for vessels/facilities exempted in 252:100-39-41(b).  Terminal owners shall not fill vessels that do not display a current tag.
                    (vi)  Delivery vessels may be inspected by representatives of the DEQ in order to determine their state of repair.  Such a test may consist of a visual inspection or a vapor test with vapors not to exceed 5,000 ppmv.  Failure of a vapor test shall require the owner or operator to make the necessary repairs within 10 days.  Failure to certify within 10 days of a vapor test that the necessary repairs have been made shall subject the owner or operator to sanctions.  Upon certification of repairs, the vessel will be allowed to resume normal operation.
               (B)  Testing requirements.
                    (i)  Pressure test.
                         (I)  Delivery vessels, delivering or receiving gasoline must be tested one time per year for vapor tightness.  The vapor tightness test must be consistent with Appendix "A" EPA Guideline Series Document, "Control of Volatile Organic Compound Leaks from Gasoline Tank Trucks and Vapor Collection Systems", EPA 450/2-78-051.  Tests shall be performed by the owner or a transport service company.  Test methods used to test these vessels by owners or testing companies must be approved for use by the Division Director.
                         (II)  The vessel shall be considered to pass the test prescribed in 252:100-39-41(e)(4)(B)(i)(I) when the test results show that the vessel and its vapor collection systems do not sustain a pressure change of more than 3 in. H₂0.  There shall be no avoidable visible liquid leaks.
                    (ii)  Vapor test.  Testing of the tank trucks for compliance with vapor tightness requirements as required under 252:100-39-41(e)(4)(A)(vi) must be consistent with Appendix "B" EPA Guideline Series Document, "Control of Volatile Organic Compound Leaks from Gasoline Tank Trucks and Vapor Collection Systems", EPA 405/2-78-051, as modified for this purpose and contained in 252:100-43-15.  The requirements of 252:100-39-41(e) took effect December 15, 1988.


252:100-39-42.  Metal cleaning

     (a)  Cold cleaning facility.
          (1)  Equipment requirements.  An owner or operator of any cold cleaning unit for metal degreasing which uses a VOC shall:
               (A)  install a cover or door on the facility that can be easily operated with one hand;
               (B)  provide an internal drain board that will allow lid closure if practical; if not practical, provide an external drainage facility; and,
               (C)  attach a permanent, conspicuous label summarizing the operating requirements specified in 252:100-39-42(a)(2) to the facility.
          (2)  Operating requirements.  Owners or operators shall at a minimum:
               (A)  drain clean parts at least 15 seconds or until dripping ceases before removal;
               (B)  close degreaser cover when not handling parts in cleaner;
               (C)  store waste VOC in covered containers;
               (D)  not dispose or allow disposition of waste VOC in such a manner that more than 20 percent by weight can evaporate into the atmosphere.
               (E)  use a solid fluid stream, not an atomized spray, when VOC is sprayed.
          (3)  Requirements for controls.  If the vapor pressure of the VOC is greater than 0.6 psi (4.1 kPa) measured at 100 degrees F (38 degrees C) or if VOC is heated to 248 degrees F (120 degrees C), the owner or operator shall apply one or more of the following control devices/techniques.
               (A)  Freeboard that gives a freeboard ratio greater than or equal to 0.7.
               (B)  Water cover where the VOC is insoluble in and denser than water or such equivalent.
               (C)  Another system of equivalent control as approved by the Division Director.
          (4)  Compliance and recordkeeping.  Compliance shall be determined in accordance with EPA guidance document "Control of Volatile Organic Emissions from Solvent Metal Cleaning," 450/2-77-022.  Test reports and maintenance and repair records of control equipment shall be maintained by the source for at least two years.

     (b)  Vapor-type metal degreasing.
          (1)  Equipment requirements.  An owner or operator of any vapor-type metal degreasing unit using a VOC shall ensure that the following requirements are met.
               (A)  The unit shall have a cover or door that can easily be opened and closed without disturbing the vapor zone.
               (B)  The unit shall have the following safety switches.
                    (i)  Condenser flow switch and thermostat or equivalent capable of shutting off the sump heat if condenser coolant is not circulating or coolant exceeds VOC manufacturer's recommended level.
                    (ii)  Spray safety switch capable of shutting off spray pumps if the vapor level drops in excess of 4 in. (10 cm).
               (C)  The unit shall have one or more of the following control devices/techniques.
                    (i)  Freeboard ratio not less than 0.75, i.e., the ratio of the freeboard to the width of the degreaser wherein the term freeboard is defined as the distance from the top of the vapor zone to the top of the degreaser tank.
                    (ii)  Refrigerated chiller, i.e., condenser coils in the upper limit of the vapor zone.
                    (iii)  Enclosed design, i.e., cover or door is opened only when a part is actually entering or exiting the facility.
                    (iv)  A carbon adsorption system with ventilation greater than 50 cfm/ft² of air/vapor area when cover is open.  The system shall exhaust less than 25 ppmv VOC average over one adsorption cycle.
                    (v)  A control system demonstrated to have a control efficiency equal to or greater than any of the systems in 252:100-39-42(b)(1)(C).
               (D)  A permanent conspicuous label summarizing operating requirements in 252:100-39-42(b)(2) shall be attached to the unit.
          (2)  Operating requirements.  An owner or operator of a vapor type metal degreasing unit using VOC shall ensure that the following requirements are met.
               (A)  As a minimum operators shall:
                    (i)  keep the cover closed at all times except when degreasing parts;
                    (ii)  rack parts to allow full drainage;
                    (iii)  move parts in and out of the degreaser at less than 11 ft/min (3.4 m/min);
                    (iv)  degrease the workload in the vapor zone at least 30 seconds or until condensation ceases;
                    (v)  tip out any pools of VOC on the cleaned parts before removal;
                    (vi)  allow parts to dry within the degreaser for at least 15 seconds or until visually dry;
                    (vii)  assure that VOC leaks are immediately repaired or the degreaser is shut down; and,
                    (viii)  store waste VOC only in closed containers.
               (B)  As a minimum operators shall not:
                    (i)  degrease porous or absorbent materials, such as cloth, leather, wood or rope;
                    (ii)  allow workloads to occupy more than half of the degreaser's open top area;
                    (iii)  spray above the vapor level;
                    (iv)  allow greater than 20 percent of the VOC waste (by weight) to evaporate into the atmosphere when disposing of the waste or transferring the waste to another party;
                    (v)  allow exhaust ventilation to exceed 65 cfm/ft² (20 m³/min/m²) of degreaser open area, unless necessary to meet OSHA requirements.
                    (vi)  use ventilation fans near the degreaser opening; or,
                    (vii)  allow water to be visually detectable in VOC exiting the water separator.
          (3)  Compliance and recordkeeping.  Compliance shall be determined in accordance with EPA document 450/2-77-022 and all test and maintenance records shall be retained by the source for at least two years.

