National Volatile Organic Compound Emission Standards for Automobile Refinish Coatings
Federal RegisterApr 30, 1996
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 59
[AD-FRL-5463-6]
RIN 2060-AE35
National Volatile Organic Compound Emission Standards for
Automobile Refinish Coatings
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule and notice of public hearing.
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SUMMARY: The EPA proposes standards to reduce emissions of volatile
organic compounds (VOC) from the use of automobile refinish coatings.
The proposed standards are in the first phase of implementation of the
portion of the Clean Air Act (Act) that requires the Administrator to
control VOC emissions from certain categories of consumer and
commercial products.
Exposure to ozone is associated with a wide variety of human health
effects, agricultural crop loss, and damage to forests and ecosystems.
As required by section 183(e) of the Act, the Administrator conducted a
study to determine the potential of consumer and commercial products to
contribute to ozone levels that violate the National Ambient Air
Quality Standards (NAAQS) for ozone. Because the automobile refinish
coatings category is a significant source of VOC emissions, the EPA is
proposing standards to reduce emissions from this source.
DATES: Comments. Comments must be received on or before July 1, 1996.
Public Hearing. A public hearing will be held, if requested. If
anyone contacts the EPA requesting to speak at a public hearing by May
21, 1996, a public hearing will be held on May 30, 1996, beginning at
9:00 a.m.
Request to Speak at Hearing. Persons wishing to present oral
testimony must contact Ms. Marguerite Thweatt at the EPA by May 21,
1996.
ADDRESSES: Comments. Comments should be submitted (in duplicate) to:
Air and Radiation Docket and Information Center (6102), Attention:
Docket No. A-95-18, U.S. Environmental Protection Agency, 401 M Street,
SW, Washington, DC 20460.
Public Hearing. Persons interested in attending the hearing should
notify Ms. Marguerite Thweatt, (919) 541-5607, to verify that a hearing
will occur and for notification of the location of the meeting.
Request to Speak at Hearing. To present oral testimony contact Ms.
Thweatt at the following address: Organic Chemicals Group (MD-13), U.S.
Environmental Protection Agency, Research Triangle Park, North Carolina
27711, telephone number (919) 541-5607, FAX number (919) 541-3470.
Docket. Docket No. A-95-18, containing supporting information used
in developing the proposed standards, is available for public
inspection and copying between 8:30 a.m. and 3:30 p.m., Monday through
Friday, at the EPA's Air and Radiation Docket and Information Center,
Waterside Mall, Room M-1500, 1st Floor, 401 M Street, SW, Washington,
DC 20460, telephone (202) 260-7548, FAX (202) 260-4400. The proposed
regulatory text and other materials related to this rulemaking are
available for review in the docket. A reasonable fee may be charged for
copying.
Background Information Document. The background information
document (BID) supporting the proposed standards may be obtained from
the docket or
[[Page 19006]]
from the U.S. EPA Library (MD-35), Research Triangle Park, North
Carolina 27711, telephone number (919) 541-2777. Please refer to
``Automobile Refinish Coatings--Background Information for Proposed
Standards,'' EPA-453/D-95-005a.
FOR FURTHER INFORMATION CONTACT: For information concerning the
proposed standards, contact Mr. Mark Morris at (919) 541-5416, Organic
Chemicals Group, Emission Standards Division (MD-13), U.S.
Environmental Protection Agency, Research Triangle Park, North Carolina
27711.
SUPPLEMENTARY INFORMATION: The regulatory text of the proposed rule is
not included in this Federal Register notice, but is available in
Docket No. A-95-18 (see ADDRESSES for information about the docket).
The proposed regulatory language is also available on one of the EPA's
Technology Transfer Network (TTN) electronic bulletin boards. The TTN
provides information and technology exchange in various areas of air
pollution control. The service is free, except for the cost of a phone
call. Dial (919) 541-5742 for up to a 14,400 bits per second (bps)
modem. If more information on the TTN is needed, call the help desk at
(919) 541-5384.
The information presented in this preamble is organized as follows:
I. Background
A. Clean Air Act Requirements
B. Legislative Authority
C. Regulatory Background
D. Supporting Documentation for the Proposed Standards
II. Summary of Proposed Standards
A. Applicability of the Standards
B. Regulated Entities
C. Standards
D. Compliance Requirements
E. Labeling Requirements
F. Reporting
G. Variance
H. Test Methods
III. Summary of Impacts
A. Environmental Impacts
B. Energy Impacts
C. Cost and Economic Impacts
D. Cost-Effectiveness
IV. Rationale
A. Applicability
B. Selection of BAC
C. Selection of Regulatory Format
D. Labeling Requirements
E. Selection of Reporting Requirements
F. Variance
G. Test Methods
H. Solicitation of Comments
V. Administrative Requirements
A. Public Hearing
B. Executive Order 12866
C. Paperwork Reduction Act
D. Regulatory Flexibility Act
E. Unfunded Mandates Reform Act
I. Background
A. Clean Air Act Requirements
Exposure to ground-level ozone is associated with a wide variety of
human health effects, agricultural crop loss, and damage to forests and
ecosystems. The most thoroughly studied health effects of exposure to
ozone at elevated levels during periods of moderate to strenuous
exercise are the impairment of normal functioning of the lungs,
symptomatic effects, and reduction in the ability to engage in
activities that require various levels of physical exertion. Typical
symptoms associated with acute (1 to 3 hour) exposure to ozone at
levels of 0.12 ppm or higher under heavy exercise or 0.16 ppm or higher
under moderate exercise include cough, chest pain, nausea, shortness of
breath, and throat irritation.
Ground-level ozone, which is a major component of ``smog,'' is
formed in the atmosphere by reactions of VOC and oxides of nitrogen
(NOX) in the presence of sunlight. In order to reduce ground-level
ozone levels, emissions of VOC and NOX must be reduced.
