[Federal Register Volume 70, Number 176 (Tuesday, September 13, 2005)]
[Rules and Regulations]
[Pages 53930-53935]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 05-18016]



[[Page 53930]]

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ENVIRONMENTAL PROTECTION AGENCY

40 CFR Parts 51 and 52

[OAR-2003-0200; FRL-7966-2]
RIN 2060-AM98


Revisions to the California State Implementation Plan and 
Revision to the Definition of Volatile Organic Compounds (VOC)--Removal 
of VOC Exemptions for California's Aerosol Coating Products Reactivity-
based Regulation

AGENCY: Environmental Protection Agency (EPA).

ACTION: Final rule.

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SUMMARY: The EPA is finalizing approval of a new consumer products 
regulation as part of the California State Implementation Plan (SIP) 
for ozone under the Clean Air Act (CAA) as amended in 1990. This 
California regulation adopts a new approach to reducing ozone formation 
from volatile organic compounds (VOC) in aerosol coating products. The 
EPA is also approving the use of California's Tables of Maximum 
Incremental Reactivity (MIR) to allow implementation of their rule. 
This action also revises EPA's definition of VOCs so that compounds 
which we previously identified as negligibly reactive and exempt from 
EPA's regulatory definition of VOCs now count towards a product's 
reactivity-based VOC limit for the purpose of California's aerosol 
coatings regulation. These revisions were previously proposed in the 
Federal Register on January 7, 2005 (70 FR 1640) and are expected to 
help in California's efforts to attain the National Ambient Air Quality 
Standards (NAAQS) for ozone.

DATES: This final rule is effective on October 13, 2005.

ADDRESSES: The EPA has established a docket for this action under 
Docket ID No. OAR-2003-0200. All documents in the docket are listed in 
the EDOCKET index at http://www.epa.gov/edocket. Although listed in the 
index, some information is not publicly available, i.e., Confidential 
Business Information (CBI) or other information whose disclosure is 
restricted by statute. Certain other material, such as copyrighted 
material, is not placed on the Internet and will be publicly available 
only in hard copy form. Publicly available docket materials are 
available either electronically in EDOCKET or in hard copy at the 
Revisions to the California State Implementation Plan Docket, Docket ID 
No. OAR-2003-0200, EPA/DC, EPA West, Room B102, 1301 Constitution Ave., 
NW., Washington, DC. The Public Reading Room is open from 8:30 a.m. to 
4:30 p.m., Monday through Friday, excluding legal holidays. The 
telephone number for the Public Reading Room is (202) 566-1744, and the 
telephone number for the Air Docket is (202) 566-1742.

FOR FURTHER INFORMATION CONTACT: Stanley Tong, Rulemaking Office, (AIR-
4), Environmental Protection Agency, Region IX, 75 Hawthorne St., San 
Francisco, CA 94105; telephone number: (415) 947-4122; fax number: 
(415) 947-3579; e-mail address: <a href="/cdn-cgi/l/email-protection#44302b2a236a3730252a28213d042134256a232b32"><span class="__cf_email__" data-cfemail="493d26272e673a3d2827252c30092c3928672e263f">[email protected]</span></a>.

SUPPLEMENTARY INFORMATION:

I. General Information

A. Does This Action Apply to Me?

    This action applies to persons that sell, supply, offer for sale, 
apply, or manufacture for use in California, any aerosol coating, 
aerosol clear coating and aerosol stain product subject to the limits 
in California's Aerosol Coating Products regulation. The regulation 
prohibits the commercial application of non-complying aerosol coating 
products.

B. Throughout This Document, ``We,'' ``Us'' and ``Our'' Refer to EPA

C. Submitted Regulations

    On January 7, 2005 (70 FR 1640), EPA proposed to approve the 
following regulations into the California SIP.

