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The Federal Register

ENVIRONMENTAL PROTECTION AGENCY

U.S. Customs and Border Protection

CFR Citation: 40 CFR Part 63

EPA ID: [EPA-HQ-OAR-2005-0526; FRL-8466-6]

RIN ID: RIN 2060-AN21

NOTICE: Part II

DOCUMENT ACTION: Proposed rule.

SUBJECT CATEGORY: National Emission Standards for Hazardous Air Pollutants: Paint Stripping and Miscellaneous Surface Coating Operations at Area Sources

DATES: Comments. Comments must be received on or before October 17, 2007. Under the Paperwork Reduction Act, comments on the information collection provisions must be received by the Office of Management and Budget (OMB) on or before October 17, 2007.

Public Hearing: If anyone contacts EPA requesting to speak at a public hearing concerning the proposed rule by September 27, 2007, we will hold a public hearing on October 2, 2007.

DOCUMENT SUMMARY: In this action, EPA proposes national emission standards for hazardous air pollutants (NESHAP) for area sources engaged in paint stripping and miscellaneous surface coating operations. EPA has listed ``Paint Stripping,'' ``Plastic Parts and Products (Surface Coating),'' and ``Autobody Refinishing Paint Shops'' as area sources of hazardous air pollutants (HAP) that contribute to the risk to public health in urban areas under the Integrated Urban Air Toxics Strategy. These three source categories are being combined into one set of standards for the purposes of this rulemaking. Paint stripping operations subject to the standards being proposed include the use of methylene chloride containing chemicals to remove paint and other coatings. Plastic parts and products surface coating operations include the application of coatings to miscellaneous parts and/or products made of metal or plastic, or combinations of metal and plastic. Autobody refinishing includes the application of coating to motor vehicles and mobile equipment. These proposed standards, when final, would require all methylene chloride (MeCl) containing paint stripping and miscellaneous surface coating operations at area sources to comply with equipment requirements and/or management practices that minimize specific HAP emissions. The standards would also establish training requirements for persons who spray apply coatings. These standards, when final, would apply to all area sources that perform methylene chloridecontaining paint stripping and miscellaneous surface coating activities, except when other NESHAP apply.

SUMMARY: Environmental Protection Agency,


SUPPLEMENTAL INFORMATION

I. General Information

A. How is this document organized?

The information presented in this preamble is organized as follows: I. General Information

A. How is this document organized?

B. Does this action apply to me?

C. What should I consider as I prepare my comments to EPA? II. Background Information for Proposed Area Source Standards

A. What is the regulatory development background for the proposed standards for paint stripping and miscellaneous surface coating operations?

B. Where in the Code of Federal Regulations (CFR) will these standards be codified?

C. What criteria are used in the development of these NESHAP?

D. What are the sources of emissions and the HAP for which these area source categories were listed?

E. What are the health effects associated with the pollutants emitted by paint stripping and miscellaneous surface coating operations?

F. How has EPA regulated major sources in the same industrial sectors (similar sources) and what has EPA learned about available control technologies and management practices from regulating these major sources?
III. Proposed NESHAP for Paint Stripping and Miscellaneous Coating Operations at Area Sources

A. What are the affected area sources?

B. What are the HAP and primary sources of emissions for which these source categories were listed?

C. Do the proposed standards apply to my source?

D. What emissions control requirements is EPA proposing?

E. What are the initial compliance requirements?

F. What are the continuous compliance requirements?

G. What are the notification, recordkeeping, and reporting requirements?

IV. Rationale for Selecting the Proposed Standards

A. What area source categories are affected by this proposal?

B. How did we select the affected source?

C. How did we determine the basis and level of the proposed standards for new and existing sources?

D. How did we select the format of the proposed standards?

E. How did we select the initial compliance and testing requirements?

F. How did we select the continuous compliance requirements?

G. How did we select the compliance date?

H. How did we decide to exempt these area source categories from the CAA title V permit requirements?
V. Impacts of the Proposed Standards

A. What are the air impacts?

B. What are the cost impacts?

C. What are the economic impacts?

D. What are the nonair health, environmental, and energy impacts?

VI. Statutory and Executive Order Reviews

A. Executive Order 12866: Regulatory Planning and Review

B. Paperwork Reduction Act

C. Regulatory Flexibility Act

D. Unfunded Mandates Reform Act

E. Executive Order 13132: Federalism

F. Executive Order 13175: Consultation and Coordination With Indian Tribal Governments

G. Executive Order 13045: Protection of Children From Environmental Health and Safety Risks

H. Executive Order 13211: Actions Concerning Regulations That Significantly Affect Energy Supply, Distribution, or Use

I. National Technology Transfer and Advancement Act

J. Executive Order 12898: Federal Actions To Address Environmental Justice in Minority Populations and LowIncome Populations

