Air Quality: Revision to Definition of Volatile Organic Compounds-Exclusion of 2,3,3,3-tetrafluoropropene, 62451-62455 [2013-23783]
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Federal Register / Vol. 78, No. 204 / Tuesday, October 22, 2013 / Rules and Regulations
use, except as noted in paragraph (a)(3)
of this section.
(iii) Manufacturing (including
importing) or processing of any
chemical substance listed in Table 3 of
paragraph (a)(1) of this section for any
use, except as noted in paragraphs (a)(3)
through (5) of this section.
(iv) Manufacturing (including
importing) or processing of any
chemical substance listed in Table 4 of
paragraph (a)(1) of this section for any
use.
(3) Manufacturing (including
importing) or processing of any
chemical substance listed in Table 2 and
Table 3 of paragraph (a)(1) of this
section for the following specific uses
shall not be considered as a significant
new use subject to reporting under this
section:
(i) Use as an anti-erosion additive in
fire-resistant phosphate ester aviation
hydraulic fluids.
(ii) Use as a component of a
photoresist substance, including a photo
acid generator or surfactant, or as a
component of an anti-reflective coating,
used in a photomicrolithography
process to produce semiconductors or
similar components of electronic or
other miniaturized devices.
(iii) Use in coating for surface tension,
static discharge, and adhesion control
for analog and digital imaging films,
papers, and printing plates, or as a
surfactant in mixtures used to process
imaging films.
(iv) Use as an intermediate only to
produce other chemical substances to be
used solely for the uses listed in
paragraph (a)(3)(i), (ii), or (iii) of this
section.
(4) Manufacturing (including
importing) or processing of
tetraethylammonium
perfluorooctanesulfonate (CAS No.
56773–42–3) for use as a fume/mist
suppressant in metal finishing and
plating baths shall not be considered as
a significant new use subject to
reporting under this section. Examples
of such metal finishing and plating
baths include: Hard chrome plating;
decorative chromium plating; chromic
acid anodizing; nickel, cadmium, or
lead plating; metal plating on plastics;
and alkaline zinc plating.
(5) Manufacturing (including
importing) or processing of: 1Pentanesulfonic acid, 1,1,2,2,3,3,4,4,5,5,
5-undecafluoro-, potassium salt (CAS
No. 3872–25–1); Glycine, N-ethyl-N[(tridecafluorohexyl)sulfonyl]-,
potassium salt (CAS No. 67584–53–6);
Glycine, N-ethyl-N[(pentadecafluoroheptyl)sulfonyl]-,
potassium salt (CAS No. 67584–62–7);
1-Heptanesulfonic acid, 1,1,2,2,3,3,4,4,
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5,5,6,6,7,7,7-pentadecafluoro-,
ammonium salt (CAS No. 68259–07–4);
1-Heptanesulfonamide, N-ethyl-1,1,2,2,
3,3,4,4,5,5,6,6,7,7,7-pentadecafluoro(CAS No. 68957–62–0); Poly(oxy-1,2ethanediyl), .alpha.-[2-[ethyl
[(pentadecafluoroheptyl)sulfonyl]
amino]ethyl]-.omega.-methoxy- (CAS
No. 68958–60–1); or 1-Hexanesulfonic
acid, 1,1,2,2,3,3,4,4,5,5,6,6,6tridecafluoro-, compd. with 2,2′iminobis[ethanol] (1:1) (CAS No. 70225–
16–0) for use as a component of an
etchant, including a surfactant or fume
suppressant, used in the plating process
to produce electronic devices shall not
be considered a significant new use
subject to reporting under this section.
*
*
*
*
*
■ 5. Add § 721.10536 to subpart E to
read as follows:
§ 721.10536 Long-chain perfluoroalkyl
carboxylate chemical substances.
(a) Definitions. The definitions in
§ 721.3 apply to this section. In
addition, the following definition
applies: Carpet means a finished fabric
or similar product intended to be used
as a floor covering. This definition
excludes resilient floor coverings such
as linoleum and vinyl tile.
(b) Chemical substances and
significant new uses subject to reporting.