                     Table 1.--Submitted Regulations
------------------------------------------------------------------------
               Regulation title                   Adopted     Submitted
------------------------------------------------------------------------
Aerosol Coating Products......................     5/1/2001    3/13/2002
Tables of Maximum Incremental Reactivities         5/1/2001    3/13/2002
 (MIR) Values.................................
------------------------------------------------------------------------

    We proposed to approve these regulations because we determined that 
they complied with the relevant CAA requirements. We also proposed to 
change our definition of VOCs so that compounds which we previously 
identified as negligibly reactive and exempt from EPA's regulatory 
definition of VOCs will now count towards a product's reactivity-based 
VOC limit for the purpose of California's aerosol coatings regulation. 
The January 7, 2005 proposed action contains more information on the 
California Air Resources Board's (CARB's) regulations and our 
evaluation.

D. Outline

    The information in this preamble is organized as follows:

I. Background Information
    A. What is Photochemical Reactivity?
    B. What Does CARB's Regulation Do?
II. Response to Major Comments
    A. Comments Supporting the Proposed Approval
    B. Response to Questions Posed by EPA in the Proposal
    C. Comments Asking EPA to Update and Expand its Reactivity 
Policy
III. Final Action
IV. Statutory and Executive Order Reviews

I. Background Information

A. What Is Photochemical Reactivity?

    There are thousands of individual species of VOC chemicals that can 
combine with nitrogen oxides (NO<INF>X</INF>) and the energy from 
sunlight to form ozone. The impact of a given VOC on formation of 
ground-level ozone is sometimes referred to as its ``reactivity.'' It 
is generally understood that not all VOCs are equal in their effects on 
ground-level ozone formation. Some VOCs react extremely slowly and 
changes in their emissions have limited effects on ozone pollution 
episodes. Some VOCs form ozone more quickly, or they may form more 
ozone than other VOCs. Others not only form ozone themselves, but also 
enhance ozone formation from other VOCs. By distinguishing between more 
reactive and less reactive VOCs, however, it should be possible to 
decrease ozone concentrations further or more efficiently than by 
controlling all VOCs equally.
    Assigning a value to the reactivity of a compound is a complex 
undertaking. Reactivity is not simply a property of the compound 
itself; it is a property of both the compound and the environment in 
which the compound is found. The reactivity of a single compound varies 
with VOC-NO<INF>X</INF> ratios, meteorological conditions, the mix of 
other VOCs in the atmosphere, and the time interval of interest. 
Designing an effective regulation that takes account of these 
interactions is difficult, and implementing and enforcing such a 
regulation carries the extra burden of characterizing and tracking the 
full chemical composition of VOC emissions. The January 7, 2005 
proposal (70 FR 1640) contains additional background information on 
photochemical reactivity. Recently, EPA has issued guidance to States 
regarding the use of VOC reactivity information in the development of 
ozone control measures. This guidance is published elsewhere in today's 
Federal Register.

[[Page 53931]]