B. Does this action apply to me?

Categories and entities potentially affected by the proposed rule are MeClcontaining paint stripping operations and miscellaneous surface coating operations located at area sources. An area source is defined in CAA section 112(a) as any stationary source of HAP that is not a major source, and a major source is defined as any stationary source or group of stationary sources located within a contiguous area and under common control that emits, or has the potential to emit, considering controls, in the aggregate, 10 tons per year (tpy) of any single HAP or 25 tpy of any combination of HAP. For the purposes of this proposal, paint stripping operations are those that involve the use of MeCl for the partial or complete removal of surface coatings from wood, metal or plastic substrates at area sources as either (1) an independent activity where paint stripping is the principle activity at the source or (2) an activity incidental to the principle activity (e.g., surface coating, inspection, maintenance, etc.) at the source. We consider paint stripping activities that use less than 150 gallons per year to be incidental to the principle activity and those using 150 gallons or more to be performing paint stripping as a principle activity. Miscellaneous surface coating operations are those that involve the application of coatings at area sources to (1) miscellaneous parts and/or products made of metal or plastic, or combinations of metal and plastic; or (2) motor vehicles and mobile equipment (e.g., heavy dutytrucks, buses, construction equipment, selfpropelled vehicles and equipment that may be drawn and/or driven on a roadway), hereinafter referred to as autobody refinishing. In general, the facilities and entities potentially affected by the proposed rule are covered under the North American Industrial Classification System (NAICS) Codes listed in the following table. However, facilities classified under other NAICS codes may be subject to the proposed standards if they meet the applicability criteria. Examples of potentially Category NAICS regulated entities Aerospace Equipment............ 336413 Aircraft engines, aircraft 336414 parts, aerospace ground 336415 equipment.
54171
[[Page 52960]]
Automobiles and Automobile 335312 Engine parts, vehicle parts Parts. 336111 and accessories, brakes, 336211 axles, etc. Motor vehicle 336312 body manufacturing and 33632 automobile assembly plants. 33633 New and used car dealers. 33634 Automotive body, paint, and 33637 interior repair and 336399 maintenance.
441110
441120
811121
Chemical Manufacturing and 325110 Petrochemicals, Industrial Product Preparation. 325120 Gases, Inorganic Dyes and 325131 Pigments, Basic Inorganic 325188 and Organic Chemicals, 325192 Cyclic Crude and 325193 Intermediates, Ethyl 325199 Alcohol, Miscellaneous 325998 Chemical Production and Preparation.
Extruded Aluminum.............. 331316 Extruded aluminum, 331524 architectural components, 332321 coils, rod, and tubes. 332323
Government..................... N/A Government entities, besides Department of Defense, that maintain vehicles, such as school buses, police and emergency vehicles, transit buses, or highway maintenance vehicles. Heavy Equipment................ 33312 Tractors, earth moving 333611 machinery.
333618
Job Shops...................... 332312 Manufacturing industries not 332722 elsewhere classified (e.g., 332813 bezels, consoles, panels, 332991 lenses).
332999
334119
336413
339999
Large Trucks and Buses......... 33612 Large trucks and buses. 336211
Metal Buildings................ 332311 Prefabricated metal buildings, carports, docks, dwellings, greenhouses, panels for buildings. Metal Containers............... 33242 Drums, kegs, pails, shipping 81131 containers.
322214
331513
332439
Metal Pipe and Foundry......... 331111 Plate, tube, rods, nails, 331513 etc.
33121
331221
331511
Rail Transportation............ 33651 Brakes, engines, freight 336611 cars, locomotives. 482111
Recreational Vehicles and Other 321991 Mobile Homes. Motorcycles, Transportation Equipment. 3369 motor homes, semi trailers, 331316 truck trailers. 336991 Miscellaneous
336211 transportation related 336112 equipment and parts. Travel 336212 trailer and camper 336213 manufacturing. 336214
336399
336999
33635
56121
8111
56211
[[Page 52961]]
RubbertoMetal Products....... 326291 Engine mounts, rubberized 326299 tank tread, harmonic balancers.
Structural Steel............... 332311 Joists, railway bridge 332312 sections, highway bridge sections.
Waste Treatment, Disposal, and 562211 Hazardous Waste Treatment Materials Recovery. 562212 and Disposal, Solid Waste 562213 Landfill, Solid Waste 562219 Combustors and 562920 Incinerators, Other Nonhazardous Waste Treatment and Disposal, Materials Recovery. Other Industrial and Commercial 211112 Natural Gas Liquid Extraction.
311942 Spices and Extracts. 331311 Alumina Refining. 337214 Office furniture, except 811420 wood.
Reupholstery and Furniture Repair.
325211 Plastics Material Synthetic Resins, and Nonvulcanizable Elastomers.
325510 Paint and Coating Manufacturing. 32614, Plastic foam products (e.g., 32615 pool floats, wrestling mats, life jackets). 326199 Plastic products not elsewhere classified (e.g., name plates, coin holders, storage boxes, license plate housings, cosmetic caps, cup holders). 333313 Office machines. 33422 Radio and television broadcasting and communications equipment (e.g., cellular telephones).
339111, Medical equipment and 339112 supplies.
33992 Sporting and athletic goods. 33995 Signs and advertising specialties.
336612 Boat building.
713930 Marinas, including boat repair yards.

This table is not intended to be exhaustive, but rather provides a guide for readers regarding entities likely to be regulated by the proposed rule. Many types of entities that perform stripping and/or coating that are not listed in this table would be potentially affected by the proposed rule. To determine whether your facility, company, business, organization, etc., is subject to this action, you should examine the applicability criteria in section 63.11170 of the proposed rule. If you have any questions regarding the applicability of this action to a particular entity, consult the person listed in the preceding FOR FURTHER INFORMATION CONTACT section.

C. What should I consider as I prepare my comments to EPA?

Do not submit information containing CBI to EPA through http://www.regulations.gov, or email. Clearly mark the part or all of the information that you claim to be CBI. For CBI information in a disk or CDROM that you mail to EPA, mark the outside of the disk or CDROM as CBI and then identify electronically within the disk or CDROM the specific information that is claimed as CBI. In addition to one complete version of the comment that includes information claimed as CBI, a copy of the comment that does not contain the information claimed as CBI must be submitted for inclusion in the public docket. Information so marked will not be disclosed except in accordance with procedures set forth in 40 CFR part 2.

When submitting comments, remember to:

1. Identify the rulemaking by docket number and other identifying information (e.g., subject heading, Federal Register proposal publication date and reference page number(s)).

2. Follow directionsEPA may ask you to respond to specific questions.

3. Explain why you agree or disagree; suggest alternatives and provide substitute language for your requested changes.

4. Describe any assumptions and provide any technical information and/or data that you used.

5. If you estimate potential costs or burdens, explain how you arrived at your estimate in sufficient detail to allow for it to be reproduced.

6. Provide specific examples to illustrate your concerns, and suggest alternatives.

7. Explain your views as clearly as possible, avoiding the use of profanity or personal threats.

8. Make sure to submit your comments by the specified comment period deadline.
II. Background Information for Proposed Area Source Standards A. What is the regulatory development background for the proposed standards for paint stripping and miscellaneous surface coating operations?