     (c)  Conveyorized degreasing unit.
          (1)  Operating requirements.  An owner or operator of a conveyorized degreasing unit using VOC shall ensure that the following requirements are met.
               (A)  Exhaust ventilation shall not exceed 65 cfm/ft² (20 m³/min/m²) of degreaser opening, unless necessary to meet OSHA requirements.
               (B)  Work place fans shall not be used near the degreaser opening.
               (C)  Carry-out emissions shall be minimized by:
                    (i)  racking parts for best drainage; and,
                    (ii)  maintaining vertical conveyor speed at less than 11 ft/min (3.4 m/min).
               (D)  Evaporation of waste VOC into the atmosphere shall not be greater than 20 percent of the waste (by weight) when disposing of the waste or transferring the waste to another party.
               (E)  Waste VOC shall be stored only in covered containers.
               (F)  VOC leaks must be repaired immediately, or the degreaser must be shut down.
               (G)  Water shall not be visibly detectable in the VOC exiting the water separator.
               (H)  A permanent conspicuous label summarizing the operating requirements listed in 252:100-39-42(b) and 252:100-39-42(c) shall be attached to the unit.
          (2)  Control requirements.  In addition to the requirements in 252:100-39-42(c)(1), any unit that has an air/vapor interface of more than 21.5 ft² (2.0 m²) shall be subject to the following control requirements.
               (A)  Major control devices.  The degreaser must be controlled by either:
                    (i)  a refrigerated chiller;
                    (ii)  a carbon adsorption system that exhausts less than 25 ppmv of VOC averaged over a complete adsorption cycle and has ventilation equal to or greater than 50 cfm/ft² (15 m³/min/m²) of air/vapor area (when down-time covers are open); or,
                    (iii)  a system demonstrated to have control efficiency equivalent to or better than either of the above.
               (B)  Carryover prevention.  Either a drying tunnel, or another means such as rotating (tumbling) basket, sufficient to prevent cleaned parts from carrying out VOC liquid or vapor subject to space limitations must be installed.
               (C)  Safety switches.  The following safety switches must be installed and be operational.
                    (i)  Condenser flow switch and thermostat that shuts off sump heat if coolant is either not circulating or too warm.
                    (ii)  Spray safety switch that shuts off spray pump or conveyor if the vapor level drops excessively, e.g. more than 4 in (10 cm).
                    (iii)  Vapor level control thermostat that shuts off sump heat when vapor level rises too high.
               (D)  Minimized openings.  Entrances and exits shall silhouette work loads so that the average clearance between parts and the edge of the degreaser opening is either less than 4 in. (10 cm) or less that 10 percent of the width of the opening.
               (E)  Covers.  Down-time covers must be placed over entrances and exits of conveyorized degreasers immediately after the conveyor and exhaust are shutdown and removed just before they are started up.
          (3)  Compliance and recordkeeping.  Compliance shall be determined in accordance with EPA document 450/2-77-022. All test and maintenance records shall be retained by the source for at least two years.

     (d)  Alternative control methods.  As an alternative to the requirements of 252:100-39-42(a) through 252:100-39-42(c) and subject to EPA approval, an operator may request the approval by the Division Director of other methods of control.  The applicant must demonstrate that the proposed method will prevent at least 80 percent of the emissions from each source from being emitted to the atmosphere, as determined by the appropriate test methods selected from EPA Methods l through 4, 18, 25, 25A and 25B.