(1) The chemical substances identified
below, where 5 < n < 21 or 6 < m < 21,
are subject to reporting under this
section for the significant new uses
described in paragraph (b)(2) of this
section.
(i) CF3(CF2)n-COO-M where M = H+ or
any other group where a formal
dissociation can be made;
(ii) CF3(CF2)n-CH = CH2;
(iii) CF3(CF2)n-C(=O)-X where X is any
chemical moiety;
(iv) CF3(CF2)m-CH2-X where X is any
chemical moiety; and
(v) CF3(CF2)m-Y-X where Y = non-S,
non-N heteroatom and where X is any
chemical moiety.
(2) The significant new use for
chemical substances identified in
paragraph (b)(1) of this section are:
Manufacture (including import) or
processing for use as part of carpets or
to treat carpets (e.g., for use in the carpet
aftercare market), except as noted in
paragraph (b)(3) of this section.
(3) Manufacture (including import) or
processing of the following two longchain perfluoroalkyl carboxylate
(LCPFAC) chemical substances for use
as a surfactant in aftermarket carpet
cleaning products shall not be
considered a significant new use subject
to reporting under this section:
(i) Phosphonic acid, perfluoro-C6-12alkyl derivs. (CAS No. 68412–68–0) and
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(ii) Phosphinic acid, bis(perfluoro-C6C12-alkyl) derivs. (CAS No. 68412–69–
1).
(c) Specific requirements. The
provisions of subpart A of this part
apply to this section except as modified
by this paragraph (c).
(1) Revocation of certain notification
exemptions. With respect to imports of
carpets, the provisions of § 721.45(f) do
not apply to this section. A person who
imports a chemical substance identified
in this section as part of a carpet is not
exempt from submitting a significant
new use notice. The other provision of
§ 721.45(f), respecting processing a
chemical substance as part of an article,
remains applicable.
(2) [Reserved]
[FR Doc. 2013–24651 Filed 10–21–13; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 51
[EPA–HQ–OAR–2010–0605; FRL–9900–53–
OAR]
RIN 2060–AR70
Air Quality: Revision to Definition of
Volatile Organic Compounds—
Exclusion of 2,3,3,3-tetrafluoropropene
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
The EPA is taking final action
to revise the regulatory definition of
volatile organic compounds (VOCs) for
purposes of preparing state
implementation plans (SIPs) to attain
the national ambient air quality
standards (NAAQS) for ozone under
title I of the Clean Air Act (CAA). This
final action adds 2,3,3,3tetrafluoropropene (also known as
HFO–1234yf) to the list of compounds
excluded from the regulatory definition
of VOCs on the basis that this
compound makes a negligible
contribution to tropospheric ozone
formation. As a result, if you are subject
to certain federal regulations limiting
emissions of VOCs, your emissions of
HFO–1234yf may not be regulated for
some purposes. This action may also
affect whether HFO–1234yf is
considered a VOC for state regulatory
purposes, depending on whether the
state relies on the EPA’s regulatory
definition of VOCs.
DATES: This rule is effective on
November 21, 2013.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
SUMMARY:
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No. EPA–HQ–OAR–2010–0605. All
documents in the docket are listed on
the www.regulations.gov Web site.
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, will be publicly
available only in hard copy. Publicly
available docket materials are available
either electronically in
www.regulations.gov or in hard copy at
the Docket ID No. EPA–HQ–OAR–2010–
0605, EPA/DC, EPA West, Room 3334,
1301 Constitution Avenue, Northwest,
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 and Radiation Docket
Information Center is (202) 566–1742.
For additional information about the
EPA’s public docket, visit the EPA
Docket Center homepage at: https://
www.epa.gov/epahome/dockets.htm.
FOR FURTHER INFORMATION CONTACT:
David Sanders, Office of Air Quality
Planning and Standards, Air Quality
Policy Division, Mail Code C539–01,
Research Triangle Park, NC 27711;
telephone: (919) 541–3356; fax number:
919–541–0824; email address:
sanders.dave@epa.gov.