Section 183(e) of the Act requires the Administrator to study and
report to Congress on emissions of VOC into the ambient air from
consumer and commercial products and their potential to contribute to
ozone nonattainment levels. In addition, section 183(e) requires the
Administrator to list those categories of consumer and commercial
products that account for at least 80 percent of the VOC emissions, on
a reactivity-adjusted basis, in ozone nonattainment areas and establish
priorities for their regulation. The list is to be divided into four
groups, with one group regulated every 2 years until all four groups
are regulated.
The EPA submitted the Report to Congress on March 15, 1995, and on
this same date established the priority list for future regulation of
the consumer and commercial products that account for 80 percent of VOC
emissions, on a reactivity-adjusted basis, in nonattainment areas
(published on March 23, 1995, at 56 FR 15264). Automobile refinish
coatings are in the first group of products to be regulated by March
1997. This listing and prioritization are not final Agency actions, and
EPA requests comment on the placement of automobile refinish coatings
on the list and the priority assigned to these coatings. Further
details about the study and the listing are available in the March 23,
1995, Federal Register.
B. Legislative Authority
Section 183(e) of the Act gives the EPA the authority to establish
national standards to reduce VOC emissions from automobile refinish
coatings. According to the Act, regulations developed under this
section shall require best available controls (BAC). Best available
controls are defined in section 183(e)(1)(A) as follows:
The term ``best available controls'' means the degree of
emissions reduction that the Administrator determines, on the basis
of technological and economic feasibility, health, environmental,
and energy impacts, is achievable through the application of the
most effective equipment, measures, processes, methods, systems, or
techniques, including chemical reformulation, product or feedstock
substitution, repackaging, and directions for use, consumption,
storage, or disposal.
Section IV.B describes the EPA's determination of BAC for the proposed
regulation.
The EPA could satisfy the requirements of section 183(e) by issuing
Control Techniques Guidelines (CTG) instead of a national rule for
automobile refinish coatings.
Section 183(e)(3)(C) states:
For any consumer or commercial product the Administrator may
issue control techniques guidelines under this Act in lieu of
regulations required under subparagraph (A) if the administrator
determines that such guidance will be substantially as effective as
regulations in reducing emissions of volatile organic compounds
which contribute to ozone levels in areas which violate the national
ambient air quality standard for ozone.
In many cases, CTG's can be effective regulatory approaches to reduce
emissions of VOC in nonattainment areas--with the advantage of not
imposing control costs on attainment areas, where VOC emissions
reductions may be less beneficial. On the other hand, rules based on
CTG's may impose requirements and costs in nonattainment areas that are
beyond those of a national rule. For example, State automobile refinish
rules require recordkeeping by body shops, while the national rule does
not.
The EPA can also use other systems of regulation. According to
section 183(e)(4), EPA can consider ``any system or systems of
regulation as the Administrator deems appropriate, including
requirements for registration and labeling, self-monitoring and
reporting, prohibitions, limitations, or economic incentives (including
marketable permits and auctions of emissions rights) concerning the
manufacture, processing, distribution, use, consumption or disposal of
the
[[Page 19007]]
product.'' The EPA solicits comments on alternative approaches to
regulation in section IV.H.
C. Regulatory Background
Automobile refinish coatings are included under the definition of
consumer and commercial products since the definition under section
183(e) of the Act specifically includes paints, coatings, and solvents.
Section 183(e) of the Act requires that the first group of consumer and
commercial products (i.e., those with highest priority for regulation)
be regulated within 2 years after publication of the regulatory
schedule. As mentioned previously, automobile refinish coatings are in
the first group of consumer and commercial products to be regulated.
The regulation is required by March 1997. The criteria which contribute
to the prioritization of automobile refinish coatings in the first
group of consumer and commercial products to be regulated include the
availability of alternatives, the cost-effectiveness of controls, and
the VOC emissions in ozone nonattainment areas. Further details about
the criteria used to prioritize consumer and commercial product
categories for regulation are available in the Report to Congress.
Automobile refinish coating regulations are in place or under
development in a number of States. For the companies that market
automobile refinish coatings nationwide, trying to fulfill the
differing requirements of State rules has created administrative,
technical, and marketing problems. A Federal rule is expected to
provide some degree of consistency, predictability, and administrative
ease for the industry.
In addition, State representatives have recommended that the EPA
develop and implement nationwide Federal control measures to enhance
enforceability and conserve State resources.
D. Supporting Documentation for the Proposed Standards
The automobile refinish coating background information document
(BID) (EPA publication number EPA-453/D-95-005a) contains supporting
documentation for this proposal. It contains a product category
description, an industry profile, a discussion of control measures and
their associated costs, and a description of the expected emissions
reductions. Other supporting information for this proposed regulation
includes existing State regulations, meeting summaries, and the report
to Congress on consumer and commercial products. This information is
contained in the docket and is available to the public as described
above.
II. Summary of Proposed Standards
The proposed standards are summarized below. The rationale for the
regulatory decisions made in developing these standards is provided in
section IV.
A. Applicability of the Standards
The provisions of this proposed rule apply to automobile refinish
coatings that are manufactured or imported for sale or distribution in
the United States.
The proposed standards do not apply to the following automobile
refinish coatings:
(1) Coatings manufactured exclusively for sale outside the United
States;
(2) Coatings manufactured or imported before the compliance date of
the rule;
(3) Coatings manufactured for use by original equipment
manufacturers for assembly-line coating operations; and
(4) Coatings supplied in nonrefillable aerosol containers.