252:100-39-43.  Graphic arts systems

     (a)  Definitions.  The following words and terms, when used in this Section, shall have the following meaning, unless the context clearly indicates otherwise.
          (1)  "Flexographic printing" means the application of words, designs and pictures to a substrate by means of a roll printing technique in which the pattern to be applied is raised above the printing roll and the image carrier is made of rubber or other elastomeric materials.
          (2)  "Packaging rotogravure printing" means rotogravure printing upon paper, paper board, metal foil, plastic film, and other substrates, that are, in subsequent operations, formed into packaging products and labels for articles to be sold.
          (3)  "Publication rotogravure printing" means rotogravure printing upon paper which is subsequently formed into books, magazines, catalogues, brochures, directories, newspaper supplements, and other types of printed materials.
          (4)  "Roll printing" means the application of words, designs and pictures to a substrate usually by means of a series of hard rubber or steel rolls each with only partial coverage.
          (5)  "Rotogravure printing" means the application of works, designs and pictures to a substrate by means of a roll printing technique that involves an intaglio or recessed image areas in the form of cells.

     (b)  Applicability.  This Section applies only to packaging rotogravure, publication rotogravure, and flexographic printing facilities whose potential emissions of VOC are equal to or more than 100 tons/yr (90 Mg/yr).  Potential emissions shall be calculated based on historical records of actual consumption of VOC and ink.

     (c)  Provisions for specific processes.
          (1)  An owner or operator of a facility subject to this Section which uses VOC containing ink shall ensure that one of the following conditions is met.
               (A)  The volatile fraction of ink, as it is applied to the substrate, contains 25.0 percent by volume or less of VOC and 75.0 percent by volume or more of water.
               (B)  The ink as it is applied to the substrate, less water, contains 60.0 percent by volume or more of nonvolatile material.
               (C)  The owner or operator installs and operates:
                    (i)  a carbon adsorption system that reduces the VOC emissions from the capture system by at least 90.0 percent by weight;
                    (ii)  an incineration system that oxidizes at least 90.0 percent of the VOC measured as total combustible carbon to carbon dioxide and water; or,
                    (iii)  an alternative VOC emission reduction system demonstrated to have at least 90.0 percent reduction efficiency, measured across the control system which has been approved by the Division Director.
          (2)  A capture system must be used in conjunction with the emission control systems in 252:100-39-43(c)(1)(C).  The design and operation of the capture system must be consistent with good engineering practice, and shall be required to provide for an overall reduction in VOC emissions of at least:
               (A)  75.0 percent where a publication rotogravure process is employed;
               (B)  65.0 percent where a packaging rotogravure process is employed; or,
               (C)  60.0 percent where a flexographic printing process is employed.

     (d)  Compliance schedule.  Compliance with this Section shall be accomplished by affected facilities by May 23, 1982.

     (e)  Testing.  Test procedures to determine compliance with this Subchapter must be consistent with EPA Reference Method 24 or equivalent ASTM Methods.


252:100-39-44.  Manufacture of pneumatic rubber tires

     (a)  Definitions.  The following words and terms, when used in this Section, shall have the following meaning, unless the context clearly indicates otherwise.
          (1)  "Automatic tread end cementing" means the application of a VOC based cement to the tire tread ends by automated devices.
          (2)  "Bead dipping" means the dipping of an assembled tire bead into a VOC based cement.
          (3)  "Green tires" means assembled tires before molding and curing have occurred.
          (4)  "Green tire spraying" means the spraying of green tires, both inside and outside, with release compounds that help remove air from the tire during molding and prevent the tire from sticking to the mold after curing.
          (5)  "Manual tread end cementing" means the application of a VOC based cement to the tire tread ends by manufacturers.
          (6)  "Passenger type tire" means agricultural, airplane, industrial, mobile home, light and medium duty truck, and passenger vehicle tires with a bead diameter up to but not including 20.0 inches and cross section dimension up to 12.8 inches.
          (7)  "Pneumatic rubber tire manufacture" means the production of pneumatic rubber, passenger type tires on a mass production basis.
          (8)  "Undertread cementing" means the application of a VOC based cement to the underside of a tire tread.
          (9)  "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 VOCs.  These sprays may contain an average of up to five percent VOC.

     (b)  Applicability.
          (1)  This Section applies to VOC emissions from all major source pneumatic rubber tire manufacturing facilities located in Oklahoma County from:
               (A)  undertread cementing;
               (B)  automatic tread end cementing; and,
               (C)  green tire spraying.
          (2)  The provisions of this Section do not apply to the production of specialty tires for antique or other vehicles when produced on an irregular basis or with short production runs.  This exemption applies only to tires produced on equipment separate from normal production lines for passenger type tires.
          (3)  Manual tread end cementing operations are exempt from the provisions of this Section.