SUPPLEMENTARY INFORMATION:
emcdonald on DSK67QTVN1PROD with RULES
I. General Information
A. Does this action apply to me?
Entities potentially affected by this
final rule include, but are not
necessarily limited to, states (typically
state air pollution control agencies) that
control VOCs; manufacturers, importers
or processors of this compound; and
industries involved in the manufacture
or servicing of automobiles or
automotive air conditioning systems.
This action has no substantial direct
effects on industry because it does not
impose any new mandates on these
entities, but, to the contrary, removes
HFO–1234yf from the regulatory
definition of VOCs. The use of this
compound is subject to restrictions
under the CAA and the Toxic
Substances Control Act (TSCA).
Specifically, the use of this compound
as an aerosol propellant, blowing agent,
or refrigerant, or any other use in which
it would substitute for
chlorofluorocarbons,
hydrochlorofluorocarbons or their
substitutes, is prohibited unless such
use has been approved under the
Significant New Alternatives Policy
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(SNAP) program (CAA § 612; 40 CFR 82
subpart G). The SNAP program has
issued a final approval for HFO–1234yf
only as a substitute for use in the motor
vehicle air conditioning end-use as a
replacement for ozone depleting
substances (76 FR 17488, March 29,
2011; revised at 77 FR 17344, March 26,
2012). Furthermore, any significant new
use of HFO–1234yf is subject to a
reporting requirement according to a
significant new use rule (SNUR)
established under TSCA (75 FR 65987,
October 27, 2010; proposed for
amendment at 78 FR 32617, May 31,
2013).
B. How is this preamble organized?
The information presented in this
preamble is organized as follows:
I. General Information
A. Does this action apply to me?
B. How is this preamble organized?
II. Background
A. The EPA’s VOC Exemption Policy
B. Petition To List HFO–1234yf as an
Exempt Compound
C. Contribution to Tropospheric Ozone
D. Health and Environmental Risks
III. Proposed Action and Response to
Comments
IV. Final Action
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
J. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low-Income
Populations
K. Congressional Review Act
L. Judicial Review
II. Background
A. The EPA’s VOC Exemption Policy
Tropospheric ozone, commonly
known as smog, is formed when VOCs
and nitrogen oxides (NOX) react in the
atmosphere in the presence of sunlight.
Because of the harmful health effects of
ozone, the EPA and state governments
limit the amount of VOCs that can be
released into the atmosphere. VOCs are
those organic compounds of carbon that
form ozone through atmospheric
photochemical reactions. Different
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VOCs have different levels of reactivity.
That is, they do not react to form ozone
at the same speed or do not form ozone
to the same extent. Some VOCs react
slowly or form less ozone; therefore,
changes in their emissions have less
and, in some cases, very limited effects
on local or regional ozone pollution
episodes. It has been the EPA’s policy
that organic compounds with a
negligible level of reactivity should be
excluded from the regulatory definition
of VOCs so as to focus VOC control
efforts on compounds that do
significantly increase ozone
concentrations. The EPA also believes
that exempting such compounds creates
an incentive for industry to use
negligibly reactive compounds in place
of more highly reactive compounds that
are regulated as VOCs. The EPA lists
compounds that it has determined to be
negligibly reactive in its regulations as
being excluded from the regulatory
definition of VOCs (40 CFR 51.100(s)).
Section 302(s) of the CAA specifies
that the EPA has the authority to define
the meaning of ‘‘VOC,’’ and hence what
compounds shall be treated as VOCs for
regulatory purposes. The policy of
excluding negligibly reactive
compounds from the regulatory
definition of VOCs was first set forth in
the ‘‘Recommended Policy on Control of
Volatile Organic Compounds’’ (42 FR
35314, July 8, 1977) and was
supplemented most recently with the
‘‘Interim Guidance on Control of
Volatile Organic Compounds in Ozone
State Implementation Plans’’ (Interim
Guidance) (70 FR 54046, September 13,
2005). The EPA uses the reactivity of
ethane as the threshold for determining
whether a compound has negligible
reactivity. Compounds that are less
reactive than, or equally reactive to,
ethane under certain assumed
conditions may be deemed negligibly
reactive and therefore suitable for
exemption from the regulatory
definition of VOCs. Compounds that are
more reactive than ethane continue to
be considered VOCs for regulatory
purposes and therefore are subject to
control requirements. The selection of
ethane as the threshold compound was
based on a series of smog chamber
experiments that underlay the 1977
policy.
