250-RICR-120-05-35
The purpose of this regulation is to limit emissions of volatile organic compounds and hazardous air pollutants from wood products manufacturing operations.
A. Unless otherwise expressly defined in this section, the terms used in this regulation shall be defined by reference to Part 0 of this Subchapter (General Definitions). As used in this regulation, the following terms shall, where the context permits, be construed as follows:
51. "Strippable booth coating" means a coating that:
61. "Wood products facility" means a facility which is engaged in coating the surface of products manufactured of wood or wood products, including, but not limited to, particle board, reed, rattan and wicker.
C. The owner or operator of a facility which is a major source of hazardous air pollutants (HAP) from wood products manufacturing operations but which has not emitted more than ten (10) tons of any one HAP or more than twenty-five (25) tons of any combination of HAP from wood products manufacturing operations in any 12-month period, may apply to the Director for an exemption from the VHAP emissions limitations in §§ 35.7.2, 35.7.3, 35.8(B), and 35.8(C) of this Part. Exemption will be given in the form of an enforceable document, and will include the following conditions:
2. The following records shall be maintained at the facility for a period of five (5) years and made available to the Department or the EPA upon request:
A. The owner or operator of a facility subject to this regulation which has the potential to emit greater than or equal to twenty-five (25) tons per year of volatile organic compounds (VOC) shall limit VOC emissions from wood products finishing operations by:
B. Prior to January 1, 2020, the owner or operator of a wood products coating facilty subject to this regulation shall meet the emission limitations listed in § 35.7.1 (B)(1) of this Part using one of more of the methods in § 35.7.1(A)(1) through (4) of this Part.
1. Emissions Limitations for Coatings used Prior to January 1, 2020
| Coating Category | lbs VOC/gal coating minus water and exempt compounds | lbs VOC/lb solids |
| clear topcoats containing HOC | 4.6 | 1.2 |
| clear topcoats not containing HOC | 5.7 | 2.5 |
| fillers | 4.2 | 1.0 |
| high-solids stains | 5.8 | 2.7 |
| low-solids stains, toners and washcoats containing HOC | 4.0 | 0.9 |
| low-solids stains, toners and washcoats not containing HOC | 6.7 | 7.5 |
| inks | 4.2 | 1.0 |
| multi-colored coatings | 5.7 | 2.5 |
| pigmented coatings | 5.0 | 1.6 |
| sealers containing HOC | 4.6 | 1.2 |
| sealers not containing HOC | 5.7 | 2.5 |
2. In addition to complying with the limitations in § 35.7.1(B)(1) of this Part, on and after March 7, 1998, the owner or operator of a facility subject to this regulation which has the potential to emit greater than or equal to twenty-five (25) tons per year of VOC shall:
C. Effective January 1, 2020, the owner or operator of a wood products coating facility subject to this regulation shall comply with the emissions limitations in § 35.7.1(C)(1) of this Part using one or more of the methods in § 35.7.1(A)(1) through (4) of this Part.
1. Emissions Limitations for Coatings used after January 1, 2020
| Coating operations | lbs VOC/lb of solid as applied |
| Finishing OperationsTopcoat | 0.8 |
| Finishing system of topcoat and sealer | |
| Topcoats | 1.8 |
| Sealers | 1.9 |
| Acid-cured alkyd amino vinyl sealers and acid-cured alkyd amino conversion varnish topcoat system, exclusively | |
| sealer | 2.3 |
| topcoat | 2.0 |
| Non-acid-cured alkyd amino vinyl sealers and acid-cured alkyd amino conversion varnish topcoat system, exclusively | |
| sealers | 1.9 |
| topcoat | 2.0 |
| Acid-cured alkyd amino vinyl sealers and non-acid-cured alkyd amino conversion varnish topcoat system, exclusively | |
| sealer | 2.3 |
| topcoat | 1.8 |
A. The owner or operator of a facility subject to this regulation which is a major source of HAP from wood products manufacturing operations and which began operations before December 6, 1994, shall limit VHAP emissions from wood products finishing operations by:
B. The formaldehyde content of a finishing material shall be calculated as the amount of free formaldehyde present in the finishing material when it is applied.
C. The styrene content of a finishing material shall be based on an estimate of unreacted styrene, which shall be calculated by multiplying the amount of styrene monomer in the finishing material when it is applied by a factor of 0.16.