     (c)  Control requirements.
          (1)  Undertread cementing or automatic tread end cementing.  The owner or operator of an undertread cementing, or automatic tread end cementing, operation subject to this Section shall install and operate the following.
               (A)  A capture system, designed to achieve maximum reasonable capture from all undertread cementing, and automatic tread end cementing operations.  Maximum reasonable capture would require that hood enclosures be designed to minimize open areas and enclose as much of the emission source as practical while maintaining a minimum in-draft velocity of 200 ft/min (61 m/min) except during times when the enclosure must be opened to allow work inside or for the inspections of the product in progress.  Maximum reasonable capture shall be consistent with:
                    (i)  Industrial Ventilation, A Manual of Recommended Practices, 14th Edition, American Federation of Industrial Hygienists; and,
                    (ii)  Recommended Industrial Ventilation guidelines, U.S. Department of Health Education and Welfare, National Institute of Occupational Safety and Health.
               (B)  A control device that meets the requirements of one of the following systems.
                    (i)  A carbon adsorption system designed and operated so that there is at least an initial 95.0 percent removal of VOC by weight from the gases ducted to the control device with at least a 90 percent 3 year removal average.
                    (ii)  An incineration system that oxidizes at least 90.0 percent of the VOCs (measured as total combustible carbon) which enter the incinerator to carbon dioxide and water.
                    (iii)  An alternative VOC emission reduction system certified by the owner or operator to have at least a 90.0 percent reduction efficiency, measured across the control system, and that has been approved by the Division Director.
          (2)  Green tire spraying.  The owner or operator of a green tire spraying operation subject to this Section shall implement one of the following means of reducing VOC emissions.
               (A)  Substitute water-based sprays for the normal VOC-based mold release compound.
               (B)  Install a capture system designed and operated to capture and transfer at least 90.0 percent of the VOC emitted by the green tire spraying operation to a control device, and install and operate a control device that meets the requirements of one of the following systems.
                    (i)  A carbon adsorption system designed and operated so that there is at least 95.0 percent removal of VOC by weight from the gases ducted to the control device.
                    (ii)  An incineration system that oxidizes at least 90.0 percent of the VOCs (measured as total combustible carbon) to carbon dioxide and water.
                    (iii)  An alternative VOC emission reduction system approved by the Division Director and certified by the owner or operator to have at least a 90.0 percent reduction efficiency, measured across the control system.
          (3)  Exemption.  If the total VOC emissions from all undertread cementing, tread-end cementing, bead dipping, and green tire spraying operations at a pneumatic rubber tire manufacturing facility do not exceed 57 g/tire, 252:100-39-44(c)(1) and 252:100-39-44(c)(2) shall not apply.

     (d)  Compliance schedule.  Compliance with this Section will be accomplished by affected facilities on or before December 31, 1982.

     (e)  Testing and monitoring.
          (1)  Test procedures to determine compliance with this Section must be approved by the Division Director and be consistent with:
               (A)  EPA Guideline Series Document "Measurement of Volatile Organic Compounds," EPA-450/2-78-041.
               (B)  Appendix A of "Control of Volatile Organic Emissions from Existing Stationary Sources - Volume II: Surface coating of Cans, Coils, Paper, Fabrics, Automobiles, and Light-Duty Trucks," EPA-450/2-77-008.
          (2)  The Division Director may accept, instead of green tire spray analysis, a certification by the manufacturer of the composition of the green tire spray, if supported by actual batch formulation records.
          (3)  If add-on control equipment is used, continuous monitors shall be installed, periodically calibrated, and operated at all times that the associated control equipment is operating.  These monitors shall measure:
               (A)  exhaust gas temperature of an incinerator;
               (B)  temperature rise across a catalytic incinerator bed;
               (C)  breakthrough of VOC on a carbon adsorption unit; and,
               (D)  any other parameter for which a continuous monitoring or recording device is required by the Division Director.


252:100-39-45.  Petroleum (solvent) dry cleaning

     (a)  Definitions.  The following words and terms, when used in this Section, shall have the following meaning, unless the context clearly indicates otherwise.
          (1)  "Cartridge filters" means perforated canisters containing filtration paper and/or activated carbon that are used in a pressurized system to remove solid particles and fugitive dyes from soil-laden petroleum solvent.
          (2)  "Containers and conveyors of petroleum solvent" means piping, ductwork, pumps, storage tanks, and other ancillary equipment that are associated with the installation and operation of washers, dryers, filters, stills, and settling tanks.
          (3)  "Dry cleaning" means a process of the cleaning of textiles and fabric products in which articles are washed in a non-aqueous solution (petroleum solvent) and then dried by exposure to a heated air stream.
          (4)  "Housekeeping" means those measures and precautions necessary to minimize the release of petroleum solvent to the atmosphere.
          (5)  "Operations parameters" means the activities required to insure that the equipment is operated in a manner to preclude the loss of petroleum solvents to the atmosphere.
          (6)  "Perceptible leaks" means any petroleum solvent vapor or liquid leaks that are conspicuous from visual observation, such as pools or droplets of liquid, or buckets or barrels of petroleum solvent or petroleum solvent-laden waste standing open to the atmosphere.
          (7)  "Petroleum solvent" means organic material produced by petroleum distillation comprising a hydrocarbon range of 8 to 12 carbon atoms per organic molecule that exists as a liquid under standard conditions.

     (b)  Applicability.  This Section applies to petroleum solvent washers, dryers, filters, settling tanks, vacuum stills, and other containers and conveyors of petroleum solvent that are used in petroleum solvent dry cleaning facilities in Tulsa County only.