B. Regulated Entities
Regulated entities are defined under section 183(e) to include
manufacturers, processors, wholesale distributors, and importers. This
proposed rule limits the VOC contents of coatings manufactured or
imported for use in this country. Since the distribution of coatings
has no effect on whether compliant coatings are used, distributors are
not regulated entities under this proposed rule.
C. Standards
Coatings subject to this proposed rule shall comply with the VOC
content standards listed in table 1. If a coating is marketed under
more than one of the listed coating categories, the coating shall
comply with the lowest applicable VOC content standard.
Table 1.--VOC Content Standards for Automobile Refinish Coatings
------------------------------------------------------------------------
Coating Category VOC Contenta (grams/liter)
------------------------------------------------------------------------
Pretreatment Wash Primer.................. 780
Primer/Primer Surfacer.................... 575
Primer Sealer............................. 550
Single/2 Stage Topcoats................... 600
Topcoats of 3 or more stages.............. 625
Specialty Coatingsb....................... 840
------------------------------------------------------------------------
aVOC content means the amount of VOC in a coating that has been prepared
for application according to the manufacturer's mixing instructions,
excluding water and exempt compounds.
bSpecialty coatings include adhesion promoters, anti-glare/safety
coatings, bright metal trim repair coatings, elastomeric materials,
impact-resistant coatings, rubberized asphaltic underbody coatings,
uniform finish blenders, and weld-through primers.
D. Compliance Requirements
The compliance date of the rule is 4 months after the promulgation
date of the rule.
E. Labeling Requirements
Containers of all subject coatings must bear labels or lids that
include the date of manufacture of the contents or a code indicating
the date of manufacture.
F. Reporting
Manufacturers and importers of coatings subject to the proposed
standards must file an initial report. The initial report must be
submitted by the compliance date or within 180 days after becoming
subject to the rule, whichever is later. The initial report must
include the following information:
(1) The name and mailing address of the manufacturer or importer.
(2) In cases where codes are used to represent the date of
manufacture, the manufacturer or importer shall submit an explanation
of each date code to the Administrator. An explanation of any new date
codes shall be filed with the Administrator no later than 30 days after
it is first introduced into commerce.
G. Variance
The proposed rule allows manufacturers and importers of automobile
refinish coatings to submit a written application to the Administrator
requesting a variance if, for reasons beyond their reasonable control,
they cannot comply with the requirements of the proposed rule. The
application must include the following information:
(1) The specific grounds for which the variance is sought;
(2) The proposed date(s) by which compliance with the provisions of
the rule will be achieved; and
(3) A compliance report reasonably detailing the method(s) by which
compliance will be achieved.
Upon receipt of the variance application, the Administrator will
hold a public hearing to determine whether, under what conditions, and
to what extent, a variance from the requirements of the proposed rule
is necessary and will be permitted.
The Administrator may grant a variance if the following criteria
are met:
(1) By complying with the proposed rule, the applicant would bear
unreasonable economic hardship;
(2) The public benefit of avoiding hardship to the applicant
outweighs the public interest in any increased emissions or air
contaminants that would result from issuing the variance; and
[[Page 19008]]
(3) The proposed compliance schedule can be reasonably implemented,
and compliance will be achieved as expeditiously as possible.
The approved variance order will designate a final compliance date
and a condition that specifies increments of progress necessary to
assure timely compliance. A variance shall end immediately upon the
failure (of the party to whom the variance was granted) to comply with
any term or condition of the variance.
H. Test Methods
For purposes of determining compliance with this rule, the VOC
content of each coating product manufactured or imported must be
determined using EPA's Reference Method 24--``Determination of Volatile
Matter Content, Water Content, Density, Volume Solids, and Weight
Solids of Surface Coatings,'' found in 40 CFR part 60, appendix A.
Analysis of waterborne coating VOC content determined by Reference
Method 24 must be adjusted as described in section 4.4 of Reference
Method 24.
The Administrator may approve, on a case-by-case basis, alternative
methods of determining the VOC content of coatings if they are
demonstrated to the Administrator's satisfaction to provide results
equivalent to those obtained using Reference Method 24.
III. Summary of Impacts
A. Environmental Impacts
This section will discuss the incremental increase or decrease in
air pollution, water pollution, and solid waste generation that would
result from implementing the proposed standards.
1. Air Pollution Impacts
The proposed standards would reduce nationwide emissions of VOC
from the use of automobile refinish coatings by an estimated 32,500 Mg
(35,800 tons) in 1996. These reductions are compared to 1995 baseline
emissions estimates. Since many regulated VOC species are also on the
list of hazardous air pollutants (HAP) in section 112 of the Act, the
proposed rule is expected to reduce some HAP emissions from the use of
automobile refinish coatings.
2. Water and Solid Waste
There are no adverse solid waste impacts anticipated from
compliance with this rule. It is not expected that the disposal of
coatings as solid waste will increase as a result of this rule. In
fact, because the compliant (higher solids) coatings are more
concentrated, fewer containers will require disposal when the same
volume of solids is applied.
In cases where conversion from solventborne to waterborne coatings
is the method used to achieve compliance, an increase in wastewater
discharge may occur if waste waterborne coatings are discharged to
publicly owned treatment works.
B. Energy Impacts
There are no adverse energy impacts anticipated from compliance
with this rule. Compliant coatings will not require different
application equipment and no add-on controls are required.
C. Cost and Economic Impacts
The total cost of this rule includes coating manufacturer process
modification costs, and costs for training coating manufacturer
representatives, distributors, and body shop personnel. The EPA
believes that coatings that meet the VOC content limits of this
proposed rule do not have longer drying times than conventional
coatings; therefore, the EPA has not included costs for lost
productivity in this rule. The EPA requests comments and data regarding
the drying times of coatings compliant with this proposed rule, and any
information that indicates that there may be costs due to losses in
productivity. The annual cost of this rule is 4.5 million dollars, or
about $140 per megagram of VOC emissions reductions.