A. The owner or operator of a facility subject to this regulation which is a major source of HAP from wood products manufacturing operations and began operation on or after December 6, 1994, shall limit VHAP emissions from wood products finishing operations by:
B. The formaldehyde content of a finishing material shall be calculated as the amount of free formaldehyde present in the finishing material when it is applied.
A. VOC Emission Limitations for Cleaning Operations
B. VHAP Emission Limitations for Existing Gluing Operations
1. The owner or operator of a facility subject to this regulation which is a major source of HAP from wood products manufacturing operations and which began operation before December 6, 1994, shall limit VHAP emissions from contact adhesives used in gluing operations as follows:
C. VHAP Emission Limitations for New Gluing Operations
C. The work practice implementation plan shall be available for inspection by the EPA or the Department upon request and shall be modified by the facility if found to be inadequate.
C. Initial and refresher trainings shall include, at a minimum, the following topics:
D. The facility shall maintain records of the training program. Records shall include, at a minimum, the following:
4. A description of the methods to be used to demonstrate successful completion of initial and refresher training.
A. Equipment Leak Inspection and Repair
3. The owner or operator of a source subject to this regulation shall prepare and maintain a written leak inspection and maintenance plan that includes:
B. Operation and Maintenance Requirements
8. If a malfunction occurs that was not adequately addressed in the startup, shutdown, and malfunction plan, the owner or operator shall revise the plan within forty-five (45) days after the event to include detailed procedures for operating and maintaining the source during similar malfunction events and a program of corrective action for similar malfunctions of process or air pollution control equipment.
A. The owner or operator of a facility subject to this regulation shall account for organic solvent use in cleaning and washoff operations by recording the following information:
C. Spray Booth Cleaning
D. Storage Requirements
1. All finishing, gluing, cleaning, and washoff materials shall be stored in containers that are closed at all times except when material is being added or removed.
A. The owner or operator of any wood products facility which has the potential to emit twenty-five (25) tons per year or more of volatile organic compounds (VOC) from wood products manufacturing operations, and is not a major source of HAP from wood product manufacturing operations shall not use conventional air spray guns to apply finishing materials, except in the following situations:
7. The application of stain on a part for which it is technically or economically infeasible to use any other spray application technology. The facility must demonstrate technical or economic infeasibility by submitting documentation to the Department that the following criteria, either independently or in combination, are met:
8. Line Cleaning
9. Gun Cleaning
B. Beginning January 1, 2020, the owner or operator of a facility which is a major source of hazardous air pollutants from wood products manufacturing operations shall not use conventional air spray guns except when all emissions from the finishing application station are routed to a functioning control device.
A. Emissions from washoff operations shall be controlled by:
2. Minimizing dripping by tilting or rotating the part to drain as much organic solvent as possible.
A. Each owner or operator of a facility that is subject to this regulation and that is a major source of hazardous air pollutants from wood products manufacturing operations shall prepare and maintain a formulation assessment plan that:
2. Establishes a baseline level of usage by the facility for each VHAP as follows:
A. Compliance with the emissions limitations in §§ 35.7 and 35.8 of this Part through the use of compliant coatings shall be demonstrated by the following methods:
3. For facilities with continuous coaters, using one of the following procedures:
4. The Department or EPA will determine compliance either by reviewing the records specified in §§ 35.10.1(A)(1) through (3) of this Part or by conducting a performance test according to the specifications in §§ 35.12.1 and 35.12.2 of this Part. If the VOC or VHAP content of a coating determined by a performance test using the procedures specified in §§ 35.12.1 and 35.12.2 of this Part is greater than that indicated on a CPDS or by the facility's formulation or viscosity data, the performance test results shall govern.
A. To demonstrate compliance with the VOC emission limitations for a particular coating category listed in §§ 35.7.1(B)(1) of this Part for coatings used prior to January 1, 2020, through the use of averaging, the owner or operator of a facility shall, each week:
B. To demonstrate compliance with the VOC emission limitations for a particular coating category listed in § 35.7.1(C)(1) of this Part for coatings used after January 1, 2020, through the use of averaging, the owner or operator of a facility shall, each week:
C. To demonstrate compliance with the VHAP emission limitations in §§ 35.7.2 and 35.7.3 of this Part through the use of averaging, the owner or operator of a facility shall, each month:
2. Demonstrate that the value calculated for EVHAP is no greater than one (1) if the facility is complying with § 35.7.2 of this Part and is no greater than 0.8 if the facility is complying with § 35.7.3 of this Part.