The EPA has used three different
metrics to compare the reactivity of a
specific compound to that of ethane: (i)
The reaction rate constant (known as
kOH) with the hydroxyl radical (OH); (ii)
the maximum incremental reactivity
(MIR) on a reactivity per unit mass
basis; and (iii) the MIR expressed on a
reactivity per mole basis. If a compound
is equally or less reactive than ethane on
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any one of these three metrics, then
under the Interim Guidance it is
considered by the EPA to be negligibly
reactive in forming ozone. A full
description of each metric and how it is
derived can be found in the proposal
notice for this action (76 FR 64059,
October 17, 2011) and is not repeated
here.
B. Petition To List HFO–1234yf as an
Exempt Compound
Honeywell Inc. submitted a petition
to the EPA on June 29, 2009, requesting
that HFO–1234yf (CAS 754–12–1) be
exempted from VOC control based on its
low reactivity relative to ethane. The
petitioner indicated that HFO–1234yf
may be used as a refrigerant for
refrigeration and air-conditioning.
Honeywell also indicated that it expects
HFO–1234yf to be widely used as a
replacement for HFC–134a in motor
vehicle air-conditioners (MVAC), and
that it has been specifically developed
for this purpose. Honeywell asserts that
as a replacement for use in motor
vehicle air conditioners, there will be an
environmental advantage in that the
global warming potential (GWP) of
HFO–1234yf is 4, which is substantially
lower than the GWP for HFC–134a (100year GWP = 1430), which HFO–1234yf
is designed to replace.
emcdonald on DSK67QTVN1PROD with RULES
C. Contribution to Tropospheric Ozone
Detailed information on the ozone
reactivity of HFO–1234yf was presented
in the proposal notice for this action (76
FR 64059, October 17, 2011) and is
summarized here.
HFO–1234yf has a higher kOH value
than ethane, meaning that it initially
reacts more quickly in the atmosphere
than ethane. A molecule of HFO–1234yf
is also more reactive than a molecule of
ethane. However, a gram of HFO–1234yf
has the same reactivity as a gram of
ethane.
Under the Interim Guidance, if a
compound is equally or less reactive
than ethane on any one or more of the
three reactivity metrics, it is considered
by the EPA to be negligibly reactive in
forming ozone. The data submitted by
Honeywell support the conclusion that
the reactivity of HFO–1234yf is equal to
or lower than that of ethane on a mass
MIR basis. Thus, HFO–1234yf is eligible
for exemption from the regulatory
definition of VOCs under the terms of
the Interim Guidance.
The EPA has also considered the
results of a recent peer-reviewed study
of the increase in ozone that may occur
as a result of the substitution of HFO–
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1234yf for HFC–134a.1 The additional
information from this study shows that,
under the assumptions used in the air
quality modeling, the use of HFO–
1234yf would produce slightly more
ozone than continued use of HFC–134a,
but the increase is unlikely to have a
significant impact on local air quality.
The EPA believes the very small
increase (0.01 percent) in ozone
concentrations that may result from
encouraging the use of HFO–1234yf via
an exemption from the regulatory
definition of VOC does not constitute a
sufficient reason to depart from the
Interim Guidance’s reliance on MIR
comparisons to ethane as the basis for
approving VOC exemption requests.
In summary, the EPA believes that
this chemical qualifies as negligibly
reactive with respect to its contribution
to tropospheric ozone formation.
D. Health and Environmental Risks
The preamble to the proposal notice
for this action (76 FR 64059, October 17,
2011) provided background information
on the Premanufacture Notice (PMN)
and SNAP reviews of HFO–1234yf. This
information is summarized and updated
here.