Section 112 of the Clean Air Act (CAA) requires EPA to develop NESHAP for both major and area sources that are listed for regulation under CAA section 112(c). As stated earlier, a major source is defined in CAA section 112(a) as any stationary source or group of stationary sources located within a contiguous area and under common control that emits, or has the potential to emit, considering controls, in the aggregate, 10 tons per year (tpy) of any single HAP or 25 tpy of any combination of HAP. An area source is any stationary source that is not a major source. Thus, area sources are those sources of HAP that do not emit nor have the potential to emit HAP at or above the 10 or 25 tpy thresholds.

CAA section 112(k)(3)(B) requires EPA to develop a list of at least 30 HAP which, as a result of area source emissions, pose the greatest threat to public health in the largest number of urban areas. We refer to these HAP as the ``urban HAP.'' Section 112(c)(3) of the CAA directs EPA to identify source categories or subcategories of area
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sources that represent 90 percent of the emissions of the urban HAP.

On July 19, 1999, EPA published its Integrated Urban Air Toxics Strategy, which included both the list of urban HAP and the initial list of area source categories (64 FR 38706). The initial list of area source categories included ``Paint Stripping Operations''. On June 26, 2002 and November 22, 2002, EPA added ``Autobody Refinishing Paint Shops (67 FR 43112)'' and ``Plastic Parts and Products (Surface Coating) (67 FR 70427)'', respectively, to the list of area source categories. A primary goal of the Integrated Urban Air Toxics Strategy is to achieve a 75 percent reduction in cancer incidence attributable to HAP emitted from stationary sources in urban areas.

Sierra Club sued EPA, alleging a failure to complete standards for the area source categories listed pursuant to CAA section 112(c)(3)and (k)(3)(B) within the timeframe specified by the statute. See Sierra Club v. Johnson, No. 011537, (D.D.C.). On March 31, 2006, the court issued an order requiring EPA to promulgate standards under CAA section 112(d) for those area source categories listed pursuant to CAA section 112(c)(3) and (k)(3)(B). Among other things, the order requires that, by December 15, 2007, EPA complete standards for certain area source categories.

In this action, EPA is proposing standards for the following area source categories: Paint stripping, plastic parts and products (surface coating), and autobody refinishing. In developing this proposed rule, we fully analyzed these three listed source categories and found that it is both reasonable and technically feasible to regulate emissions from these three source categories by a single set of emission standards. The processes, emission points, emission characteristics, and emission controls for plastic parts and products surface coating and autobody refinishing are very similar. Additionally, paint stripping is often performed as part of the surface preparation for both plastic parts and autobody refinishing which, by regulating within the scope of a single set of standards, reduces the burden of complying with multiple standards on the sources performing both the paint stripping and subsequent coating. This single set of emission standards that addresses all three categories also minimizes the cost of developing, permitting, and enforcing the standards. For purposes of this preamble and proposed rule, the term ``paint stripping and miscellaneous surface coating'' is used to indicate that the three area source categories of paint stripping, plastic parts and products (surface coating), and autobody refinishing have been treated as a single source category for purposes of developing this rule.

Early in the development of standards to implement EPA's Integrated Urban Strategy, the States expressed concern over the burden and resources that would be required for the States to take delegation for the implementation of the area source rules listed as part of the strategy. Specifically, States were concerned that implementing Federal requirements, in lieu of established State programs, would be overly burdensome with little or no additional emission reductions for certain source categories. In these discussions, the States acknowledged the provisions in CAA section 112(l) as a route for providing them this reduction of burden and flexibility in accepting delegation of some of the area source standards. Guidance on the provisions of CAA section 112(l) are presented in 40 CFR 63 Subpart E which provides certain administrative (i.e., monitoring, recordkeeping, and reporting) criteria for an alternative program to be considered equivalent. This guidance provides States with information regarding the necessary components for their program to be considered equivalent. EPA believes some States may have programs that address the emissions from the surface coating of motor vehicles and mobile equipment that are at least as effective as the proposed standards and encourages States to consider utilizing these provisions in lieu of implementing the proposed standards.

The EPA is seeking comment on (1) whether or not the States are interested in utilizing the Section 112(l) alternative program approach, and (2) what technical assistance the States may need to develop equivalency determinations.
B. Where in the Code of Federal Regulations (CFR) will these standards be codified?

The CFR is a codification of the general and permanent rules published in the Federal Register by the Executive departments and agencies of the Federal Government. The code is divided into 50 titles that represent broad areas subject to Federal Regulation. When final, these proposed standards will be published in Title 40, Protection of the Environment, part 63, subpart HHHHHH: National Emission Standards for Hazardous Air Pollutants: Paint Stripping and Miscellaneous Surface Coating Operations.
C. What criteria are used in the development of these NESHAP?

CAA section 112(d)(5) authorizes EPA to issue alternative emission standards for area sources in lieu of the authorities provided in CAA sections 112(d)(2) and 112(f). Specifically, section 112(d)(5), which is entitled ``Alternative Standard for Area Sources,'' provides:

With respect only to categories and subcategories of area sources listed pursuant to subsection (c) of this section, the Administrator may, in lieu of the authorities provided in paragraph (2) and subsection (f) of this section, elect to promulgate standards or requirements applicable to sources in such categories or subcategories which provide for the use of generally available control technologies or management practices by such sources to reduce emissions of hazardous air pollutants.

Thus, CAA section 112(d)(5) authorizes EPA to promulgate standards under section 112(d)(5) that provide for the use of generally available control technologies or management practices (GACT), instead of issuing maximum achievable control technology (MACT) standards pursuant to CAA section 112(d)(2) and (d)(3). The statute does not set any condition precedent for issuing standards under CAA section 112(d)(5) other than that the area source category or subcategory at issue must be one that EPA listed pursuant to CAA section 112(c)(3), which is the case in this proposal.

When setting a GACT standard for an area source category as opposed to a MACT standard, EPA must ensure that the GACT standard is consistent with the requirements of CAA section 112(d)(5) and have a reasonable basis for its GACT determination. Thus, in developing standards for area sources of HAP emissions, EPA evaluates the control technologies and management practices that reduce HAP emissions that are generally available for each area source category, and, in determining GACT, may establish standards on either (or both) generally available control technologies or (and) management practices that reduce the emission of HAP. EPA's analysis supporting the proposed GACT requirements is discussed in detail in section IV of this preamble. D. What are the sources of emissions and the HAP for which these area source categories were listed?