     (c)  Operating requirements.
          (1)  The owner or operator of a petroleum solvent dry cleaning facility shall not operate any dry cleaning equipment using petroleum solvents unless:
               (A)  there are no perceptible liquid or vapor leaks from any portion of the equipment;
               (B)  all washer lint traps, button traps, access doors and other parts of the equipment where petroleum solvent may be exposed to the atmosphere are kept closed at all times except when required for proper operation or maintenance;
               (C)  the still residue is stored in sealed containers and the used filtering material is placed into a sealed container suitable for use with petroleum solvents, immediately after removal from the filter and disposed of in the prescribed manner; or,
               (D)  cartridge filters containing paper or carbon or a combination thereof, which are used in the dry cleaning process are drained in the filter housing for at least 24 hours prior to removal.
          (2)  The owner or operator of a petroleum solvent dry cleaning facility shall not operate any drying tumblers and cabinets that use petroleum solvents unless tumblers and cabinets are operated in a manner to control petroleum solvent vapor leaks by reducing the number of sources where petroleum solvent is exposed to the atmosphere.  Under no circumstances should there be any open containers (can, buckets, barrels) of petroleum solvent or petroleum solvent-containing material.  Equipment containing solvent (washers, dryers, extractors, and filters) should remain closed at all times other than during maintenance or load transfer.  Lint filter and button trap covers should remain closed except when petroleum solvent-laden lint and debris are removed.  Gaskets and seals should be inspected and replaced when found worn or defective.  Petroleum solvent-laden clothes should never be allowed to remain exposed to the atmosphere for longer periods than are necessary for load transfers.  Finally, vents on petroleum solvent-containing waste and new petroleum solvent storage tanks should be constructed and maintained in a manner that limits petroleum solvent vapor emissions to the maximum possible extent.
          (3)  The owner or operator shall repair all petroleum solvent vapor and liquid leaks within 3 working days after identifying the sources of the leaks.  If necessary repair parts are not on hand, the owner or operator shall order these parts within 3 working days, and repair the leaks no later than 3 working days following the arrival of the necessary parts.

     (d)  Disposal of filters.  Filters from the petroleum dry cleaning facility shall be disposed of by:
          (1)  incineration at a facility approved by the fire marshall's office for such disposal;
          (2)  by recycling through an approved vendor of this service; or,
          (3)  by any other method approved by the Division Director.

     (e)  Compliance schedule.  Compliance with 252:100-39-45(c)(1) through 252:100-39-45(c)(3), shall be accomplished by affected facilities on or before October l, 1986.


252:100-39-46.  Coating of parts and products

     (a)  Applicability.  This Section shall apply only to industries located in Tulsa County which manufacture and/or coat metal parts and products, such as large farm machinery, small farm machinery, small appliances, commercial machinery, industrial machinery and fabricated metal products.  Architectural coating, aerospace coating, and automobile refinishing are not included.

     (b)  Definitions.  The following words and terms, when used in this Section, shall have the following meaning, unless the context clearly indicates otherwise.
          (1)  "Air or forced air dry coatings" means coatings that are dried by the use of air or forced warm air at temperatures up to 194 degrees F.
          (2)  "Clear coat" means a coating that lacks color and opacity or is transparent and uses the undercoat as a reflectant base.
          (3)  "Extreme performance coatings" mean coatings designed for harsh exposure or extreme environmental conditions (e.g., exposure to the weather all of the time, temperature above 200 degrees F, detergents, abrasive and scouring agents, solvents, corrosive atmosphere or similar conditions).
          (4)  "Facility" means all emission sources located on contiguous properties under common control which are affected by the surface coating provisions of 252:100-37 and 252:100-39.
          (5)  "Powder" means a coating that is applied in a finely divided state by various methods, and becomes a continuous, solid film when the metal part or product is moved to an oven for curing.
          (6)  "Transfer efficiency" means the weight (or volume) of coating solids adhering to the surface being coated divided by the total weight (or volume) of coating solids delivered to the applicator.

     (c)  Existing source requirement.  No owner or operator shall discharge or cause the discharge into the atmosphere from an existing coating line or individual coating operation any VOC in excess of the amounts listed in 252:100-39-46(d) as calculated by EPA method 24, 40 CFR Part 60.

     (d)  Standards.  The following table enumerates the limitations for surface coatings in pounds of VOC per gallon of coating as applied (water and exempt compounds).  If more than one limit listed in the table is applicable to a specific coating, then the least stringent limitation shall be applied.
 

    (e)  Emission factor.  For the purposes of calculating an emission factor (EF) in pounds VOC per gallon of coating solids for use in the development of a plant-wide emission plan as described in 252:100-39-46(j)(1), the following formula will be utilized:

          EF = V D / l-(V+W) = V D / S 

where:

          (1)  V = volume fraction of VOC in coating.
          (2)  D = density of VOC in the coating.
          (3)  W = volume fraction of water in coating.
          (4)  S = l-(V+W) = volume fraction of solids in coating.

     (f)  Compliance.  Compliance with the coating limits listed in 252:100-39-46(d) is to be calculated on a daily weighted average basis.

     (g)  VOC-containing materials.  VOC-containing materials used for clean up shall be considered in the VOC content limits listed in 252:100-39-46(d) unless:
          (1)  the VOC containing materials are maintained in a closed container when not in use;
          (2)  closed containers are used for the disposal of cloth or paper or other materials used for surface preparation and cleanup;
          (3)  the spray equipment is disassembled and cleaned in a VOC vat and the vat is closed when not in use; or,
          (4)  the VOC containing materials used for the clean up of spray equipment are sprayed directly into closed containers.

     (h)  Exemptions.  Facilities with a potential to emit 10 tons/year or less of VOC from coating operations are exempt from this Section.  Once this limit is exceeded, the facility will always be subject to this Section.