After reviewing available information
and public comments regarding its
safety, health and environmental risks
and benefits under the SNAP program,
the EPA issued a final listing on March
29, 2011, for HFO–1234yf as an
acceptable substitute for use of ozone
depleting substances in MVAC, subject
to specific use conditions, in place of
CFC–12 and HFC–134a (76 FR 174888).2
In the SNAP review, the EPA found
that the use of HFO–1234yf in new
passenger vehicle and light-duty truck
MVAC systems, subject to the use
conditions, does not present a
significantly greater risk to human
health and the environment compared
to the currently approved MVAC
alternatives. The 2011 SNAP rule for
HFO–1234yf was amended on March
26, 2012, to incorporate by reference a
revised standard for connecting fittings
from SAE International (77 FR 17344).
Under the TSCA, the EPA in 2010
completed a pre-manufacture review for
HFO–1234yf and issued a SNUR (75 FR
65987, October 27, 2010). The 2010
1 D. Luecken, R. Waterland, S. Papasavva, K.
Taddonio, W. Hutzell, J. Rugh, and S. Andersen.
Ozone and TFA Impacts in North America from
Degradation of 2,3,3,3-Tetrafluoropropene (HFO–
1234yf), A Potential Greenhouse Gas Replacement.
Environ. Sci. Technol. 44, pp. 343–349. See 76 FR
64059 (October 17, 2011). See 76 FR 64059 (October
17, 2011) at 64062 for additional description of this
study and the EPA’s assessment of it.
2 HFC–134a, which is not an ozone depleting
substance, has already largely replaced CFC–12 in
motor vehicle air conditioners.
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SNUR for HFO–1234yf requires
significant new use notification to the
EPA at least 90 days before
manufacturing or processing for uses
beyond air conditioning in new
passenger cars and vehicles or
commercial servicing of new passenger
cars and vehicles originally designed for
HFO–1234yf. In particular, under the
2010 rule, notification is required before
HFO–1234yf can be sold directly to
consumers for the purpose of servicing
the MVAC system of their own vehicles.
During the notification period, the EPA
can take further action to prevent any
unreasonable risk. This precautionary
step was taken because of certain animal
exposure studies indicating toxicity,
and the possibility that consumers
might be exposed to levels of HFO–
1234yf that would cause an
unreasonable health risk. However,
based on information submitted
subsequent to the 2010 rule that in the
EPA’s view resolves the issue pertaining
to the potential risks from consumer
exposure that was present in 2010, the
EPA has proposed to amend the SNUR
for HFO–1234yf such that notification
would not be required prior to sale of
HFO–1234yf-containing consumer
products used to recharge the MVAC
systems in passenger cars and vehicles
originally designed for HFO–1234yf (78
FR 32617, May 31, 2013).
III. Proposed Action and Response to
Comments
Based on the mass MIR value for
HFO–1234yf being equal to or less than
that of ethane, the EPA proposed to find
that HFO–1234yf is ‘‘negligibly
reactive’’ and to exempt HFO–1234yf
from the regulatory definition of VOCs
at 40 CFR 51.100(s) (76 FR 64059,
October 17, 2011).3
There were two comments regarding
HFO–1234yf submitted to the docket
during the public comment period. One
comment was from the petitioner,
Honeywell. Another comment came
from the Alliance of Automobile
Manufacturers. Both comments were in
favor of exempting HFO–1234yf. The
EPA acknowledges the commenters’
support for the proposed action.
IV. Final Action
The EPA is taking final action to
approve the petition for exemption of
HFO–1234yf from the regulatory
definition of VOCs.
If an entity uses or produces HFO–
1234yf and is subject to the EPA
3 In this proposal, we also proposed to exempt
trans-1,3,3,3-tetrafluoropropene (also known as
HFO–1234ze) from the definition of VOC. We have
taken final action separately for HFO–1234ze on
that proposal. 77 FR 37610, June 22, 2012.
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regulations limiting the use of VOC in
a product other than an aerosol coating,
limiting the VOC emissions from a
facility, or otherwise controlling the use
of VOC for purposes related to attaining
the ozone NAAQS, then the compound
will not be counted as a VOC in
determining whether these regulatory
obligations have been met. Emissions of
this compound will not be considered
in determining whether a proposed new
or modified source triggers the
applicability of Prevention of
Significant Deterioration (PSD)
requirements, in areas where the PSD
program is implemented by the EPA or
a delegated state, local or tribal agency.