B. Initial compliance with VOC emission limitations for finishing materials through the use of a control system shall be determined as follows:
C. Initial compliance with VHAP emission limitations for finishing materials through the use of a control system shall be determined as follows:
D. Initial compliance with VHAP emission limitations for gluing materials through the use of a control system shall be determined as follows:
2. Demonstrate that the value of Rn calculated using Equation 6 in § 35.10.3(D)(1) of this Part is less than or equal to the actual overall control efficiency (Ra) calculated using the capture efficiency (N) and control efficiency (F) of the control system measured in the initial performance test and Equation 4 in § 35.10.3(B)(3) of this Part.
F. Where a carbon adsorber is used, the operating parameters to be monitored shall be either the total regeneration mass stream flow for each regeneration cycle and the carbon bed temperature after each regeneration, or the concentration level of organic compounds exiting the adsorber, unless the owner or operator requests and receives approval from the Department and the EPA to establish other operating parameters. One of the following devices is required to monitor these parameters:
A. The owner or operator of a facility subject to this regulation shall maintain the following records for a period of five (5) years:
4. If viscosity measurements are used to track VOC and/or VHAP concentrations:
C. The owner or operator of a source using control equipment to comply with the emissions limitations in this regulation shall maintain the following records for a period of five (5) years:
D. The owner or operator of a facility subject to this regulation shall maintain onsite the work practice implementation plan and for five (5) years shall maintain onsite all records associated with fulfilling the requirements of that plan, as specified in § 35.9 of this Part, including, but not limited to:
E. Initial Notifications
1. The owner or operator of a facility subject to this regulation which was constructed before December 7, 1995, and which is a major source of HAP from wood products manufacturing operations shall submit an Initial Notification to the Office of Air Resources within thirty (30) days of becoming a major source of HAP from wood products manufacturing operations. Initial Notifications for facilities constructed before December 7, 1995, shall include the following information:
2. The owner or operator of a facility subject to this regulation which was constructed or reconstructed on or after December 7, 1995, and which is a major source of HAP from wood products manufacturing operations shall submit an Initial Notification in conjunction with its construction permit application. A facility constructed or reconstructed on or after December 7, 1995, which subsequently becomes a major source of HAP shall submit an Initial Notification within thirty (30) days of becoming a major source of HAP. Initial Notifications for facilities constructed on or after December 7, 1995, shall include the following information:
F. Initial Compliance Certification
2. Initial Compliance Certifications shall include the following information:
d. For a facility using a control system to comply with the emission limitations in this regulation, the Initial Compliance Certification shall identify each control device installed, including the identification number, permit number, installation date and equipment controlled. In addition, the following information must be submitted no more than sixty (60) days after completing the initial performance test of the control system:
G. Periodic Reports
1. The owner or operator of a facility subject to this regulation shall submit periodic reports to the Office of Air Resources according to the following specifications:
a. Periodic reports shall be submitted semi-annually by February 1 of each year for the reporting period of July 1 through December 31 of the previous year and by September 1 for the reporting period of January 1 through June 30, which include the following:
i. If an exceedance occurs, periodic reports must be submitted quarterly until a request to reduce the reporting frequency has been approved. Submittal frequencies may be reduced to semi-annual provided that the following conditions have been satisfied:
B. The owner or operator of a facility that uses a finishing material that does not release VOC reaction byproducts during the cure; for example, if all VOC is solvent; may request permission to use batch formulation information to demonstrate compliance. If the VOC content of a coating determined by 40 C.F.R. § 60 Appendix A-7 Method 24, incorporated in § 35.4(A) of this Part, test is greater than that indicated by the facility's formulation data, the 40 C.F.R. § 60 Appendix A-7 Method 24 test shall govern.