EPA listed the area source paint stripping category pursuant to CAA section 112(c)(3) based on emissions of MeCl contained in paint stripper formulations. The emissions of MeCl comes from evaporative losses during the use or storage of MeCl. EPA listed
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the area source miscellaneous coating operations category pursuant to section 112(c)(3) based on emissions of cadmium, chromium, lead compounds (lead), manganese and nickel compounds that are in the coatings, as part of the pigment in topcoats or for the corrosion protection in primers. For purposes of this proposal we will refer to these HAP as the ``target HAP.''

The anticipated national impacts of these proposed standards is summarized in section V of this preamble.
E. What are the health effects associated with the pollutants emitted by paint stripping and miscellaneous surface coating operations?

Emissions data collected in the development of this proposed rule shows that HAP emitted from paint stripping and miscellaneous surface coating operations are associated with a variety of adverse health effects. These adverse health effects include chronic health disorders (e.g., central nervous system effects, blood disorders, cancer) and acute health disorders (e.g., irritation of eyes, nose and throat, with longterm impairment of lung function possible at high acute exposures). The proposed rule protects air quality and promotes the public health by reducing the emissions of the HAP for which the three source categories at issue in this proposed rule were listed. F. How has EPA regulated major sources in the same industrial sectors (similar sources) and what has EPA learned about available control technologies and management practices from regulating these major sources?

Major sources performing paint stripping and surface coating of miscellaneous parts and/or products made of metal or plastic, or combinations of metal and plastic; or motor vehicles and mobile equipment (e.g., heavy dutytrucks, buses, construction equipment, selfpropelled vehicles and equipment that may be drawn and/or driven on a roadway), were addressed in different surface coating NESHAP requiring MACT level of control, of which the last NESHAP was promulgated in 2004. Major sources must currently be in compliance with those surface coating NESHAP.

Paint stripping was a separately listed major source category under CAA section 112 (c)(1), however, during the data gathering phase EPA determined that there were no major source paint stripping operations conducted independent of surface coating. Therefore, all paint stripping operations were covered in each surface coating NESHAP, as part of the cleaning material used for surface preparation activities. Each NESHAP assumed that the initial emission control technology would be reduction of the usage of HAP cleaners or implementation of management practices to reduce the evaporative losses from these cleaning activities.

The data gathering for the major source categories revealed that when the coatings are sprayapplied, it was common practice to perform application of the coatings within the confines of a spray booth to minimize worker exposure. This limited the dispersion of the HAP to the parts being coated as solids in the dry coating film, deposition onto the walls, floor, and grates of the spray booths in which they are applied, or some of the HAP particles would be entrained in the spray booth exhaust air. We have learned, as part of the data gathering phase of this area source proposal that although most, if not all, sources are spray applying these coatings in a spray booth, not all of the spray booths are capable of capturing and controlling the target HAP (the HAP for which the area source categories at issue here were listed pursuant to CAA section 112(c)(3).
III. Proposed NESHAP for Paint Stripping and Miscellaneous Coating Operations at Area Sources

A. What are the affected area sources?

The sources that would be affected by the proposed standards are area sources engaged in paint stripping using MeCl, and/or engaged in coating of miscellaneous parts and/or products made of metal or plastic, or combinations of metal and plastic, or autobody refinishing. The proposed standards would not apply to any of these operations that are specifically covered under another area source NESHAP (e.g., the NESHAP for Defense Land Systems and Miscellaneous Equipment currently under development). While these sources are not currently listed pursuant to CAA section 112(c)(3) or 112(k)(3)(b), we intend to list them under these provisions of the act.
B. What are the HAP and primary sources of emissions for which these source categories were listed?

Paint Stripping Operations

The primary source of emissions from paint stripping operations and the HAP for which this source category was listed pursuant to CAA section 112(c)(3) (the ``target HAP'') is the MeCl contained in paint stripper formulations. The primary source of the MeCl emissions in this source category comes from evaporative losses during the use or storage of MeCl.

Miscellaneous Coating Operations

The primary sources of emissions from miscellaneous coating operations are the metal pigments that are in the coatings and/or refinish material. The target HAP for which these source categories were listed are the heavy metals including cadmium, chromium, lead, manganese and nickel compounds. The primary source of emissions of these HAP are the spray application of the coatings and curing process.

The heavy metals are contained primarily in the coatings (e.g., primers and the pigments in topcoats) and include compounds of lead (Pb), trivalent chromium (CrIII), or hexavalent chromium (CrVI), plus compounds of other metals that are considered HAP, such as cadmium, manganese, and nickel. The metal HAP compounds are emitted as the coatings are atomized during spray application. A substantial fraction of coating that is atomized does not reach the part and becomes what is termed ``overspray.'' The fraction that becomes overspray depends on many variables, but two of the most important are the type of equipment and the skill of the painter. Some overspray lands on surfaces of the spray booth and the masking paper that is usually placed around the surface being sprayed, but the rest of the overspray is drawn into the spray booth exhaust system. If the spray booth has filters, most of the overspray is captured by the filters; otherwise, it is exhausted to the atmosphere.

After coating application, the spray gun must be cleaned to remove the remaining coating before it cures and to prepare it for the next coating job. Solvents used for equipment cleaning may contain the same HAP as the coatings they remove. Spray guns are usually cleaned in a device, commonly referred to as an enclosed spray gun washer, that consists of a solvent reservoir and a covered enclosure that dispenses solvent for gun cleaning. The enclosure may hold the gun for automated gun cleaning. During gun cleaning, HAP from the cleaning solvent and the coating may be emitted as the cleaning solvent is sprayed through the gun during cleaning from the equipment that stores and dispenses the cleaning solvent while it is opened.

C. Do the proposed standards apply to my source?

The area source requirements specified in the proposed rule would apply to your source if your source (or
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facility) is an area source that performs (1) paint stripping using MeClcontaining chemicals or (2) surface coating using spray equipment.