     (i)  Alternate standard.  Coatings with VOC contents in excess of those allowed by 252:100-39-46(d) may be used if both of the following conditions are met.
          (1)  Emissions are reduced to levels equivalent to those that would occur if the VOC content of the coatings met the limits contained in 252:100-39-46(d) and there is an overall control efficiency of at least:
               (A)  85 percent by incineration;
               (B)  85 percent by absorption; or,
               (C)  85 percent by any other equipment of equivalent reliability and effectiveness.
          (2)  No air pollution, as defined by the Clean Air Act, results.

     (j)  Emission plan.  
          (1)  Development of a plant-wide emission plan.  An owner or operator may develop a plant-wide emission plan consistent with EPA's Emission Trading Policy as published in the December 4, 1986 Federal Register instead of having each coating line comply with the VOC content limitations contained in 252:100-39-46(d), if the following conditions are met.
               (A)  The owner or operator demonstrates by the methods prescribed in 252:100-5-2.1(d) that sufficient reductions in VOC emissions may be obtained by controlling other sources within the plant to the extent necessary to compensate for all excess emissions which result from one or more coating lines not achieving the prescribed limitation.  Such demonstration shall be made in writing and shall include:
                    (i)  a complete description of the coating line or lines that can not comply with the VOC content limitation in 252:100-39-46(d);
                    (ii)  quantification of emissions, in terms of pounds per day of VOCs, which are in excess of the prescribed VOC content limitation for each coating line described in 252:100-39-46(j)(A)(i);
                    (iii)  a complete description of how emissions will be decreased at specific sources to compensate for excess emissions from each coating line described in 252:100-39-46(j)(A)(i) and the date on which such reduction will be achieved;
                    (iv)  a transfer efficiency based on a 60 percent baseline with emissions expressed in pounds of VOC per gallon of solids when transfer efficiency is used to compensate for excess emissions from spray painting operations;
                    (v)  a demonstration of credits for improvements in transfer efficiency with in plant testing that complies with EPA methods.
                    (vi)  quantification of emissions, in terms of pounds per day of VOCs, for each source both before and after the improvement or installation of any applicable control system, or any physical or operational changes to such a facility or facilities to reduce emissions and the date on which such reductions will be achieved; and,
                    (vii)  a description of the procedures and methods used to determine the emissions of VOCs.
               (B)  The plant-wide emission reduction plan does not include decreases in emissions resulting from requirements of other applicable air pollution rules.  The plant-wide emission reduction plan as described in the Emissions Trading Policy may include voluntary decreases in emissions accomplished through installation or improvement of a control system or through physical or operational changes to emission units, including permanently reduced production or closing a facility, located on the premises of a surface-coating operation.
          (2)  Compliance with a plant-wide emission plan.  The implementation of a plant-wide emission reduction plan instead of compliance with the VOC content limitation prescribed in 252:100-39-46(d) has been expressly approved by the Executive Director and the EPA Administrator.  Upon approval of a plan, any emissions in excess of those established for each facility under the plan shall be a violation of these rules.

     (k)  Compliance, testing, and monitoring requirements.
          (1)  The Division Director may require at the expense of the owner or operator a demonstration of compliance with the emission limits using EPA Methods 24, 24A, 1-4, 25, 25A, 25B in 40 CFR 60.444 or EPA Document 450/3-84-019.  At a minimum, such test must show that the overall capture efficiency and destruction efficiency are equal to 85 percent (e.g., 90 percent capture efficiency multiplied by 95 percent destruction efficiency equals 85.5 percent system efficiency).  The one hour bake option in Method 24 is required when doing compliance testing.
          (2)  Testing for plant-wide emission plans shall be conducted at the expense of the owner or operator to demonstrate compliance with the VOC content limits contained in 252:100-39-46(d).
          (3)  Monitoring shall be required of any owner or operator subject to this Section who uses add-on control equipment for compliance.  Such monitoring shall include installation and maintenance of monitors to accurately measure and record operational parameters of all required control devices to ensure the proper functioning of those devices in accordance with design specifications, including:
               (A)  the exhaust temperature of direct flame incinerators and/or gas temperature immediately upstream and downstream of any catalyst bed;
               (B)  the total amount of VOCs recovered by carbon adsorption or other VOC recovery system during a calendar month; and,
               (C)  the dates and reasons for any maintenance and repair of the required control devices and the estimated quantity and duration of emissions during such activities;

     (l)  Reporting and recordkeeping.
          (1)  The owner or operator of a facility subject to this Section shall submit to the Division Director upon written request reports detailing specific VOC sources; the quantity of coatings used for a specific time period, VOC content of each coating; capture and control efficiencies; and any other information pertinent to the calculation of VOC emissions.  The data necessary to supply the requested information shall be retained by the owner or operator for a minimum of two years.
          (2)  The owner or operator of a facility subject to this Section shall maintain records of any testing conducted at an affected facility in accordance with the provisions specified in 252:100-39-46(k), as well as all other records, for at least two years.  These records shall be available to representatives of the DEQ upon request.

     (m)  Compliance date.  The date of compliance with the requirements of this Section is December 31, 1990.