This action may also affect whether
HFO–1234yf is considered a VOC for
state regulatory purposes to reduce
ozone formation, depending on whether
a state relies on the EPA’s regulatory
definition of VOCs. States are not
obligated to exclude from control as
VOCs those compounds that the EPA
has found to be negligibly reactive.
However, states may not take credit for
controlling these compounds in their
ozone control strategies.
This action is consistent with the
Interim Guidance in that one of the
three reactivity metric values for HFO–
1234yf compares favorably to the
corresponding value for ethane. This
action is also supported by the EPA’s
finding during PMN review that HFO–
1234yf did not present an unreasonable
risk to human health or the environment
from the expected uses of the substance,
our finding in the SNAP program review
of this chemical that use of this
chemical in currently-allowed
applications poses lower or comparable
overall risk to human health and the
environment than other acceptable
options for the same uses and our
confidence that the SNAP program, and
the requirements under TSCA will
prevent the use of this chemical in any
additional applications where such use
would pose a significant risk to human
health or the environment.
V. Statutory and Executive Order
Reviews
emcdonald on DSK67QTVN1PROD with RULES
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
This action is not a ‘‘significant
regulatory action’’ under the terms of
Executive Order 12866 (58 FR 51735,
October 4, 1993) and is therefore not
subject to review under Executive
Orders 12866 and 13563 (76 FR 3821,
January 21, 2011).
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B. Paperwork Reduction Act
This action does not impose an
information collection burden under the
provisions of the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. Burden is
defined at 5 CFR 1320.3(b). It does not
contain any recordkeeping or reporting
requirement.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA)
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedure Act or any
other statute unless the agency certifies
that the rule will not have a significant
economic impact on a substantial
number of small entities. Small entities
include small businesses, small
organizations and small governmental
jurisdictions.
For purposes of assessing the impacts
of this action on small entities, small
entity is defined as: (1) A small business
as defined by the Small Business
Administration (SBA) regulation (see 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, I certify that this action will not
have a significant economic impact on
a substantial number of small entities.
In determining whether a rule has a
significant economic impact on a
substantial number of small entities, the
impact of concern is any significant
adverse economic impact on small
entities, since the primary purpose of
the regulatory flexibility analyses is to
identify and address regulatory
alternatives ‘‘which minimize any
significant economic impact of the rule
on small entities.’’ 5 U.S.C. 603 and 604.
Thus, an agency may certify that a rule
will not have a significant economic
impact on a substantial number of small
entities if the rule relieves regulatory
burden, or otherwise has a positive
economic effect on all of the small
entities subject to the rule. This final
rule removes HFO–1234yf from the
regulatory definition of VOCs and
thereby relieves users from
requirements to control emissions of the
compound. We have, therefore,
concluded that today’s final rule will
relieve regulatory burden for all affected
small entities.
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D. Unfunded Mandates Reform Act
This action contains no federal
mandates under the provisions of Title
II of the Unfunded Mandates Reform
Act of 1995 (UMRA), 2 U.S.C. 1531–
1538 for state, local or tribal
governments or the private sector. The
action imposes no enforceable duty on
any state, local or tribal governments or
the private sector. Therefore, this action
is not subject to the requirements of
sections 202 and 205 of the UMRA.
This action is also not subject to the
requirements of section 203 of UMRA
because it contains no regulatory
requirements that might significantly or
uniquely affect small governments. This
final rule removes HFO–1234yf from the
regulatory definition of VOCs and
thereby relieves users of the compound
from requirements to control emissions
of the compound.