B. What Does CARB's Regulation Do?

    The CARB has been exploring the use of reactivity-based regulations 
since the early 1990s as a means of achieving further ozone reductions. 
For example, in 1991, the CARB incorporated a reactivity scale for 
weighting vehicle emissions of individual VOC species in their low 
emitting vehicle and clean fuels regulation. In 2001, the CARB adopted 
an aerosol coatings regulation \1\ that set reactivity-based VOC limits 
for six general coating categories and 29 speciality coating 
categories. The reactivity-based limits for the general coatings took 
effect on June 1, 2002 and the limits for the speciality coatings took 
effect on January 1, 2003. The CARB had previously controlled VOC 
emissions from aerosol coatings in California by limiting the mass of 
VOCs in the product, with limits expressed as maximum allowable percent 
of mass of VOC. The CARB's new approach incorporates the concept of VOC 
photochemical reactivity. This concept relies on the fact that the same 
weight/amount of some VOCs (e.g., xylene) has the potential to form 
more ozone, or to form ozone more quickly, than the same weight/amount 
of other VOCs (e.g., propane) once they are emitted into the ambient 
air under the same conditions. The EPA's action to approve CARB's 
regulation into the SIP enables CARB to include the ozone reductions 
achieved by their aerosol coatings regulation into their State SIP 
plan.
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    \1\ http:www.arb.ca.gov/colsprod/reg/apt.pdf or Title 17, 
California Code of Regulations, Division 3, Chapter 1, Subchapter 
8.5, Article 3.
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    The CARB's aerosol coatings regulation applies to aerosol coatings, 
aerosol clear coatings and aerosol stains. It applies to any person who 
sells, supplies, offers for sale, applies or manufactures for use in 
California any aerosol coating subject to the limits in the regulation. 
The regulation prohibits the commercial application of non-complying 
aerosol coating products.
    All aerosol coating products covered by the CARB's regulation were 
required to meet the new reactivity-based limits by January 1, 2003. 
The regulation contains a sell-through provision whereby products 
manufactured prior to the effective date of the regulation could be 
sold, supplied, offered for sale, or applied up to 3 years after that 
date.
    The CARB believes that some VOC mass-based limits in the previous 
version of their rule presented particularly difficult reformulation 
challenges for manufacturers of water-based coatings, and the State 
concluded that it may not be feasible to achieve additional VOC 
reductions from a traditional VOC mass-based program. The CARB hopes to 
target VOC emissions reductions to better control a product's 
contribution to ozone formation by encouraging reductions of higher 
reactivity VOCs, rather than by treating all VOCs in a product alike 
through a mass-based rule. The submitted regulation, therefore, 
consists of reactivity-based limits that replace the existing mass-
based VOC limits for aerosol spray coatings.
    To discriminate among VOCs, the CARB has used a version of the MIR 
scale (W. P. L. Carter, ``Development of Ozone Reactivity Scales for 
Volatile Organic Compounds,'' Journal of the Air and Waste Management 
Association, 44, p.881-899, July 1994.) The MIR scale is designed using 
certain assumptions about meteorological and environmental conditions 
where ozone production is most sensitive to changes in hydrocarbon 
emissions and, therefore, is intended to represent conditions where VOC 
emission controls will be most effective. The MIR scale is expressed as 
grams of ozone formed per gram of organic compound reacted. Each 
compound is assigned an individual MIR value, which enables the 
reactivities of different compounds to be compared quantitatively. 
Individual MIR values now exist for many commonly used compounds, and a 
list of these individual values comprises a scale. Today's action 
approves into the SIP, the CARB's reactivity-weighted emission limits 
and the associated MIR scale.
    The EPA believes that reactivity-based approaches such as the one 
developed by the CARB can be more efficient and effective than 
traditional approaches that do not distinguish among VOCs based on 
reactivity. In particular, reactivity-based approaches may be useful in 
areas where significant VOC emission controls are already in place and 
further mass-based emissions reductions may be difficult or very 
expensive to achieve. In such situations, regulations that distinguish 
between individual VOCs and create an incentive to shift production and 
use from more reactive VOCs to less reactive VOCs may provide the 
flexibility necessary to continue progress towards attainment of the 
ozone NAAQS.
    To support the CARB's aerosol coating reactivity-based program, EPA 
is modifying our regulatory definition of VOC under 40 CFR 51.100(s) so 
that compounds previously excluded from the definition of VOC will now 
be counted towards a product's reactivity-based VOC limit for the 
limited purpose of the CARB's regulation.

II. Response to Major Comments

    In our proposal to approve the CARB's aerosol coatings reactivity-
based regulation and associated MIR tables into the SIP, and to change 
our definition of VOC, EPA indicated that interested parties could 
request that EPA hold a public hearing on the proposed action. The EPA 
received no requests for a public hearing.
    The EPA also provided for a 60-day public comment period in the 
proposal. We received six comment letters. One letter was submitted 
from a regulatory agency and five letters were submitted from industry 
and trade associations. The major comments fell into 3 categories: (1) 
Comments supporting the proposed approval, (2) Response to questions 
posed by EPA in the proposal, and (3) Comments asking EPA to update and 
expand its reactivity policy. All comment letters are contained in the 
docket (OAR-2003-0200) for this action. In today's final action, we 
have summarized the significant comments and provided the Agency's 
responses.