The area source requirements specified in the proposed rule would not apply if your paint stripping or surface coating operations meet any of the following:

  • Paint stripping or surface coating performed onsite at installations owned or operated by the Armed Forces of the United States (including the Coast Guard and the National Guard of any such State), or the National Aeronautics and Space Administration because these activities will be subject to the area source NESHAP for military operations which is in development.
  • Paint stripping or surface coating of military munitions manufactured by or for the Armed Forces of the United States (including the Coast Guard and the National Guard of any such State) or equipment directly and exclusively used for the purposes of transporting munitions manufactured by or for the Armed Forces of the United States (including the Coast Guard and the National Guard of any such State) because these activities will be subject to the area source NESHAP for military operations which is in development.

    D. What emissions control requirements is EPA proposing?

    This section describes the proposed emissions control requirements for paint stripping and miscellaneous coating operations. The basis for these proposed requirements is discussed in section IV, below. Paint Stripping Operations

    All sources conducting paint stripping involving the use of MeCl must implement management practice standards that reduce emissions of MeCl by minimizing evaporative losses of MeCl.

    In addition to the management practices, sources that use 150 gal or more of paint stripper containing MeCl, per year would need to develop and implement a MeCl minimization plan consisting of a written plan with the criteria to evaluate the necessity of MeCl in the stripping operations and management techniques to minimize MeCl emissions when it is needed in the paint stripping operation.

    The MeCl minimization plan evaluation criteria would involve only using a MeClcontaining paint stripper when an alternative onsite stripping method or material is incapable of accomplishing the work as determined by the operator. Alternative methods to reduce MeCl usage may include: (1) NonMeClcontaining chemical strippers; (2) mechanical stripping; (3) blasting (including dry or wet media); or (4) thermal and cryogenic decomposition.

    The management practices that would be required to be contained in the plan include optimizing stripper application conditions, reducing exposure of stripper to the air, and practicing proper storage and disposal of materials containing MeCl. Sources would be required to submit the plan either to EPA or to the delegated state permit authority, keep a written copy of the plan on site and post a placard or sign outlining the evaluation criteria and management techniques in each area where MeClcontaining paint stripping operations occur. Miscellaneous Coating Operations

    All sources conducting surface coating operations involving spray applied coatings would need to apply the coatings with a high volume, low pressure (HVLP) spray gun, electrostatic spray gun, or a gun demonstrated to be equal in transfer efficiency to an HVLP spray gun. All sprayapplied coatings would need to be applied in a prep station or spray booth, with a full roof and at least three complete walls or complete side curtains, ventilated so that air is drawn into the booth. The exhaust from the prep station or spray booth would need to be fitted with fiberglass or polyester fiber filters or some other filter technology demonstrated to achieve at least 98 percent capture efficiency of paint overspray. As explained further below, we are proposing that the combination of these technologies are GACT for the miscellaneous surface coating operations.

    Additionally, sources would be required to comply with the management practices by demonstrating that (1) all painters that spray apply coatings are certified and (2) that all spray gun cleaning performed by spraying HAP solvent through the gun is performed in an enclosed spray gun cleaner or by cleaning the disassembled gun parts by hand (i.e., spraying HAP solvent through a gun outside of a gun cleaner would be prohibited). The painter would need to be certified as having completed classroom and handson training in the proper selection, mixing, and application of coatings. Refresher training would need to be repeated at least once every 5 years. The initial and refresher training would need to address the following topics:

  • Surface preparation (prep).
  • Spray gun set up and operation and spray technique for different types of coatings to improve transfer efficiency and minimize coating usage and overspray.
  • Routine spray booth and filter maintenance.
  • Paint mixing, matching, and applying.
  • Resolving paint application problems.
  • Finish defects causes and cures.
  • Safety precautions.
  • Environmental compliance.

    E. What are the initial compliance requirements?

    If your facility is a new source (one that began construction or reconstruction after the date this rule is proposed) and you use MeCl in your paint stripping operations or you spray apply coatings, you would be required to comply with all of the requirements established in this subpart as of the date of promulgation of the final rule or upon startup, whichever is later.

    If your facility is an existing source (one that began construction or reconstruction before the date this rule is proposed), you would be required to comply with the requirements no later than 2 years after the date the final rule is published. In addition, each painter would need to comply with the training requirements of the rule no later than 60 days after hiring. Painters would be allowed to use training that was completed within 5 years prior to the date training is required to meet this requirement. All painters would need to receive refresher training and be recertified every 5 years.

    To demonstrate initial compliance for paint stripping operations, you would need to:

  • Certify that you have implemented a best management practices plan, and
  • If you are a source that uses 150 gal or more of paint stripper containing MeCl, per year, certify that you have developed and implemented a MeCl minimization plan consisting of a written plan with the criteria to evaluate the necessity of MeCl in the stripping operations and management techniques to minimize MeCl emissions when it is needed in the paint stripping operation.

    To demonstrate initial compliance for miscellaneous surface coating operations, you would need to:

  • Certify that all coatings are sprayed in booths or prep stations that are fitted with filters.
  • Certify that all spray guns are HVLP or an equivalent.
  • Certify that all painters that apply coatings using a spray gun have completed the training described in section III.D. of this preamble.
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  • Certify that all gun cleaning is performed in enclosed gun cleaners or by hand.

    After the compliance date for your source, you would have 120 days if you are a new source, and 30 days if you are an existing source, to submit a notification of compliance status to the EPA or a delegated State or local air pollution control agency.

    You would also be required to submit an initial notification to the EPA or the delegated agency that you are subject to the standard. You would have 120 days after startup or publication of the final rule (whichever is later) to submit the initial notification if you are a new source. If you are an existing source, you would have 1 year after publication of the final rule to submit the initial notification.

    If your facility is an existing source, you would be required to comply with the requirements no later than 2 years after the date the final rule is published. In addition, each painter would need to comply with the training requirements of the rule no later than 60 days after hiring. Painters would be allowed to use training that was completed within 5 years prior to the date training is required to meet this requirement. All painters would need to receive refresher training and be recertified every 5 years.

    F. What are the continuous compliance requirements?

    To demonstrate continuous compliance, you would need to continually maintain the emission control requirements (i.e., management practices and equipment requirements) that are described in section III.D. of this preamble.
    G. What are the notification, recordkeeping, and reporting requirements?