E. Sampling procedures shall follow the guidelines presented in "Standard Procedures for Collection of Coating and Ink Samples for VOC Content Analysis by Reference Method 24 and Reference Method 24A," EPA-340/1-91-010, incorporated in § 35.4(B) of this Part.
| Chemical name | CAS No. |
| Acetaldehyde | 75070 |
| Acetamide | 60355 |
| Acetonitrile | 75058 |
| Acetophenone | 98862 |
| 2-Acetylaminofluorine | 53963 |
| Acrolein | 107028 |
| Acrylamide | 79061 |
| Acrylic acid | 79107 |
| Acrylonitrile | 107131 |
| Allyl chloride | 107051 |
| 4-Aminobiphenyl | 92671 |
| Aniline | 62533 |
| o-Anisidine | 90040 |
| Benzene | 71432 |
| Benzidine | 92875 |
| Benzotrichloride | 98077 |
| Benzyl chloride | 100447 |
| Biphenyl | 92524 |
| Bis(2-ethylhexyl)phthalate (DEHP) | 117817 |
| Bis(chloromethyl)ether | 542881 |
| Bromoform | 75252 |
| 1,3-Butadiene | 106990 |
| Caprolactam | 105602 |
| Carbon disulfide | 75150 |
| Carbon tetrachloride | 56235 |
| Carbonyl sulfide | 463581 |
| Catechol | 120809 |
| Chloroacetic acid | 79118 |
| 2-Chloroacetophenone | 532274 |
| Chlorobenzene | 108907 |
| Chloroform | 67663 |
| Chloromethyl methyl ether | 107302 |
| Chloroprene | 126998 |
| Cresols (isomers and mixture) | 1319773 |
| o-Cresol | 95487 |
| m-Cresol | 108394 |
| p-Cresol | 106445 |
| Cumene | 98828 |
| 2,4-D (2,4-Dichlorophenoxyacetic acid, including salts and esters | 94757 |
| DDE (1,1-Dichloro-2,2-bis(p-chlorophenyl)ethylene | 72559 |
| Diazomethane | 334883 |
| Dibenzofuran | 132649 |
| 1,2-Dibromo-3-chloropropane | 96128 |
| Dibutylphthalate | 84742 |
| 1,4-Dichlorobenzene | 106467 |
| 3,3’-Dichlorobenzidine | 91941 |
| Dichloroethyl ether (Bis(2-chloroethyl)ether) | 111444 |
| 1,3-Dichloropropene | 542756 |
| Diethanolamine | 111422 |
| N,N-Dimethylaniline | 121697 |
| Diethyl sulfate | 64675 |
| 3,3’-Dimethoxybenzidine | 119904 |
| 4-Dimethylaminoazobenzene | 60117 |
| 3,3’-Dimethylbenzidine | 119937 |
| Dimethylcarbamoyl chloride | 79447 |
| N,N-Dimethylformamide | 68122 |
| 1,1-Dimethylhydrazine | 57147 |
| Dimethyl phthalate | 131113 |
| Dimethyl sulfate | 77781 |
| 4,6-Dinitro-o-cresol, and salts | |
| 2,4-Dinitrophenol | 51285 |
| 2,4-Dinitrotoluene | 121142 |
| 1,4-Dioxane (1,4-Diethyleneoxide) | 123911 |
| 1,2-Diphenylhydrazine | 122667 |
| Epichlorohydrin (1-Chloro-2,3-epoxypropane) | 106898 |
| 1,2-Epoxybutane | 106887 |
| Ethyl acrylate | 140885 |
| Ethylbenzene | 100414 |
| Ethyl carbamate (Urethane) | 51796 |
| Ethyl chloride (Chloroethane) | 75003 |
| Ethylene dibromide (Dibromoethane) | 106934 |
| Ethylene dichloride (1,2-Dichloroethane) | 107062 |
| Ethylene glycol | 107211 |
| Ethylene oxide | 75218 |
| Ethylenethiourea | 96457 |
| Ethylidene dichloride (1,1-Dichloroethane) | 75343 |
| Formaldehyde | 50000 |
| Glycol ethers | 0 |
| Hexachlorobenzene | 118741 |
| Hexachloro-1,3-butadiene | 87683 |
| Hexachloroethane | 67721 |
| Hexamethylene-1,6-diisocyanate | 822060 |
| Hexamethylphosphoramide | 680319 |