A. Comments Supporting the Proposed Approval

    Comment: All six comment letters supported the approval of the 
CARB's reactivity-based regulation into the SIP.
    One commenter (84-1-2) stated that reactivity-based regulations for 
consumer products, where technologically feasible, were a more 
effective form of regulation. Another commenter (87-2-4) stated the 
approval provided the aerosol coatings industry with a relatively 
stable and reliable regulatory arena at least in the State of 
California and further indicated (87-2-5) that the CARB had already 
taken steps to make sure the reactivity-based regulatory program 
remained enforceable and scientifically accurate by updating the MIR 
tables in December 2003.
    Response: This final rulemaking approves the CARB's aerosol 
coatings reactivity-based regulation into the SIP.

B. Response to Questions Posed by EPA in the Proposal

    The EPA requested comments on the following areas in the proposed 
rule: how reactivity-based programs might affect industry compliance 
(e.g., compliance testing) and recordkeeping costs; and how industry 
and regulatory agency costs and staff requirements might change with 
respect to detailed emission inventories, manufacturing or material 
costs, product quality and price.
    Comment: Two commenters (82-2-1) and (85-3-4) stated the MIR 
concept

[[Page 53932]]

allows formulators greater flexibility and cost effectiveness in 
meeting regulatory requirements, and that the simplicity of determining 
MIR values for hydrocarbon solvents creates the incentive for the 
substitution and use of solvents with relatively low contribution to 
ozone formation in aerosol coating applications.
    One commenter (85-2-5) stated that reactivity-based regulations in 
general do not present significant or insurmountable problems regarding 
enforceability. This commenter stated that while calculating a product 
weighted average MIR is arithmetically slightly more complex than 
simply adding up the percent of each ingredient classified as a VOC, 
this slight increase in complexity does not deter enforceability 
determinations, which were primarily based on the product formulations.
    The commenter (85-3-3) further stated that there was nothing 
inherent in reactivity-based regulations that should unreasonably 
increase industry costs and that in both mass-based and reactivity-
based cases, industry needed to keep records and the most significant 
costs were in the research and development process to develop and 
assess new product formulation technologies.
    Another commenter (87-3-1) stated that quantifying compliance and 
recordkeeping costs relative to the implementation of a regulation was 
a difficult task for large, medium and small members of the industry 
and there were significant obstacles to gathering this type of 
information. Consequently, they stated they were unable to respond with 
any accurate data at this time without further clarification on the 
exact level of data needs.
    Response: From the industry and trade associations responses, EPA 
concludes that in general, industry compliance and recordkeeping costs 
are not expected to be significantly different between mass-based and 
reactivity-based regulations and that generally, expenditures for 
formulation and research and development efforts exceed expenditures 
for compliance determination.
    The EPA's concern in posing this question was whether reactivity-
based programs resulted in a significant increase in compliance 
determination costs. This does not appear to be the case for industry, 
however, we are unsure of the potential impact on regulatory agencies 
since we did not receive any replies from regulatory agencies on this 
question. We believe that because reactivity-based programs rely on 
identifying and quantifying all the individual VOC ingredients in a 
coating to determine compliance, it appears reasonable to conclude that 
they can be more complex and costly than the traditional ``bake and 
weigh'' method employed in EPA Method 24 to determine compliance with a 
mass-based VOC limit. We recognize that some regulatory agencies such 
as the CARB have extensive laboratory capabilities and capable staff to 
conduct the required analysis using gas chromatography, however other 
States and local regulatory agencies may not have these capabilities 
and may need to investigate acquiring these resources and skills before 
developing their own reactivity-based regulations to ensure their 
programs are enforceable and have the opportunity to succeed.