    You would be required to submit an initial notification to the EPA or the delegated agency that you are subject to the standard. If you are a new source, you would have 120 days after startup or publication of the final rule (whichever is later) to submit the initial notification. If you are an existing source, you would have 1 year after publication of the final rule to submit the initial notification.

    After the compliance date for your source, you would have 120 days if you are a new source and 30 days if you are an existing source to submit a notification of compliance status to the EPA or a delegated State or local air pollution control agency.

    Paint Stripping Operations

    For paint stripping operations, you would need to maintain records demonstrating the following:

  • Annual usage of MeCl in paint strippers is below 150 gallons (if you are a source qualifying for the best management practices, only); or
  • You have complied with the MeCl minimization plan.

    If you are required to have a MeCl minimization plan, you would also be required to submit annual compliance reports in which you certify that the source is in compliance, or report the date, duration, and description of any deviations from the MeCl minimization plan that occurred and the corrective actions taken.

    Miscellaneous Coating Operations

    For miscellaneous coating operations, you would need to maintain records demonstrating the following:

  • All spray painters are trained and certified;
  • Any spray booth filters or particulate controls that are not fiberglass or polyester fiber filters achieve at least 98 percent efficiency; and
  • Any spray guns that do not meet the definition of HVLP or electrostatic spray gun have been demonstrated to achieve comparable transfer efficiency.
  • Spray gun cleaning is being performed manually or in an enclosed gun cleaner when solvent is being atomized through the gun as part of the cleaning process.

    You would also be required to submit annual compliance reports in which you certify that the source is in compliance, or report the date, duration, and description of any deviations from the specified control requirements that occurred and the corrective actions taken. IV. Rationale for Selecting the Proposed Standards
    A. What area source categories are affected by this proposal?

    As discussed above, this rulemaking covers facilities engaged in MeCl paint stripping and spray applied surface coating of parts and/or products made of metal or plastic, or combinations of metal and plastic; and refinishing of motor vehicles and mobile equipment which are a source of emissions of MeCl, cadmium, chromium, lead, manganese and nickel compounds which are the target HAP described above. B. How did we select the affected source?

    In selecting the affected source for emission standards, our primary goal is to ensure that all emission points responsible for the emissions of the target HAP (i.e., MeCl & the heavy metals) in each listed source category are controlled as specified in CAA section 112(d)(5), described previously in Section II.C. The affected source also serves to establish when new source standards should be applied. Specifically, the General Provisions in subpart A of 40 CFR part 63 define the terms ``construction'' and ``reconstruction'' with reference to the term ``affected source'' (40 CFR part 63.2) and provide that new source standards apply when construction or reconstruction of an affected source occurs.

    The affected source for this proposed rule is broadly defined to include all operations associated with the removal of paint from a substrate using MeCl and the spray application of coatings. These operations include the use of MeClcontaining paint strippers by immersion, brushing on, and/or spraying on to remove a coating to change the color of the item or because the life of the coating has been exceeded, or to remove paint for inspection purposes or during repair; storage and mixing of coatings and other materials; surface preparation; coating application and flashoff; drying and curing of applied coatings; cleaning operations; and waste handling operations.

    Each of the equipment items subject to regulation (e.g., containers of paint or stripper, spray booths, spray guns, gun cleaners) is either a relatively low cost item, or could be easily moved about inside a paint stripping and miscellaneous surface coating operation, hence, for this proposal, a broad definition of affected source that encompasses the entire paint stripping and miscellaneous surface coating operation was selected. This approach would subject the entire operation to the same compliance date. Had we proposed a narrow definition for an affected source, replacement or purchase of a single item could cause that item to be considered a new source, resulting in different compliance dates and additional reporting. Furthermore, for the most part, new and existing affected sources are subject to the same emission standards, so the same environmental benefit will be realized regardless of whether the source is considered new or existing. Defining the affected source narrowly could result in
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    a paint stripping or miscellaneous surface coating operation having several affected sources that could be subject to different compliance dates, but the same standards, imposing additional burdens on the source without any environmental benefit.
    C. How did we determine the basis and level of the proposed standards for new and existing sources?

    As previously stated above, CAA section 112(d)(5) authorizes EPA to establish emission standards for area sources that provide for the use of generally available control technologies or management practices that reduce emissions of HAP (GACT). Determining what constitutes GACT involves considering the control technologies and management practices that are generally available to the area sources in the source category. We also consider the standards applicable to major sources in the same industrial sector to determine if the control technologies and management practices are transferable and generally available to area sources. In appropriate circumstances, we may also consider technologies and practices at area and major sources in similar categories to determine whether such technologies and practices could be considered generally available for the area source category at issue. Finally, as noted above, in determining GACT for a particular area source category, we consider the costs and economic impacts of available control technologies and management practices on that category.

    We began the rule development process by identifying other standards developed for these specific processes. As discussed in section II.E., above, we evaluated the emission control technology at major sources for the types of operations found in these area source categories to determine whether or not they were reasonable, feasible, and costeffective for the area sources. Based on the findings of the major source NESHAP data gathering, the technology considered to be appropriate for the target HAP, and the availability of the technology, we considered whether or not these same emission controls were technically feasible and generally available for the area source categories.

    Next, we met with industry associations and discussed their current processes and the feasibility of adopting the emission control technology specified as appropriate for the major sources. We learned that, in fact, similar technology (i.e., spray booths, painter training, HVLP guns, enclosed gun cleaners, and management practices to reduce HAP usage) were already being employed at many of the area sources. Therefore, it was determined that, given the availability and costeffectiveness of these emission control technologies, they represent GACT for the targeted HAP from each source category (i.e., paint stripping, autobody refinishing, and plastic parts surface coating). As previously stated, the target HAP emissions for which these source categories were listed are MeCl from paint stripping operations and cadmium, chromium, lead, manganese and nickel compounds from the coatings operations. The resulting proposed GACT standards are a combination of technology and management practices that control the target HAP, and have a cobenefit of reducing other associated emissions \1\ from these operations. The cobenefit is realized due to the fact that the same technology applied to control the target HAP emissions are also the best techniques for reducing some other emissions associated with these operations.
    \1\ The baseline emissions from the surface coating operations are estimated to be about 38,000 tpy of HAP, including 12.4 tpy of inorganic HAP (e.g.; Pb and CrVI compounds), 123,500 tpy of criteria pollutants including 3,100 tpy of particulate matter (PM) from paint overspray and 120,400 tpy of volatile organic compounds (VOC) from coating and solvent evaporation.