| Hexane | 110543 |
| Hydrazine | 302012 |
| Hydroquinone | 123319 |
| Isophorone | 78591 |
| Maleic anhydride | 108316 |
| Methanol | 67561 |
| Methyl bromide (Bromomethane) | 74839 |
| Methyl chloride (Chloromethane) | 74873 |
| Methyl chloroform (1,1,1-Trichloroethane) | 71556 |
| Methyl ethyl ketone (2-Butanone) | 78933 |
| Methylhydrazine | 60344 |
| Methyl iodide (lodomethane) | 74884 |
| Methyl isobutyl ketone (Hexone) | 108101 |
| Methyl isocyanate | 624839 |
| Methyl methacrylate | 80626 |
| Methyl tert-butyl ether | 1634044 |
| 4,4’-Methylenebis(2-chloroaniline) | 101144 |
| Methylene chloride (Dichloromethane) | 75092 |
| 4,4’Methylenediphenyl diisocyanate (MDI) | 101688 |
| 4,4’-Methylenedianiline | 101779 |
| Naphthalene | 91203 |
| Nitrobenzene | 98953 |
| 4-Nitrobiphenyl | 92933 |
| 4-Nitrophenol | 100027 |
| 2-Nitropropane | 79469 |
| N-Nitroso-N-methylurea | 684935 |
| N-Nitrosodimethylamine | 62759 |
| N-Nitrosomorpholine | 59892 |
| Phenol | 108952 |
| p-Phenylenediamine | 106503 |
| Phosgene | 75445 |
| Phthalic anhydride | 85449 |
| Polychlorinated biphenyls (Aroclors) | 1336363 |
| Polycyclic Organic Matterb | 0 |
| 1,3-Propane sultone | 1120714 |
| beta-Propiolactone | 57578 |
| Propionaldehyde | 123386 |
| Propoxur (Baygon) | 114261 |
| Propylene dichloride (1,2-Dichloropropane) | 78875 |
| Propylene oxide | 75569 |
| 1,2-Propylenimine (2-Methyl aziridine) | 75558 |
| Quinone | 106514 |
| Styrene | 100425 |
| Styrene oxide | 96093 |
| 2,3,7,8-Tetrachlorodibenzo-p-dioxin | 1746016 |
| 1,1,2,2-Tetrachloroethane | 79345 |
| Tetrachloroethylene (Perchloroethylene) | 127184 |
| Toluene | 108883 |
| 2,4,-Toluenediamine | 95807 |
| Toluene-2,4-diisocyanate | 584849 |
| o-Toluidine | 95534 |
| 1,2,4-Trichlorobenzene | 120821 |
| 1,1,2-Trichloroethane | 79005 |
| Trichloroethylene | 79016 |
| 2,4,5-Trichlorophenol | 95954 |
| 2,4,6-Trichlorophenol | 88062 |
| Triethylamine | 121448 |
| Trifluralin | 1582098 |
| 2,2,4-Trimethylpentane | 540841 |
| Vinyl acetate | 108054 |
| Vinyl bromide | 593602 |
| Vinyl chloride | 75014 |
| Vinylidene chloride (1,1,-Dichloroethylene) | 75354 |
| Xylenes (isomers and mixture) | 1330207 |
| o-Xylene | 95476 |
| m-Xylene | 108383 |
| p-Xylene | 106523 |
| a Includes mono- and di-ethers of ethylene glycol, diethylene glycols and triethylene glycol; R-(OCH2CH2)RR-OR where:n = 1,2, or 3,R = alkyl or aryl groupsR’ = R, H, or groups which, when removed, yield glycol ethers with the structure: R-(OCH2CH2)n – OH. Polymers are excluded from the glycol category. | |
| b Includes organic compounds with more than one benzene ring, and which have a boiling point greater than or equal to 100°C. |
| Chemical Name | CAS No. |
| 4-Aminobiphenyl | 92671 |
| Styrene oxide | 96093 |
| Diethyl sulfate | 64675 |
| N-Nitrosomorpholine | 59892 |
| Dimethyl formamide | 68122 |
| Hexamethylphosphoramide | 680319 |
| Acetamide | 60355 |
| 4,4'-Methylenedianiline | 101779 |
| o-Anisidine | 90040 |