252:100-39-47.  Control of VOC emissions from aerospace industries coatings operations

     (a)  Applicability.
          (1)  This Section applies to all aerospace facilities located in Tulsa County.  Sources once subject to this Section are always subject.
          (2)  This Section does not apply to individual coating formulations that, when aggregated, do not exceed 55 gal/yr for the facility.
          (3)  Facilities with a potential to emit 10 tons/year or less of VOC from coatings operations are exempt from this Section.

     (b)  Definitions.  The following words and terms, when used in this Section, shall have the following meaning, unless the context clearly indicates otherwise
          (1)  "Aerospace" means the industries, air bases and depots that manufacture, rework, or repair aircraft or military equipment components for either commercial or military customers.
          (2)  "Aircraft" means any machine designed to travel through the earth's atmosphere.  This group includes but is not limited to airplanes, balloons, dirigibles, drones, helicopters, missiles, and rockets.
          (3)  "Alternate reasonably available control technology (ARACT)" 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 as determined on a case-by-case basis.
          (4)  "Coating" means a material which covers a surface which alters the surface characteristics and from which VOCs can be emitted during the application and/or curing process.
          (5)  "CTG" means the Control Techniques Guidance Document "Control of Volatile Organic Emissions From Existing Stationary Sources, Volume VI: Surface Coating of Miscellaneous Metal Parts and Products," EPA No. 450/2-78-015.
          (6)  "Facility" means all of the pollutant-emitting activities that belong to the same industrial grouping, are located on one or more contiguous or adjacent properties, and are under the control of the same person or persons under common control.
          (7)  "Low VOC coating (LVOCC)" means a coating that contains less VOC than the conventional coatings used by the industry.  Low VOC coatings include waterborne, higher solids, electrodeposition, and powder coatings.
          (8)  "Reasonably available control technology (RACT)" means control technology that is reasonably available considering technological and economic feasibility and the need to impose such controls to attain and maintain a National Ambient Air Quality Standard.

     (c)  General requirements.
          (1)  All affected facilities shall develop an emissions reduction plan as set forth in 252:100-39-47(d).  This plan, upon approval, shall constitute ARACT for that particular facility.
          (2)  ARACT must be installed and operating as provided in the approved plan no later than January 1, 1991 for existing facilities, unless additional phased compliance dates are approved in the plan.
          (3)  New and modified sources and coating applications not included in the plan are subject to the permit requirements set forth in 252:100-7 or 252:100-8, and will be submitted to EPA as source-specific SIP revisions, unless one of the following applies.
               (A)  The new coatings meet the presumptive norm of 3.5 pounds of VOC per gallon less water and exempt compounds.
               (B)  The total usage of the new coating does not exceed 55 gal/yr of each coating formulation.

     (d)  Emissions reduction plan.
          (1)  Plan development.  Each plan shall include:
               (A)  a detailed, reasoned and exhaustive review of each source of emissions within the facility and the entire plant collectively;
               (B)  identification and quantification of emissions, in terms of pounds per day, of all VOC both before and after the application of ARACT;
               (C)  a detailed, innovative engineering effort directed toward finding alternative air management schemes that can be incorporated in order to abate emissions at costs which are reasonable;
               (D)  a consideration of the level of control that is achievable using available alternative coatings, to include LVOCC for every application;
               (E)  a demonstration of the level of control achievable using available add-on control devices which shall include, at a minimum, the feasibility/infeasibility of carbon adsorption, incineration/flaring, condensation, and a combination of carbon adsorption and incineration/flaring;
               (F)  a consideration of facility redesign, including recirculation, reduced air flows, consolidation of spray operations, and installation of common control devices for two or more separate coating operations;
               (G)  a consideration of alternative applications, to improve transfer efficiency, including high-volume-low-pressure spray equipment, heated spray guns, and electrostatic spray equipment/powder coatings;
               (H)  an explanation why each source is not a typical coating source covered by the CTG as defined in 252:100-39-47(b);
               (I)  a cost/benefit analysis for all control technology considered; and,
               (J)  a detailed compliance schedule that includes the emission limit and/or control techniques for each emission source which together with other relevant considerations, shall be set forth in a separate section of the plan that summarizes and outlines ARACT for the referenced facility.
          (2)  Submission of emission reduction plans.  Three copies of the emissions reduction plan shall be submitted to the Division and one shall be submitted to EPA, Region VI.
          (3)  Action on plan.  Within 30 days of submittal, or of May 25, 1990, whichever is later, the Division shall, considering any comments submitted by EPA, either approve, modify or disapprove the plan.
          (4)  Public hearing.  The Division shall, at the first meeting of the Air Quality Council following the approval, modification, or disapproval of the plan, present at public hearing, the staff's findings and ARACT determination.
          (5)  Final approval.  Upon consideration of comments and recommendations from the Council, the owner or operator of the affected facility, the public, and EPA, the DEQ shall, within ten (10) days after the public hearing, issue a final ARACT approval.  Final approval shall constitute ARACT for the affected facility.
          (6)  Compliance.  The owner or operator shall be responsible for installation and operational provisions of the approved ARACT.  Any violation of the plan or of its provisions shall constitute a violation of this Section.
          (7)  Submission of SIP revision.  Upon approval by the DEQ, the ARACT determination shall be submitted to EPA as a SIP revision.