If the manufacturer and distributor costs are completely passed on
as a coating price increase, the price of coatings is estimated to
increase less than 10 cents per gallon (less than 0.2 percent). If the
total cost of the rule is passed on as an increase in the price of a
refinish job, the price is estimated to increase less than 30 cents per
job (less than 0.05 percent).
D. Cost-Effectiveness
The EPA often compares the relative cost of different measures for
controlling a pollutant by calculating the ``cost-effectiveness'' of
the measures. Using EPA's traditional calculation methodology, the
cost-effectiveness of a regulation that applies nationwide is based on
a comparison of national costs and nationwide emission reductions. This
comparison is expressed as the cost per megagram (or ton) of emissions
reduced. Using cost and emission reduction figures presented earlier in
this section of the preamble, the nationwide cost-effectiveness of the
proposed regulation is $140/Mg ($130/ton).
Alternative ways to calculate a measure of the ``cost-
effectiveness'' of the regulation have been suggested by others. One
alternative would be to calculate cost-effectiveness on the basis of
the nationwide cost of the regulation ($4.5 million for the proposed
regulation) and the VOC reduction achieved in ozone nonattainment
areas. The stated rationale for this approach is that cost-
effectiveness measures should be designed in a way that best represents
the objective of the regulatory action. In this case, for example, a
major objective, though not the only objective, of these regulations is
the control of ozone formation in nonattainment areas. By establishing
nationwide standards, the cost of achieving emission reductions in
ozone nonattainment areas during the ozone seasons requires nationwide
expenditures during all seasons of the year, including expenditures
year-round in areas currently in attainment with the current standard.
These nationwide emission reductions--including emission reductions
outside of nonattainment areas and out of the ozone season--may or may
not contribute to efforts to limit ozone in nonattainment areas,
depending on whether they participate in ozone transport from one area
to another. One example of the application of this method is presented
in a December 21, 1993, draft Regulatory Impact Analysis developed by
the EPA's Office of Mobile Sources (OMS) in which control of emissions
from refueling of light duty vehicles (i.e., onboard refueling vapor
recovery, or ORVR) could viably be applied either nationwide or in
nonattainment areas alone. In this example, regional regulation
represented an important alternative to national regulation. The OMS
calculated cost-effectiveness using (1) nationwide costs and nationwide
emission reductions, as well as (2) nationwide costs and the emission
reductions achieved in nonattainment areas.
Emissions from automobile refinish coatings used in nonattainment
areas have been estimated. On a nonattainment area basis, the cost-
effectiveness of the proposed automobile refinish coatings rule would
be $300/Mg ($280/ton). A similar calculation could be done to account
for the seasonality of ozone formation.
While such an approach offers a measure of the cost of emission
reductions in nonattainment areas, EPA sees significant drawbacks to
this approach. First, cost-effectiveness figures would no longer
provide a consistent basis for comparison of the relative cost of
different control measures or regulations considered at different
points in time. Because the number and location of nonattainment areas
changes frequently, the initial
[[Page 19009]]
calculation of the cost-effectiveness of a rule would depend upon when
it was issued. The EPA believes it is important that cost-effectiveness
be calculated in a consistent manner that allows for valid comparisons.
Also, introducing new methodology would tend to make new control
measures appear superficially to be less cost-effective than measures
utilized in the past, simply because of a change in well-established
terminology.
Second, this alternative approach attributes all costs of the rule
to emission reductions achieved in nonattainment areas and no cost to
emission reductions achieved in attainment areas. By not including
emission reductions in attainment areas, the methodology assumes that
emission reductions in areas which attain the NAAQS for ozone have no
value. In fact, attainment areas often contribute to pollution problems
in nonattainment areas through the transport of emissions downwind.
Also, emission reductions in attainment areas help to maintain clean
air as the economy grows and new pollution sources come into existence.
Furthermore, measures to reduce emissions of VOC often reduce emissions
of toxic air pollutants.
Another alternative that has been suggested would be to calculate
not only the emission reductions but also the cost if the requirements
applied only in ozone nonattainment areas, perhaps through issuance of
a Control Techniques Guideline (CTG). The EPA has not estimated the
cost of using a CTG to regulate only those products sold for use in
ozone nonattainment areas.
The EPA is planning to review internally the generic question of
the alternative approach to measuring costs against emission
reductions. The results of this review are not available for
incorporation into this rulemaking. Therefore, the EPA requests
comments on the traditional and alternative methods discussed above to
characterize the cost-effectiveness of this and other Section 183(e)
regulations.
V. Rationale
The following sections explain the rationale for selecting the
proposed standards.
A. Applicability
This proposed rule applies to automobile refinish coatings that are
manufactured or imported for sale or distribution in the United States.
Coatings that are currently used for automobile refinishing are also
used outside the automobile refinish industry. In fact, some of these
coatings are not labeled specifically as automobile refinish coatings,
but are labeled generally as primers, basecoats, etc. This proposed
rule applies only to those coatings that are marketed as automobile
refinish coatings. Therefore, coating manufacturers define which of
their coatings are automobile refinish coatings by the way they market
them. All coatings marketed as automobile refinish coatings are subject
to this proposed rule; all other coatings are not.
Automobile refinish coatings were determined to be a significant
source of VOC emissions in nonattainment areas and were designated for
regulation under the authority of section 183(e) of the Act. The
proposed standards do not apply to some types of coatings. There are
exemptions for exported coatings, coatings manufactured or imported
before the compliance date, coatings that are sold in nonrefillable
aerosol containers, and coatings that are manufactured for use by
original equipment manufacturers (OEM's) for assembly-line coating
operations.
The purpose of section 183(e) of the Act is to control VOC
emissions that contribute to ozone nonattainment in the United States.