C. Comments Asking EPA To Update and Expand Its Reactivity Policy

    Comment: One commenter (83-3-2) believed EPA should encourage other 
States to evaluate opportunities to incorporate reactivity-based 
approaches into their VOC emissions and ozone control regulatory 
programs, and should not limit the use of photochemical reactivity to 
situations where further mass-based limits are difficult to achieve. 
The commenter further urged EPA to state clearly that the technical 
support provided by California would not necessarily represent what 
would be required in each case to support a reactivity-based approach.
    Another commenter (85-2-4) stated that scientific studies provide a 
clear picture that both VOC mass and reactivity should be considered in 
ozone control strategies. This commenter also indicated that while 
reactivity reductions may not be appropriate for many consumer products 
or some other sources of VOC emissions, for some sources, reactivity 
reductions will represent the most cost-effective way to reduce ozone 
formation. The commenter (85-3-5) further stated that EPA should update 
and broaden its policies regarding reactivity and ozone attainment and 
(85-4-1) urged EPA to initiate a scientific-based policy review of its 
ozone attainment strategies to assure that the latest scientific 
studies are incorporated to encourage the most effective, and cost-
effective control strategies.
    Another commenter (87-3-2) stated that it was important that the 
Federal agency charged with stewardship over environmental issues be 
receptive to reactivity-based regulations. They further stated that 
many of the consumer products that could be addressed in this 
rulemaking have been regulated several times already and that further 
efforts to lower the mass-based VOC limits could be impossible without 
seriously altering the performance characteristics of the product or 
eliminating it from the marketplace altogether.
    Response: Recently, EPA has issued interim guidance to States, 
which is published elsewhere in today's Federal Register encouraging 
them to consider recent scientific information on VOC reactivity in the 
development of ozone control measures. This interim guidance summarizes 
recent scientific findings, provides examples of innovative 
applications of reactivity information in the development of VOC 
control measures, and clarifies the relationship between innovative 
reactivity-based policies and EPA's current definition of VOC at 40 CFR 
51.100(s). The EPA will continue to work with the CARB and other 
interested parties through the Reactivity Research Working Group (RRWG) 
(http://www.cgenv.com/Narsto/reactinfo.html) to improve the scientific 
foundation of VOC reactivity-based regulations. The EPA will update its 
guidance to States as new information becomes available.

III. Final Action

    By this final rulemaking, EPA is approving: the CARB's aerosol 
coatings reactivity-based regulation and associated MIR tables into the 
SIP; the use of the CARB Method 310 to determine compliance with the 
CARB's reactivity-based regulation, granting SIP credit for the 
equivalent mass-based reductions achieved by the CARB's regulation, and 
modifying our regulatory definition of VOC at 40 CFR 51.100(s) to 
support the CARB's regulation.

IV. Statutory and Executive Order Reviews

A. Executive Order 12866: Regulatory Planning and Review

    Under Executive Order 12866 (58 FR 51735; October 4, 1993), the 
Agency must determine whether the regulatory action is ``significant'' 
and therefore subject to the Office of Management and 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;

[[Page 53933]]

    (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.
    For the change in definition of VOCs, EPA has determined that this 
final rulemaking is not a ``significant regulatory action'' under the 
terms of Executive Order 12866 and is therefore not subject to the OMB 
review. For the approval of the CARB's rule into the SIP, the OMB has 
exempted this regulatory action from Executive Order 12866 review.

B. Paperwork Reduction Act

    For the change in the definition of VOCs, this action does not 
impose an information collection burden under the provisions of the 
Paperwork Reduction Act, 44 U.S.C. 3501 et seq. The change in the 
definition of VOCs only reinstates, for the purposes of determining 
compliance with California's aerosol coatings rule, compounds which 
were previously exempted from the definition of VOC. The change in the 
definition of VOCs does not impose any information collection 
requirements.
    For the approval of the CARB's regulation into the SIP, this final 
rulemaking does not contain any information collection requirements 
that would require any person to provide information to EPA, however 
the CARB's regulation contain requirements for the aerosol coating 
industry to provide information to the CARB.
    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.
    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 number. The OMB control numbers for EPA's 
regulations in 40 CFR are listed in 40 CFR part 9.