     (e)  Reporting and recordkeeping.
          (1)  Recordkeeping requirements.  The owner or operator shall maintain:
               (A)  a material safety data sheet which documents the VOC content, composition, solids content, VOC density and other relevant information regarding each coating and VOC available for use in the affected surface coating processes;
               (B)  information detailing the operational parameters of the coating process sufficient to determine continuous compliance with the applicable control limits;
               (C)  information as to the amounts of each type coating used and the amounts of VOC used for dilution in each coating type for each coating operation;
               (D)  daily usage records for all coatings used that do not comply with the applicable control limits specified in the plan; and,
               (E)  records of any monitoring and testing conducted at an affected facility in accordance with the provisions specified in 252:100-39-47(f).
          (2)  Method of calculating VOC content in coatings.  Records required by 252:100-39-47(e)(1)(A) through 252:100-39-47(e)(1)(E) detailing VOC in pounds per gallon of coating (less water and exempt compounds) shall be calculated as follows:

               VOC in lbs/gal of coating = Wv-Ww-Wx / 1-Vw-Vx  

where:

               (A)  Wv = weight of all volatiles;
               (B)  Ww = weight of water;
               (C)  Wx = weight of exempt compounds;
               (D)  Vw = volume fraction of water; and,
               (E)  Vx = volume fraction of exempt compounds.

          (3)  Maintenance of records.  Records required by 252:100-39-47(e)(1)(A) through 252:100-39-47(e)(1)(E) shall be maintained for at least two years and shall be made available upon request by representatives of the AQD or EPA.
          (4)  Alternative recordkeeping provision.  Alternatively to 252:100-39-47(e)(1) through 252:100-39-47(e)(3), an equivalent recordkeeping provision that satisfies the substantive requirements of 252:100-39-47(e)(1) through 252:10-39-47(e)(3) may be approved under the plan.

     (f)  Testing and monitoring.
          (1)  Testing.  The Division may require testing at the expense of the owner or operator to establish emission from any particular source or sources.  Test methods may include 1-4, 18, 24, 24A, 25A, 25B found in the Appendix A of 40 CFR Part 60, including the procedures found at 40 CFR 60.444.
          (2)  Monitoring.  Monitoring shall be required of any owner or operator who uses add-on control equipment for compliance.  Such monitoring shall accurately measure and record operational parameters of all required control devices to ensure the proper functioning of those devices in accordance with design specifications, including:
               (A)  the exhaust temperature of direct flame incinerators and/or gas temperature immediately upstream and downstream of any catalyst bed;
               (B)  the total amount of VOCs recovered by carbon adsorption or other VOC recovery system during a calendar month; and,
               (C)  the dates and reasons for any maintenance and repair of the required control devices and the estimated quantity and duration of VOC emissions during such activities.
(252:100-39-47 Effective May 25, 1990)


252:100-39-49.  Manufacturing of fiberglass reinforced plastic products

     (a)  Applicability.
          (1)  This Section applies to any process gas stream with actual VOC emissions that exceed six tons per year based on 6,240 hours of operation per year.
          (2)  Once the limit in 242:100-39-49(a)(1) is exceeded, the controls required in 252:100-39-49(b) must be put in place and maintained and used at any operating level.

     (b)  Standards.  Affected facilities shall limit emissions of VOC from fiberglass manufacturing by use of control equipment which can demonstrate an 85 percent reduction in the VOC released from each process stream (e.g. 90 percent capture efficiency multiplied by 95 percent destruction efficiency equals 85.5 percent system efficiency).

     (c)  Compliance.  All affected facilities must comply with one of the following.
          (1)  Meet the requirements of 252:100-39-49(b) by February 13, 1991.
          (2)  Have an approved plan for the reduction of VOC emissions as required by 252:100-39-49(b) by February 13, 1991.
               (A)  The plan shall be submitted by August 13, 1990, and shall:
                    (i)  detail those emissions which will be controlled;
                    (ii)  detail the means by which control will be achieved; and,
                    (iii)  demonstrate that compliance will be achieved by February 13, 1992.
               (B)  The Air Quality Council shall have approval authority for the plans.
               (C)  All approved plans shall be submitted to the EPA as SIP revisions.

     (d)  Demonstration of compliance.
          (1)  The Division Director may require at the expense of the owner or operator a demonstration of compliance with the requirements of 252:100-39-49(b).
          (2)  The testing shall be accomplished using the appropriate EPA test method or methods.  These include methods 1-4, 18-25, 25A, 25B and 40 CFR 60.444.
          (3)  Initial compliance testing shall be accomplished within 180 days of the applicable compliance date.
          (4)  Testing for the emissions plan described in 252:100-39-49(c)(2) shall be conducted at the expense of the owner or operator at his expense and shall demonstrate compliance with the emission limits contained in the approved plan.

     (e)  Recordkeeping.
          (1)  The owner or operator of a facility subject to this Section shall submit to the Division Director upon written request, reports that include:
               (A)  details of specific VOC sources;
               (B)  the quantity of VOC used during specific months;
               (C)  a description of the VOC used;
               (D)  control equipment efficiencies;
               (E)  details of maintenance performed on all control equipment;
               (F)  equipment downtime; and,
               (G)  any other information pertinent to the calculation of VOC emissions from the facility.
          (2)  The records required in 252:100-39-49(e)(1) shall be maintained by the source for at least two years.  
(252:100-390-49, Effective February 12, 1990)