Because exported coatings do not contribute to VOC emissions in the
United States, and because EPA has no legal or factual basis to impose
VOC control measures outside the United States, coatings manufactured
for the explicit purpose of export, and which are in fact exported, are
exempt from the requirements of the proposed rule.
An exemption for coatings sold in nonrefillable aerosol containers
is included in the proposed rule because the EPA is developing a
separate VOC regulation for these coatings under section 183(e)
authority.
Coatings that are manufactured for use by OEM's for assembly-line
coating operations are exempt from this proposed rule because such
coatings are significantly different than refinish coatings; OEM's are
covered by standards promulgated under section 111 of the Act, and will
be covered by standards promulgated under section 112 of the Act.
Each coating manufacturer produces coating components, such as
hardeners, reducers, additives, etc., necessary for the preparation of
a ``ready-to-spray'' coating. Some coating manufacturers also produce
components for use in the coatings of other manufacturers; some
companies do not produce coatings at all, but produce only coating
components for use in the coatings of other manufacturers. Although
preparing a coating using only the components and suggested mixing
ratio of one manufacturer may yield a compliant coating, preparing a
coating with the components of several manufacturers may not. To be
effective, this proposed rule may need to apply to all coating
components; that is, if a coating component manufacturer suggests that
a coating component may be used for automobile refinishing, and if its
suggested use would result in the preparation of a noncompliant
coating, then the coating component manufacturer would be out of
compliance with the rule. Until recently the EPA was not aware of the
extent to which coating users combined the components of multiple
manufacturers. As a result, the EPA has not sufficiently examined how
to enforce this proposed rule if its applicability were expanded to
include all automobile refinish coating components, or the impacts that
the rule would have on the manufacturers who would become affected by
the rule if its applicability were expanded. The EPA has, therefore,
limited applicability to coating manufacturers in this proposed rule,
but is soliciting comments on whether to expand the applicability.
Based on information received during the comment period, the EPA may
expand the applicability in the promulgated rule.
The EPA is aware that the VOC content standards of this proposed
rule would likely prohibit the manufacture or import of lacquer
coatings. Lacquers are no longer used on new vehicles, and are mainly
used by antique car restorers; therefore, the demand for lacquers is
small and is likely to decrease. Although other coatings are compatible
with lacquers and may be used to refinish an existing lacquer finish,
some colors available in lacquer are not available in other coatings.
Since the production of lacquer topcoats is small and not likely to
increase, and since they may be necessary to fill a niche in automobile
refinishing, the EPA is considering exempting lacquer topcoats from the
proposed rule. Although lacquer topcoat use is not likely to increase,
an exemption would not prevent it. Therefore, the EPA is also
considering whether to include lacquer topcoats in the specialty
coating category (described in section IV.B.) and limit their
production to a small percentage of total automobile refinish coating
production. The EPA solicits comments on these issues in section IV.H.;
based on information received during the public comment period, the EPA
may, in the promulgated rule, either exempt lacquer topcoats, or
[[Page 19010]]
categorize them as specialty coatings and limit their production.
B. Selection of BAC
The primary factors considered in determining best available
controls (BAC) were technological and economic feasibility, and
environmental impacts. Other impacts, such as nonair environmental
impacts (solid waste and water) and energy impacts, are expected to be
minimal. Health impacts are expected to parallel environmental impacts
in terms of directional benefit (i.e., as environment improves, health
improves). The EPA relied on existing State and local automobile
refinish rules, coating product information, and input from the
automobile refinish industry to determine the availability and
technological and economic feasibility of coatings.
The BAC selection process involves both the selection of coating
categories and the determination of VOC content limits for those
categories. These components are linked in a determination of what
degree of emissions reduction represents BAC. Decisions to subdivide a
given category into more specific ``subcategories'' can be a direct
consequence of the VOC content levels under consideration. For example,
pretreatment wash primers etch bare metal surfaces to provide adhesion
of the coating to the metal. According to coating product information
there are no pretreatment wash primers that have VOC content levels as
low as other primers. Therefore, a subcategory was created for this
primer, along with a VOC content level different from the general
primer category. Similarly, a subcategory was created for topcoats of
three (or more) stages because coating information indicates that there
are no such coatings with VOC content levels as low as those of other
topcoats.
``Specialty coatings'' that serve specific functions and that
either do not belong in other coating categories or are not available
at the VOC content limits of those categories are included in a
separate category. This category includes coatings that are designed
for a specific use, and coatings of other categories that are modified
by changing the components of the coating. In this proposed rule, all
coatings that the EPA considers specialty coatings are defined. It may
not be possible to determine all of the specialty coatings that may be
needed in the future as new OEM coatings are developed; therefore, an
open-ended definition of specialty coatings is desirable. However, such
a definition could be abused by simply renaming existing coatings as
specialty coatings. Even with a closed definition, the specialty
coating category may have undesirable effects. For example, an
elastomeric coating is a specialty coating. Some flexible topcoats,
which are considered elastomeric coatings, are prepared simply by
adding a flexible hardener in place of the normal hardener. In this
case, the specialty coating category would allow topcoats to be used
that exceed the VOC content standard for topcoats.
Limiting the production of specialty coatings to a small percentage
of total automobile refinish coating production may be effective in
minimizing the problems associated with this category. However, as
mentioned above, some specialty coatings are just modifications of
other coatings, and it is unclear what the EPA would be limiting.
Limiting specialty coating production to a percentage of total
production would adversely affect manufacturers that are mainly in the
specialty coating business. The EPA is considering limiting the
production of specialty coatings, and is soliciting comments on how to
determine such limits and how they can be made enforceable. Based on
information received during the public comment period, the EPA may
include specialty coating production limits in the promulgated rule.