C. Regulatory Flexibility Act (RFA)

    The EPA has determined that it is not necessary to prepare a 
regulatory flexibility analysis in connection with this final rule.
    For purposes of assessing the impacts of today's rule on small 
entities, small entity is defined as: (1) A small business as defined 
by the Small Business Administration's regulations at 13 CFR 121.201; 
(2) a small governmental jurisdiction that is a government of a city, 
county, town, school district or special district with a population of 
less than 50,000; and (3) a small organization that is any not-for-
profit enterprise which is independently owned and operated and is not 
dominant in its field.
    After considering the economic impacts of today's final rule on 
small entities, EPA has concluded that this action will not have a 
significant economic impact on a substantial number of small entities. 
This final action will not impose any requirements on small entities.
    SIP approvals under section 110 and subchapter I, part D of the CAA 
do not create any new requirements but simply act on requirements that 
the State is already imposing.

D. Unfunded Mandates Reform Act

    Title II of the Unfunded Mandates Reform Act of 1995 (UMRA), Public 
Law 104-4, establishes requirements for Federal agencies to assess the 
effects of their regulatory actions on State, local, and Tribal 
governments and the private sector. Under section 202 of the UMRA, EPA 
generally must prepare a written statement, including a cost-benefit 
analysis, for proposed and final rules with ``Federal mandates'' that 
may result in expenditures by State, local, and Tribal governments, in 
the aggregate, or the private sector, of $100 million or more in any 1 
year. Before promulgating an EPA rule for which a written statement is 
needed, section 205 of the UMRA generally requires EPA to identify and 
consider a reasonable number of regulatory alternatives and adopt the 
least costly, most cost-effective or least burdensome alternative that 
achieves the objectives of the rule. The provisions of section 205 do 
not apply when they are inconsistent with applicable law. Moreover, 
section 205 allows EPA to adopt an alternative other than the least 
costly, most cost-effective or least burdensome alternative if the 
Administrator publishes with the final rule an explanation why that 
alternative was not adopted. Before EPA establishes any regulatory 
requirements that may significantly or uniquely affect small 
governments, including Tribal governments, it must have developed under 
section 203 of UMRA a small government agency plan. The plan must 
provide for notifying potentially affected small governments, enabling 
officials of affected small governments to have meaningful and timely 
input in the development of EPA regulatory proposals with significant 
Federal intergovernmental mandates, and informing, educating, and 
advising small governments on compliance with the regulatory 
requirements.
    For the change in the definition of VOCs, today's rulemaking 
contains no Federal mandates (under the regulatory provisions of title 
II of the UMRA) for State, local, or Tribal governments or the private 
sector.
    For the approval of the CARB's regulation into the SIP, EPA has 
determined that the approval action does not include a Federal mandate 
that may result in estimated costs of $100 million or more to either 
State, local, or Tribal governments in the aggregate, or to the private 
sector. This Federal action approves pre-existing requirements under 
State or local law, and imposes no new requirements. Accordingly, no 
additional costs to State, local, or Tribal governments, or to the 
private sector, result from this action.
    Thus, today's rule is not subject to the requirements of sections 
202 and 205 of the UMRA.
    In addition, EPA has determined that this rule contains no 
regulatory requirements that might significantly or uniquely affect 
small governments in accordance with section 203 of the UMRA.

E. Executive Order 13132: Federalism

    Executive Order 13132, entitled ``Federalism'' (64 FR 43255, August 
10, 1999), requires EPA to develop an accountable process to ensure 
``meaningful and timely input by State and local officials in the 
development of regulatory policies that have federalism implications.'' 
``Policies that have federalism implications'' is defined in the 
Executive Order to include regulations that have ``substantial direct 
effects on the States, on the relationship between the national 
government and the States, or on the distribution of power and 
responsibilities among the various levels of government.''
    This final rulemaking does not have federalism implications. It 
will not have substantial direct effects on the States, on the 
relationship between the national

[[Page 53934]]

government and the States, or on the distribution of power and 
responsibilities among the various levels of government, as specified 
in Executive Order 13132. Today's final rulemaking does not impose any 
new mandates on State or local governments. The change to the 
definition of VOCs merely assists the CARB in implementing its aerosol 
coatings reactivity regulation. The approval of this regulation into 
the SIP acts on a State regulation implementing a Federal standard, and 
does not alter the relationship or the distribution of power and 
responsibilities established in the CAA. Thus, Executive Order 13132 
does not apply to this rule.