    In the development of these proposed emission standards, EPA visited numerous paint stripping and coating operations, collected data from various databases, and compiled information received during previous data collection activities. We also met with facility owners and other representatives of these industries. These site visits, data review and contacts with industry provided the technical basis for the proposed standards and are included in the public docket for this rulemaking.

    Paint Stripping

    MeCl is the most common solvent and the target HAP for this source category. Since MeCl is the target HAP, our analysis in determining GACT began with understanding alternative stripping technologies and best management practices to minimize MeCl emissions at existing major and area sources. In selecting GACT for affected area sources that perform paint stripping operations, we determined that best management practices to minimize evaporative losses (fugitive emissions) from MeCl in paint stripper formulations was not only a practice that many in the industry use, but also was generally cost effective for all sources in this category.

    As part of the GACT analysis, we considered whether there were differences in processes, sizes, or other factors affecting emissions, control technologies or management practices that would warrant subcategorization. Under CAA section 112(d)(1) of the CAA, EPA ``may distinguish among classes, types, and sizes within a source category or subcategory in establishing such standard.'' In looking to other means by which MeCl emissions could be reduced from these operations, we did recognize that some sources utilized alternative stripping technologies (e.g., blasting) to accomplish much of their work. These sources, distinguishable from the rest of the category by having other available on site methods to strip paint not involving MeCl, could reasonably route work away from paint stripping operations that involved MeCl as a means of control. Pursuant to section 112(d)(1), we have subcategorized these sources with alternative stripping methods by class. As mentioned earlier, these different paint stripping methods include (1) nonMeCl containing chemical strippers; (2) mechanical stripping; (3) blasting (including dry or wet media); and (4) thermal or cryogenic decomposition. We also recognized that this subcategory represented the 30 percent (approximately) of the source category with the highest MeCl emissions. We determined that sources that used 150 gallons or more per year of paint stripper containing MeCl was the best approximation criteria for defining this subcategory for three reasons.

    First, based on our findings from: (1) A study of paint stripping facilities (referenced in a Metropolitan Water District of Southern California (Environmental Defense Fund) document entitled ``Source Reduction and Recycling of Halogenated Solvents in Paint Stripping Technical Support Document''), (2) our understanding of the affected facilities, and (3) our analysis of the model plants, for facilities using 150 gallons of MeCl or more per year, we believe it is reasonable to expect cost savings from the process of routing work away from paint stripping operations involving MeCl to other means of stripping. The study of paint stripping facilities highlighted to us that a good portion of paint stripping at these facilities (as high as 90 percent at one facility) was not really necessary. In being conservative, we believe that 5 percent of paint stripping is not necessary. An example of paint stripping that may be found as not necessary includes the [[Page 52967]]
    refinishing of personal oxygen gas cylinder surfaces (that often automatically get stripped of paint for cosmetic purposes during recycling) when they actually need no refinishing for serviceability. In addition, we believe that there is a slight cost savings associated with routing work away from paint stripping involving MeCl to a media blasting technique, when the media involved is recycled. Second, our analysis of model plants suggested that most facilities using 150 gallons of MeCl or more per year had other methods of stripping available on site (e.g., blasting or thermal) to which work could be easily routed. Finally, we recognized that the 150 gallon threshold reasonably coincides with exposure levels at which Occupational Safety and Health Administration (OSHA) requirements (29 CFR 1910.123 1910.126) are to be implemented. OSHA provided specific dip tank size criteria to characterize which size tanks must follow specific worker safety requirements. We calculated, based on the sizes provided by OSHA, the volume of stripper that the minimum tank would hold and used this volume for our size criteria. For these reasons we are proposing that facilities using 150 gallons of MeCl or more per year must, in addition to the best management practices to minimize evaporative losses, develop and implement the MeCl minimization plan mentioned earlier.

    We recognize that given the wide range of paint stripping operations and techniques, there is no single substitute that could completely eliminate the need for MeClcontaining paint strippers, particularly on confined and hard to reach surfaces where other methods tend not to remove paint as well. We do, however, believe that given the existing management practices currently exercised by much of this industry, it is not unreasonable to incorporate management practices that minimize or eliminate MeCl emissions from many of the applications where MeClcontaining paint strippers are used. Therefore, we are proposing standards that require operators to employ management practices to reduce the emissions of MeCl through alternative paint stripping techniques when possible, and, for sources that use 150 gallons of MeCl or more per year to develop and implement a minimization plan to reduce MeClcontaining paint stripper use when it is not needed.

    Miscellaneous Surface Coating

    The emissions from these operations come primarily from the spray application of coatings. Although most of the HAP are deposited as part of the paint film, some of the HAP becomes airborne in the paint overspray. The volume of coating deposited as part of the paint film as a fraction of the volume of paint sprayed is referred to as the transfer efficiency (i.e., 60 percent of the coating sprayed is deposited as paint film then the transfer efficiency is 60 percent).

    Our analysis of operations that involve the spray application of coatings has determined that GACT for these coating operations is a combination of: (1) Confining all spray coating operations to a spray booth or equivalent ventilated and filtered enclosure, (2) using only spray equipment that is designed to achieve a high rate of transfer efficiency (HVLP or equivalent spray technology), and (3) having the spray equipment operator trained and certified in the techniques needed to properly set up and operate high transfer efficiency spray equipment in order to optimize the transfer efficiency.