The process of determining BAC began with the examination of State
and local automobile refinish rules. The EPA focused on existing
coating categories and their associated VOC standards in State and
local rules to determine which categories and VOC content limits might
constitute the degree of emissions reduction that represents BAC.
Specifically, California rules were analyzed because California has
been regulating automobile refinish coatings for several years and
generally has the most stringent VOC standards in the country.
The VOC limits of California rules are typically met with
waterborne coatings. Coating manufacturers have stated that they would
need to modify their production facilities to supply the entire country
with waterborne coatings. Such modifications reportedly include the
replacement of carbon steel equipment with corrosion-resistant
materials. Although not usually necessary in the relatively dry climate
of California, in some geographic areas of the country waterborne
coatings would likely require forced drying with supplemental heating
equipment (such as heated spray booths or infrared heating lamps)
because of their longer drying times.
In geographic areas without existing automobile refinish rules,
solventborne coatings are typically used that have relatively high VOC
content levels; these coatings are sometimes referred to as
``conventional'' coatings. Conventional coatings are typically fast-
drying and, therefore, do not need to be force-dried. There is not a
continuous spectrum of coating VOC content levels; coatings with the
lowest VOC content levels (such as waterborne coatings) were developed
to comply with State and local rules. Conventional coatings (that have
the highest VOC content levels) were developed to satisfy the demand
for fast-drying coatings that are easy to use. However, between these
extremes there exist coatings that have VOC content levels that are
lower than those of conventional coatings, that are not significantly
harder to use or slower to dry than conventional coatings, and that do
not require the forced drying or extensive coating manufacturer process
modifications of the coatings with the lowest VOC content levels. The
VOC content limits that are being proposed as BAC in this proposed rule
are based on such ``medium-solids'' coatings.
The EPA considered proposing a VOC content standard of 550 grams
per liter for primers and primer surfacers. Coating product information
indicates that coatings at this level are available. However, primers
at this level are not tintable according to the information available
to the EPA. Tintable primers are available with a VOC content of 575
grams per liter. When tintable primers are used, less topcoat needs to
be applied because the tint of the primer assists in achieving the
final color desired. Since less topcoat is used when tintable primers
are used, and since the VOC content of topcoats are generally higher
than 550 grams per liter, VOC emissions reductions are expected to be
equal or greater when tintable primers are used. The EPA is therefore
proposing a 575 grams per liter standard for primers and primer
surfacers. Comments on the proposed standard for primers and primer
surfacers are solicited in section IV.H.
Since most of the nation uses conventional coatings, these coatings
provide a reference point from which to assess technological and
economic feasibility. The emissions reductions and cost impacts of
regulatory alternatives considered by the EPA are given in table 2.
[[Page 19011]]
Table 2.--Impacts of Regulatory Alternatives
----------------------------------------------------------------------------------------------------------------
Emissions Capital Annual Cost Incremental cost
Regulatory alternative reductions * costs 10 costs 10 effectiveness $/ effectiveness $/
Mg/yr \6\ $ \6\ $ Mg Mg
----------------------------------------------------------------------------------------------------------------
BAC................................... 32,500 32 5 140 ................
Beyond BAC............................ 36,800 240 34 930 6900
----------------------------------------------------------------------------------------------------------------
* Baseline emissions are 88,500 Mg/yr.
As previously mentioned, medium-solids coatings do not need to be
force-dried, and the process modifications of coating manufacturing
facilities necessary to produce such coatings nationwide are less
extensive than those needed to produce waterborne coatings. The capital
cost associated with the use of medium-solids coatings is about 4.5
million dollars; about 60% of the cost is for the training of coating
manufacturer and distributor representatives and shop personnel in the
use of lower-VOC coatings. The cost effectiveness of using medium-
solids coatings is about $140 per megagram; the incremental emissions
reductions that would be achieved by going beyond (or lower than) the
VOC content limits of medium-solids coatings would cost about $6900 per
megagram. Most of this cost (60%) is from the purchase by body shops of
additional heating equipment necessary to speed the drying of the
coatings to avoid losses in productivity. Because of these high
incremental costs, the EPA selected the VOC content limits in Table 1
as BAC.
C. Selection of Regulatory Format
In contrast to traditionally regulated stationary sources that emit
VOC at a specific fixed location (e.g., a manufacturing plant), VOC
from automobile refinish coatings are emitted wherever the products are
used. For this reason, regulating at the manufacturer and importer
level is the most efficient and least burdensome method of regulating
the VOC content of coatings, and would ultimately impact the VOC
content of automobile refinish coatings at the distributor and end user
level.
The framework EPA chose to implement BAC is VOC content standards.
Coatings manufactured or imported on or after the effective date must
comply with the VOC content standards. The EPA will continue to gather
data with which to evaluate the potential for further emissions
reductions or alternate frameworks for implementing BAC such as
economic incentive-type approaches.
D. Labeling Requirements
The proposed regulation requires that containers for all subject
coatings display on the label or lid the date of manufacture or a code
indicating the date of manufacture. This information allows enforcement
personnel to determine whether a coating was manufactured before or
after the compliance date.
E. Selection of Reporting Requirements
The EPA evaluated what reported information would be sufficient to
ensure compliance with VOC standards within the proposed rule. The
reporting requirements proposed are necessary to allow determination of
compliance, and the EPA believes they do not represent an undue burden
on manufacturers or importers of automobile refinish coatings.
Compliance with this rule will be determined by periodic random testing
(EPA Reference Method 24, described below). Therefore, beyond the
initial report, which serves to identify all manufacturers and
importers of automobile refinish coatings, there are no reporting
provisions in this rule (except for reports explaining any new date
codes and for variances).