| 2,3,7,8-Tetrachlorodibenzo-p-dioxin | 1746016 |
| Beryllium salts | - |
| Benzidine | 92875 |
| N-Nitroso-N-methylurea | 684935 |
| Bis(chloromethyl)ether | 542881 |
| Dimethyl carbamoyl chloride | 79447 |
| Chromium compounds (hexavalent) | - |
| 1,2-Propylenimine (2-Methyl aziridine) | 75558 |
| Arsenic and inorganic arsenic compounds | 99999904 |
| Hydrazine | 302012 |
| 1,1-Dimethyl hydrazine | 57147 |
| Beryllium compounds | 7440417 |
| 1,2-Dibromo-3-chloropropane | 96128 |
| N-Nitrosodimethylamine | 62759 |
| Cadmium compounds | - |
| Benzo (a) pyrene | 50328 |
| Polychlorinated biphenyls (Aroclors) | 1336363 |
| Heptachlor | 76448 |
| 3,3'-Dimethyl benzidine | 119937 |
| Nickel subsulfide | 12035722 |
| Acrylamide | 79061 |
| Hexachlorobenzene | 118741 |
| Chlordane | 57749 |
| 1,3-Propane sultone | 1120714 |
| 1,3-Butadiene | 106990 |
| Nickel refinery dust | - |
| 2-Acetylaminoflourine | 53963 |
| 3,3'-Dichlorobenzidine | 53963 |
| Lindane (hexachlorcyclohexane, gamma) | 58899 |
| 2,4-Toluene diamine | 95807 |
| Dichloroethyl ether (Bis(2-chloroethyl)ether) | 111444 |
| 1,2 - Diphenylhydrazine | 122667 |
| Toxaphene (chlorinated camphene) | 8001352 |
| 2,4-Dinitrotoluene | 121142 |
| 3,3'-Dimethoxybenzidine | 119904 |
| Formaldehyde | 50000 |
| 4,4'-Methylene bis(2-chloroaniline)Acrylonitrile | 101144 107131 |
| Ethylene dibromide(1,2-Dibromoethane) | 106934 |
| DDE (1,1-p-chlorophenyl 1-2 dichloroethylene) | 72559 |
| Chlorobenzilate | 510156 |
| Dichlorvos | 62737 |
| Vinyl chloride | 75014 |
| Coke Oven Emissions | 99999908 |
| Ethylene oxide | 75218 |
| Ethylene thiourea | 96457 |
| Vinyl bromide (bromoethene) | 593602 |
| Selenium sulfide (mono and di) | 7488564 |
| Chloroform | 67663 |
| Pentachlorophenol | 87865 |
| Ethyl carbamate (Urethane) | 51796 |
| Ethylene dichloride (1,2-Dichloroethane) | 107062 |
| Propylene dichloride (1,2-Dichloropropane) | 78875 |
| Carbon tetrachloride | 56235 |
| Benzene | 71432 |
| Methyl hydrazine | 60344 |
| Ethyl acrylate | 140885 |
| Propylene oxide | 75569 |
| Aniline | 62533 |
| 1,4-Dichlorobenzene(p) | 106467 |
| 2,4,6-Trichlorophenol | 88062 |
| Bis(2-ethylhexyl)phthalate (DEHP) | 117817 |
| o-Toluidine | 95534 |
| Propoxur | 114261 |
| Trichloroethylene | 79016 |
| 1,4-Dioxane (1,4-Diethyleneoxide) | 123911 |
| Acetaldehyde | 75070 |
| Bromoform | 75252 |
| Captan | 133062 |
| Epichlorohydrin | 106898 |
| Methylene chloride (Dichloromethane) | 75092 |
| Tetrachloroethylene (Perchloroethylene) | 127184 |
| Dibenz (ah) anthracene | 53703 |
| Chrysene | 218019 |
| Dimethyl aminoazobenzene | 60117 |
| Benzo (a) anthracene | 56553 |
| Benzo (b) fluoranthene | 205992 |
| Antimony trioxide | 1309644 |
| 2-Nitropropane | 79469 |
| 1,3-Dichloropropene | 542756 |
| 7, 12-Dimethylbenz(a)anthracene | 57976 |
| Benz(c)acridine | 225514 |
| Indeno(1,2,3-cd)pyrene | 193395 |
| 1,2:7,8-Dibenzopyrene | 189559 |
| Solvents containing these pollutants in concentrations less than or equal to 0.1% may be used. |