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

    Executive Order 13175, entitled ``Consultation and Coordination 
with Indian Tribal Governments'' (65 FR 67249, November 9, 2000), 
requires EPA to develop an accountable process to ensure ``meaningful 
and timely input by tribal officials in the development of regulatory 
policies that have tribal implications.'' This final rule does not have 
Tribal implications, as specified in Executive Order 13175. The change 
to the definition of VOCs merely assists the CARB in implementing its 
aerosol coatings reactivity regulation and does not impose any direct 
compliance costs. The approval of the CARB's regulation into the SIP 
acts on a State regulation and does not alter the relationship between 
the Federal government and Indian Tribes, as specified in Executive 
Order 13175. Thus, Executive Order 13175 does not apply to this rule.

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

    Executive Order 13045: ``Protection of Children from Environmental 
Health and Safety Risks'' (62 FR 19885, April 23, 1997) applies to any 
rule that: (1) Is determined to be ``economically significant'' as 
defined under Executive Order 12866, and (2) concerns an environmental 
health or safety risk that EPA has reason to believe may have a 
disproportionate effect on children. If the regulatory action meets 
both criteria, the Agency must evaluate the environmental health or 
safety effects of the planned rule on children, and explain why the 
planned regulation is preferable to other potentially effective and 
reasonably feasible alternatives considered by the Agency.
    While this final action is not subject to the Executive Order 
because it is not economically significant as defined in Executive 
Order 12866, we have reason to believe that ozone has a 
disproportionate effect on active children who play outdoors. (See 62 
FR 38856 and 38859; July 18, 1997). However, we do not expect today's 
approval of the CARB's regulation into the SIP to result in an adverse 
impact, as it is intended to at least achieve the same ozone reductions 
as the mass-based limits they supplant. Also, we do not expect today's 
change to the definition of VOC to result in any adverse impact, 
because it increases the number of compounds subject to regulation as 
VOCs for the purpose of California's aerosol coatings reactivity-based 
regulation.

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

    This rule is not subject to Executive Order 13211, ``Actions 
Concerning Regulations That Significantly Affect Energy Supply, 
Distribution, or Use'' (66 FR 28355, May 22, 2001) because it is not a 
significant regulatory action under Executive Order 12866.

I. National Technology Transfer Advancement Act

    As noted in the proposed rule, section 12(d) of the National 
Technology Transfer and Advancement Act of 1995 (``NTTAA''), Public Law 
No. 104-113, 12(d) (15 U.S.C. 272 note) directs EPA to use voluntary 
consensus standards in its regulatory activities unless to do so would 
be inconsistent with applicable law or otherwise impractical. Voluntary 
consensus standards are technical standards (e.g., materials 
specifications, test methods, sampling procedures, and business 
practices) that are developed or adopted by voluntary consensus 
standards bodies. The NTTAA directs EPA to provide Congress, through 
OMB, explanations when the Agency decides not to use available and 
applicable voluntary consensus standards.
    For the change in definition of VOCs, this final rulemaking does 
not involve technical standards. Therefore, EPA did not consider the 
use of any voluntary consensus standards. For the approval of the 
CARB's regulation into the SIP, the State regulation references 
standard test methods and makes modifications to methods adopted by the 
American Society for Testing and Materials (ASTM) D3074-94, D3063-94, 
and D2879-97 to support the regulatory objectives. These ASTM methods 
can be obtained through the ASTM Web site at: http://www.astm.org.