F. Variance
The proposed rule includes a variance provision whereby
manufacturers and importers of subject automobile refinish coatings may
apply to the Administrator for a temporary variance from compliance
with the standards. A variance will be granted if the applicant
demonstrates that compliance would result in economic hardship, and
that granting the variance would better serve the public interest than
would requiring continuous compliance under the conditions of economic
hardship. The EPA intends for this provision to allow manufacturers and
importers some flexibility in responding to unforeseen circumstances
that may cause additional, unanticipated compliance burden. The EPA
recognizes that certain interruptions in the availability of raw
materials and or manufacturing processes may affect the manufacturer's
or importer's ability to continuously comply with the standards. In
particular, the EPA anticipates that this variance provision will help
to mitigate impacts to small manufacturers. Small manufacturers are
likely to have fewer research and development resources, and,
therefore, will benefit from the allowed variance.
G. Test Methods
Under the proposed provisions, compliance with the VOC content
standards is based on the EPA's Reference Method 24. This test method
represents the EPA's approved protocol for determining the VOC content
of coatings and is EPA's standard test method for determining the VOC
content of coatings.
Standard language allowing use of alternative methods of
determining VOC content subject to the Administrator's approval is also
included in the proposed rule.
H. Solicitation of Comments
The Administrator welcomes comments from interested persons on any
aspect of the proposed rule, and on any statement in the preamble or
the referenced supporting documents. The proposed rule was developed on
the basis of information available to the EPA. The Administrator is
specifically requesting factual information that may support either the
approach taken in the proposed standards or an alternate approach.
The EPA is requesting specific comments and data on several aspects
of the proposed rule: (1) Alternative approaches to regulation; (2)
expanding the applicability of the rule to include all automobile
refinish coating components; (3) limiting production of lacquer
topcoats, or exempting lacquer topcoats from the rule; (4) determining
and enforcing specialty coating production limits; and (5) the
technical and economic feasibility of VOC content levels that are
higher or lower than the 575 grams/liter standard for primers and
primer surfacers.
The EPA anticipates promulgating this rule on an expedited
schedule. This will benefit States for which VOC reductions from
automobile refinish coating are critical to their 15 percent rate-of-
progress plans, and help minimize the patchwork of individual State
automobile refinish coating rules across the country.
[[Page 19012]]
Comments submitted to the Administrator should contain specific
proposals and supporting data to allow the EPA to fully evaluate the
comments. Recommended changes to any of the VOC content standards
presented in this proposal should include sufficient information for
the EPA to evaluate the technological and economic feasibility
associated with such changes. Applicable dates and addresses for the
submission of comments are included at the beginning of this preamble.
VI. Administrative Requirements
A. Public Hearing
A public hearing will be held, if requested, to provide opportunity
for interested persons to make oral presentations regarding the
proposed regulation in accordance with section 307(d)(5) of the Act.
Persons wishing to make oral presentation on the proposed regulation
for automobile refinish coatings should contact the EPA at the address
given in the ADDRESSES section of this preamble. Oral presentations
will be limited to 15 minutes each. Any member of the public may file a
written statement before, during, or within 30 days after the hearing.
Written statements should be addressed to the Air Docket Section at the
address given in the ADDRESSES section of this preamble and should
refer to Docket No. A-95-18.
A verbatim transcript of the hearing and written statements will be
available for inspection and copying during normal business hours at
the EPA's Air Docket Section in Washington, DC (see ADDRESSES section
of the preamble).
B. Executive Order 12866
Under Executive Order 12866, the Agency must determine whether a
regulatory action is ``significant'' and therefore subject to Office of
Management Budget (OMB) review and the requirements of the Executive
Order. The Order defines ``significant regulatory action'' as one that
is likely to result in a rule that may:
(1) Have an annual effect on the economy of $100 million or more,
or adversely affect in a material way the economy, a sector of the
economy, productivity, competition, jobs, the environment, public
health or safety, or State, local, or tribal governments or
communities;
(2) Create a serious inconsistency or otherwise interfere with an
action taken or planned by another agency;
(3) Materially alter the budgetary impact of entitlements, grants,
user fees, or loan programs or the rights and obligations of recipients
thereof; or
(4) Raise novel legal or policy issues arising out of legal
mandates, the President's priorities, or the principles set forth in
the Executive Order.
Pursuant to the terms of the Executive Order, the OMB has notified
the EPA that it considers this a ``significant regulatory action''
within the meaning of the Executive Order. The EPA submitted this
action to the OMB for review. Any written comments from the OMB to the
EPA and any written EPA response to those comments will be included in
Docket No. A-95-18, listed at the beginning of this notice under
ADDRESSES.
C. Paperwork Reduction Act
The information collection requirements in this proposed rule have
been submitted for approval to the Office of Management and Budget
(OMB) under the Paperwork Reduction Act, 44 U.S.C. 3501 et seq. An
Information Collection Request (ICR) document has been prepared by EPA
(ICR No. __) and a copy may be obtained from Sandy Farmer, OPPE
Regulatory Information Division; U.S. Environmental Protection Agency
(2136); 401 M Street, S.W.; Washington, DC 20460, or by calling (202)
260-2740.
Pursuant to Section 183(e) of the Act, the proposed rule regulates
VOC emissions from automobile refinish coatings. The only information
collection requirements of the proposed rule are for labeling and
reporting. To determine whether a coating is manufactured before or
after the compliance date of the rule, the date of manufacture, or code
representing the date, must appear on the coating container. Coating
manufacturers currently include this information on coating containers.
The proposed rule requires all coating manufacturers to submit an
initial report containing their name and mailing address, and an
explanation of coating date codes, if codes are used to represent the
date of coating manufacture. Reporting beyond the initial report is
required only for the explanation of any new date codes used by coating
manufacturers, and for requests for variances. The information to be
reported is not of a sensitive nature.