    Based on the site visits, data review, and contacts with industry, for which documentation is provided in the public docket for this rulemaking, we have determined that the standard practice among the majority of facilities in the miscellaneous surface coating industry is to perform nearly all spray painting inside a spray booth or ventilated prep station enclosed by curtains. The only exceptions are priming small areas, or performing spot repairs with an air brush. At many facilities, all spray painting is performed in a spray booth or ventilated prep station to reduce contaminants that would compromise the final finish and to maintain a clean work area. In addition, it is standard practice to filter the exhaust from the booth or prep station to capture paint overspray so that it is not deposited on ventilation equipment or surrounding property. Therefore, based on the availability and costeffectiveness, we have determined that a filtered spray booth or prep station is GACT for all miscellaneous surface coating operations to control HAP emissions. The proposed standards would require all spray painting that is not done with an airbrush or hand held nonrefillable aerosol cans to be done in a filtered spray booth or prep station. We also conclude that the above proposed control requirements can be achieved without additional burden to affected sources because filtered spray booths or prep stations are already required in order to comply with OSHA standards for spray finishing operations (29 CFR 1910.94(c)).

    At the majority of facilities that were visited, the spray booths were fitted with either fiberglass or polyester fiber filters on the spray booth and prep station exhaust. One facility had a waterwash spray booth filter and another had expanded polystyrene foam baffle filters. An EPA study entitled ``Comparative Study of Spray Booth Filter System Efficiency'', which is provided in the public docket for this rulemaking, determined that fiberglass and polyester fiber filters had superior performance, relative to other filter types, such as polystyrene foam and cardboard baffle filters, in controlling the heavy metals found in paint overspray and which are the target HAP for these source categories. Therefore, based on our findings during the site visits, information provided by the industry on the most commonly used filters, and the EPA study on filter effectiveness and the cost effectiveness we have determined that these fiberglass and polyester fiber filters represent GACT for controlling the heavy metals present in paint overspray.

    The proposed rule would allow for the use of other types of paint overspray filters, but they would be required to achieve 98percent filter efficiency. This alternative was included since the EPA did not test all types of filters used in spray booths; therefore the market may already provide for filters that are as equally efficient which were not available or not tested in the EPA study, but nevertheless representative of GACT. The EPA study on filter effectiveness and filter efficiency data provided by filter vendors formed the basis for the 98percent filter efficiency The limit represents a performance level that separates the fiberglass and polyester fiber filters from baffle type filters. The baffle type filters were shown in the EPA study to have poor performance in controlling fine particulate that can contain heavy metals.

    The proposed standards would not prohibit the use of coatings that contain the heavy metals or target HAP for these source categories. Although California has prohibited the use of automotive refinish coatings that contain CrVI and cadmium (Cd), a nationwide prohibition would impose unreasonable burden on the industry, and could force facilities out of business due to a lack of alternative materials that could address the performance criteria (e.g., corrosion protection) that may be used in all environments across the United States. The proposed standards would specifically require spray equipment that is designed to achieve a high rate of transfer efficiency (HVLP or equivalent spray technology) in order to reduce the overall amount of coating
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    required to complete each coating job. Reducing the amount of coating required for each job directly correlates to significant reductions in the overall emissions from these coating operations. Conventional high pressure airatomized spray guns have a typical transfer efficiency of about 30 percent. That means that for every gallon of coating sprayed, only 0.30 gallon reaches the part being coated. The remaining 0.70 gallon misses the part and either lands on the booth walls and floor or is pulled into the spray booth filters and exhaust system. To get one gallon on the part, a conventional spray gun needs to use 3\1/3\ gallons of coating. HVLP and other types of highefficiency spray guns use lower air pressures and achieve transfer efficiencies of about 50 percent, or greater, with appropriate operator training. To get one gallon on the part, a high efficiency spray gun needs to use only 2 gallons of coating. This increased transfer efficiency represents a 40 percent decrease in coating consumption and in resultant emissions compared to conventional spray guns. For these reasons, many surface coating operations have already switched to HVLP and other types of high efficiency spray guns.

    All of the autobody refinishing facilities visited by EPA and about 80 percent of the other miscellaneous surface coating facilities for which EPA has data used HVLP or equivalent spray guns for coating application. About half these sources were not required to do so by regulations and have switched in order to reduce coating costs through reduced consumption. Regulations for autobody refinishing in 10 States require the use of HVLP spray guns or their equivalent statewide, and they are required in ozone nonattainment areas in 12 States without a statewide requirement. Given the costeffectiveness and the use of HVLP or equivalent spray guns has been adopted at the facilities visited by EPA and is required in many States and ozone nonattainment areas, we have determined that these types of spray guns are GACT for spray applied coatings.

    The purpose of requiring the spray equipment operator to be trained and certified is to ensure that the operator is skilled in the techniques needed to achieve a high rate of transfer efficiency. We have concluded, based on the findings of the Spray Technique Analysis and Research (STAR[supreg]) program study presented in the following paragraph, and included in the public docket for this rulemaking, that even when spray operations are confined within a spray booth and appropriate spray technology is used, they are not as effective if the painter is not properly trained. We therefore have determined that GACT requires implementation of the above requirements by a trained painter.

    The training would include measures intended to increase transfer efficiency and reduce overspray and coating usage. Most, if not all of the measures are currently offered in training provided by coating manufacturers on an annual basis. In addition to manufacturersponsored training, the STAR[supreg] program, which originated at the University of Northern Iowa Waste Reduction Center, has now been adopted at 37 locations (primarily community colleges) throughout the United States. Coating manufacturers currently provide this training to their clients as part of the service benefits of contracting with them and as a component in the warranty agreement. Data from the STAR[supreg] program demonstrate that spray operator training can increase transfer efficiency for those using high efficiency spray equipment from

    FOR FURTHER INFORMATION CONTACT For information concerning the proposed standards, contact Mr. Warren Johnson, Office of Air Quality Planning and Standards, Sector Policies and Programs
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    Division, Natural Resources and Commerce Group (E14303), U.S. Environmental Protection Agency, Research Triangle Park, North Carolina 27711, telephone (919) 5415124, or email at johnson.warren@epa.gov. For technical information concerning the proposed surface coating standards, contact Ms. Kim Teal, Office of Air Quality Planning and Standards, Sector Policies and Programs Division, Natural Resources and Commerce Group (E14303), U.S. Environmental Protection Agency, Research Triangle Park, North Carolina 27711, telephone (919) 5415580, or email at teal.kim@epa.gov.


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