J. Congressional Review Act

    The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the 
Small Business Regulatory Enforcement Fairness Act of 1996, generally 
provides that before a rule may take effect, the agency promulgating 
the rule must submit a rule report, which includes a copy of the rule, 
to each House of the Congress and to the Comptroller General of the 
United States. The EPA will submit a report containing this rule and 
other required information to the U.S. Senate, the U.S. House of 
Representatives, and the Comptroller General of the United States prior 
to publication of the rule in the Federal Register. A major rule cannot 
take effect until 60 days after it is published in the Federal 
Register. This action is not a ``major rule'' as defined by 5 U.S.C. 
804(2). This rule will be effective 30 days after publication in the 
Federal Register.

K. Petitions for Judicial Review

    Under section 307(b)(1) of the CAA, petitions for judicial review 
of this action must be filed in the United States Court of Appeals for 
the appropriate circuit by November 14, 2005. Filing a petition for 
reconsideration by the Administrator of this final rule does not affect 
the finality of this rule for the purposes of judicial review nor does 
it extend the time within which a petition for judicial review may be 
filed, and shall not postpone the effectiveness of such rule or action. 
This action may not be challenged later in proceedings to enforce its 
requirements. [See section 307(b)(2)].

List of Subjects

40 CFR Part 51

    Environmental protection, Administrative practice and procedure, 
Air pollution control, Carbon monoxide, Intergovernmental relations, 
Lead, Nitrogen dioxide, Ozone, Particulate matter, Reporting and 
recordkeeping requirements, Sulfur oxides, Volatile organic compound.

40 CFR Part 52

    Environmental protection, Air pollution control, Intergovernmental 
relations, Ozone, Reporting and recordkeeping requirements, Volatile 
organic compound.

    Authority: 42 U.S.C. 7401 et seq.

    Dated: September 2, 2005.
Stephen L. Johnson,
Administrator.

0
Parts 51 and 52, Chapter I, title 40 of the Code of Federal Regulations 
are amended as follows:

[[Page 53935]]

PART 51--[AMENDED]

0
1. The authority citation for Part 51 continues to read as follows:

    Authority: 23 U.S.C. 101; 42 U.S.C. 7401-7671q.


0
2. Section 51.100 is amended by adding paragraph (s)(6) to read as 
follows:


Sec.  51.100  Definitions.

* * * * *
    (s) * * *
    (6) For the purposes of determining compliance with California's 
aerosol coatings reactivity-based regulation, (as described in the 
California Code of Regulations, Title 17, Division 3, Chapter 1, 
Subchapter 8.5, Article 3), any organic compound in the volatile 
portion of an aerosol coating is counted towards that product's 
reactivity-based limit. Therefore, the compounds identified in 
paragraph (s) of this section as negligibly reactive and excluded from 
EPA's definition of VOCs are to be counted towards a product's 
reactivity limit for the purposes of determining compliance with 
California's aerosol coatings reactivity-based regulation.
* * * * *

PART 52--[AMENDED]

0
1. The authority citation for part 52 continues to read as follows:

    Authority: 42 U.S.C. 7401 et seq.

Subpart F--California

0
2. Section 52.220 is amended by adding paragraph (c)(338) to read as 
follows:


Sec.  52.220  Identification of plan.

* * * * *
    (c) * * *
    (338) New and amended regulations for the following agency were 
submitted on March 13, 2002, by the Governor's designee.
    (i) Incorporation by reference.
    (A) California Air Resources Board.
    (1) California Code of Regulations, Title 17, Division 3, Chapter 
1, Subchapter 8.5, Consumer Products, Article 3, Aerosol Coating 
Products, Sections 94520 to 94528, and Subchapter 8.6, Maximum 
Incremental Reactivity, Article 1, Tables of Maximum Incremental 
Reactivity (MIR) Values, Sections 94700 to 94701, both adopted on May 
1, 2001.
* * * * *
[FR Doc. 05-18016 Filed 9-12-05; 8:45 am]
BILLING CODE 6560-50-P


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