The EPA estimated the cost and hour burden of the information
collection requirements of the proposed rule. Burden means the total
time, effort, or financial resources expended by persons to generate,
maintain, retain, or disclose or provide information to or for a
Federal agency. This includes the time needed to review instructions;
develop, acquire, install, and utilize technology and systems for the
purposes of collecting, validating, and verifying information,
processing and maintaining information, and disclosing and providing
information; adjust the existing ways to comply with any previously
applicable instructions and requirements; train personnel to be able to
respond to a collection of information; search data sources; complete
and review the collection of information; and transmit or otherwise
disclose the information.
The initial report must be submitted by all coating manufacturers.
Averaged over a 3 year period, EPA estimates that the initial report
will require 8 hours to complete, and will be submitted by 10
respondents annually. Beyond the initial report, EPA estimates that 3
respondents per year will spend 2 hours each reporting the explanations
of any new date codes used. The total annual cost of the reporting
requirements of the proposed rule is $3,200.
An agency may not conduct or sponsor, and a person is not required
to respond to a collection of information unless it displays a
currently valid OMB control number. The OMB control numbers for EPA's
regulations are listed in 40 CFR Part 9 and 48 CFR Chapter 15.
Comments are requested on the Agency's need for this information,
the accuracy of the provided burden estimates, and any suggested
methods for minimizing respondent burden, including through the use of
automated collection techniques. Send comments on the ICR to the
Director, OPPE Regulatory Information Division; U.S. Environmental
Protection Agency (2136); 401 M St., S.W.; Washington, D.C. 20460; and
to the Office of Information and Regulatory Affairs, Office of
Management and Budget, 725 17th St., N.W., Washington, D.C. 20503,
marked ``Attention: Desk Officer for EPA.'' Include the ICR number in
any correspondence. Since OMB is required to make a decision concerning
the ICR between 30 and 60 days after April 30, 1996, a comment to OMB
is best assured of having its full effect if OMB receives it by May 30,
1996. The final rule will respond to any OMB or public comments on the
information collection requirements contained in this proposal.
D. Regulatory Flexibility Act
The Regulatory Flexibility Act (5 U.S.C. 601 et seq.) requires EPA
to consider potential impacts of proposed regulations on small business
``entities.'' A regulatory flexibility analysis (RFA) is required if
preliminary analysis indicates ``a significant economic impact on a
substantial number of small entities.''
[[Page 19013]]
Shops in the autobody refinish industry are classified as small by
the U.S. Small Business Administration if the entity that owns the shop
has total sales of less than $3.5 million. Most individual shops are
small by this criterion if the owning entity has no other sales from
other shops. Therefore, an RFA was performed and is contained in the
docket for this proposed rule. Information on the size of manufacturers
and distributors impacted by this rule is not available, but some small
entities among manufacturers and distributors may also be affected.
Several industry trade associations, including the Automotive
Service Association (ASA) that represents body shops, and the
Automotive Service Industry Association (ASIA) that represents coating
distributors, have submitted comments and provided information during
the development of the national rule. Most of the members of these
associations are small businesses. The main concerns of these
associations deal with recordkeeping and VOC content limits. Some
members of ASA are already subject to State rules that contain VOC
content limits and recordkeeping at the body shop. The drying times of
some coatings compliant with State rules are significantly longer than
those of conventional coatings, which can result in losses in body shop
productivity. Some shops report that the recordkeeping required under
some rules is burdensome and time consuming.
The proposed national rule applies to automobile refinish coating
manufacturers and importers only, not to body shops or any other users
of the coatings. After the national rule is effective, only compliant
coatings will be available for purchase by coating users in this
country. Since the purpose of most State recordkeeping requirements is
to demonstrate that body shops are using compliant coatings, some
States may decide to remove such requirements from their rules after
the national rule is effective.
Coatings compliant with the proposed rule do not take significantly
longer to dry than conventional coatings; therefore, small shops will
be able to apply compliant coatings without purchasing additional
equipment.
E. Unfunded Mandates Reform Act
Section 202 of the Unfunded Mandates Reform Act of 1995 (``Unfunded
Mandates Act'') (signed into law on March 22, 1995) requires that the
Agency prepare a budgetary impact statement to accompany any proposed
or final rule that includes a Federal mandate that may result in
expenditure by State, local, and tribal governments, in the aggregate,
or by the private sector, of $100 million or more in any one year.
Section 203 requires the Agency to establish a plan for obtaining input
from and informing, educating, and advising any small governments that
may be significantly or uniquely affected by the rule.
Under section 205 of the Unfunded Mandates Act, the Agency must
identify and consider a reasonable number of regulatory alternatives
before promulgating a rule for which a budgetary impact statement must
be prepared. The Agency must select from those alternatives the least
costly, most cost-effective, or least burdensome alternative that
achieves the objectives of the rule, unless the Agency explains why
this alternative is not selected or the selection of this alternative
is inconsistent with law.
Because the proposed rule is estimated to result in expenditure by
State, local, and tribal governments or the private sector of less than
$100 million in any one year, the Agency has not prepared a budgetary
impact statement or specifically addressed the selection of the least
costly, most cost-effective, or least burdensome alternative. Because
small governments will not be significantly or uniquely affected by
this rule, the Agency is not required to develop a plan with regard to
small governments.
List of Subjects in 40 CFR Part 59
Environmental protection, Air pollution control, Automobile
refinish coatings, Consumer and commercial products, Ozone, Volatile
organic compound.
Dated: April 19, 1996.
Carol M. Browner,
Administrator.
[FR Doc. 96-10381 Filed 4-29-96; 8:45 am]
BILLING CODE 6560-50-P
This is a copy of a public record, reproduced as it was published. It is not legal advice, and it may not be the version a court would rely on. Check the official source before you cite it.