E. Executive Order 13132: Federalism
This action does not have federalism
implications. It will not 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, as specified in
Executive Order 13132. This final rule
removes HFO–1234yf from the
regulatory definition of VOCs and
thereby relieves users from
requirements to control emissions of the
compound. Thus, Executive Order
13132 does not apply to this rule.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This action does not have tribal
implications, as specified in Executive
Order 13175 (65 FR 67249, November 9,
2000). It would not have substantial
direct effects on tribal governments, on
the relationship between the federal
government and Indian Tribes, or on the
distribution of power and
responsibilities 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
This action is not subject to EO 13045
(62 FR 19885, April 23, 1997) because
it is not economically significant as
defined in EO 12866. While this final
rule is not subject to the Executive
Order, the EPA has reason to believe
that ozone has a disproportionate effect
on active children who play outdoors
(62 FR 38856; 38859, July 18, 1997). The
E:\FR\FM\22OCR1.SGM
22OCR1
Federal Register / Vol. 78, No. 204 / Tuesday, October 22, 2013 / Rules and Regulations
K. Congressional Review Act
EPA has not identified any specific
studies on whether or to what extent
HFO–1234yf may affect children’s
health.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution or Use
This action is not subject to Executive
Order 13211 (66 FR 28355 (May 22,
2001)), because it is not a significant
regulatory action under Executive Order
12866.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113, section 12(d), (15 U.S.C. 272
note) directs the 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
the EPA to provide Congress, through
OMB, explanations when the agency
decides not to use available and
applicable voluntary consensus
standards. This rulemaking does not
involve technical standards. Therefore,
the EPA has not considered the use of
any voluntary consensus standards.
emcdonald on DSK67QTVN1PROD with RULES
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order (EO) 12898 (59 FR
7629, February 16, 1994) establishes
federal executive policy on
environmental justice. Its main
provision directs federal agencies, to the
greatest extent practicable and
permitted by law, to make
environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies and activities on minority
populations and low-income
populations in the United States.
The EPA has determined that this
final rule will not have
disproportionately high and adverse
human health or environmental effects
on minority or low-income populations
because it will not affect the level of
protection provided to human health or
the environment.
VerDate Mar<15>2010
16:26 Oct 21, 2013
Jkt 232001
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 on
November 21, 2013.
62455
PART 51—REQUIREMENTS FOR
PREPARATION, ADOPTION, AND
SUBMITTAL OF IMPLEMENTATION
PLANS
Subpart F—[Amended]
1. The authority citation for part 51,
Subpart F, continues to read as follows:
■
Authority: 42 U.S.C. 7401, 7411, 7412,
7413, 7414, 7470–7479, 7501–7508, 7601,
and 7602.
§ 51.100
[Amended]
2. Section 51.100 is amended at the
end of paragraph (s)(1) introductory text
by removing the words ‘‘and
perfluorocarbon compounds which fall
into these classes:’’ and adding in their
place the words ‘‘2,3,3,3tetrafluoropropene; and perfluorocarbon
compounds which fall into these
classes:’’.
■
[FR Doc. 2013–23783 Filed 10–21–13; 8:45 am]
BILLING CODE 6560–50–P
L. 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 District of
Columbia Circuit Court within 60 days
from the date the final action is
published in the Federal Register.
Filing a petition for review by the
Administrator of this final action does
not affect the finality of this action for
the purposes of judicial review nor does
it extend the time within which a
petition for judicial review must be
final, and shall not postpone the
effectiveness of such action. Thus, any
petitions for review of this action
related to the exemption of HFO–1234yf
from the regulatory definition of VOCs
must be filed in the Court of Appeals for
the District of Columbia Circuit within
60 days from the date final action is
published in the Federal Register.
List of Subjects in 40 CFR Part 51
Environmental protection,
Administrative practice and procedure,
Air pollution control, Ozone, Reporting
and recordkeeping requirements,
Volatile organic compounds.
Dated: September 19, 2013.
Gina McCarthy,
EPA Administrator.
For reasons set forth in the preamble,
part 51 of chapter I of title 40 of the
Code of Federal Regulations is amended
as follows:
PO 00000
Frm 00039
Fmt 4700
Sfmt 4700
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R03–OAR–2013–0499; FRL–9901–35–
Region3]
Approval and Promulgation of Air
Quality Implementation Plans; District
of Columbia; Infrastructure
Requirements for the 2008 Lead
National Ambient Air Quality
Standards and State Board
Requirements
Environmental Protection
Agency (EPA).
ACTION: Direct final rule.
AGENCY:
EPA is taking direct final
action to approve two State
Implementation Plan (SIP) revisions
submitted by the District of Columbia
(hereafter ‘‘the District’’) pursuant to the
Clean Air Act (CAA). Whenever new or
revised national ambient air quality
standards (NAAQS) are promulgated,
the CAA requires states to submit a plan
for the implementation, maintenance,
and enforcement of such NAAQS. The
plan is required to address basic
program elements including, but not
limited to, regulatory structure,
monitoring, modeling, legal authority,
and adequate resources necessary to
assure attainment and maintenance of
the NAAQS. These elements are referred
to as infrastructure requirements. The
District made a submittal addressing the
infrastructure requirements for the 2008
lead (Pb) NAAQS and a separate
submittal addressing requirements in
SUMMARY:
E:\FR\FM\22OCR1.SGM
22OCR1
Agencies
[Federal Register Volume 78, Number 204 (Tuesday, October 22, 2013)]
[Rules and Regulations]
[Pages 62451-62455]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2013-23783]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 51
[EPA-HQ-OAR-2010-0605; FRL-9900-53-OAR]
RIN 2060-AR70
Air Quality: Revision to Definition of Volatile Organic
Compounds--Exclusion of 2,3,3,3-tetrafluoropropene
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The EPA is taking final action to revise the regulatory
definition of volatile organic compounds (VOCs) for purposes of
preparing state implementation plans (SIPs) to attain the national
ambient air quality standards (NAAQS) for ozone under title I of the
Clean Air Act (CAA). This final action adds 2,3,3,3-tetrafluoropropene
(also known as HFO-1234yf) to the list of compounds excluded from the
regulatory definition of VOCs on the basis that this compound makes a
negligible contribution to tropospheric ozone formation. As a result,
if you are subject to certain federal regulations limiting emissions of
VOCs, your emissions of HFO-1234yf may not be regulated for some
purposes. This action may also affect whether HFO-1234yf is considered
a VOC for state regulatory purposes, depending on whether the state
relies on the EPA's regulatory definition of VOCs.
DATES: This rule is effective on November 21, 2013.
ADDRESSES: The EPA has established a docket for this action under
Docket ID
[[Page 62452]]
No. EPA-HQ-OAR-2010-0605. All documents in the docket are listed on the
www.regulations.gov Web site. 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, will
be publicly available only in hard copy. Publicly available docket
materials are available either electronically in www.regulations.gov or
in hard copy at the Docket ID No. EPA-HQ-OAR-2010-0605, EPA/DC, EPA
West, Room 3334, 1301 Constitution Avenue, Northwest, 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 and Radiation Docket Information Center is (202) 566-1742. For
additional information about the EPA's public docket, visit the EPA
Docket Center homepage at: https://www.epa.gov/epahome/dockets.htm.
FOR FURTHER INFORMATION CONTACT: David Sanders, Office of Air Quality
Planning and Standards, Air Quality Policy Division, Mail Code C539-01,
Research Triangle Park, NC 27711; telephone: (919) 541-3356; fax
number: 919-541-0824; email address: sanders.dave@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this action apply to me?
Entities potentially affected by this final rule include, but are
not necessarily limited to, states (typically state air pollution
control agencies) that control VOCs; manufacturers, importers or
processors of this compound; and industries involved in the manufacture
or servicing of automobiles or automotive air conditioning systems.
This action has no substantial direct effects on industry because it
does not impose any new mandates on these entities, but, to the
contrary, removes HFO-1234yf from the regulatory definition of VOCs.
The use of this compound is subject to restrictions under the CAA and
the Toxic Substances Control Act (TSCA). Specifically, the use of this
compound as an aerosol propellant, blowing agent, or refrigerant, or
any other use in which it would substitute for chlorofluorocarbons,
hydrochlorofluorocarbons or their substitutes, is prohibited unless
such use has been approved under the Significant New Alternatives
Policy (SNAP) program (CAA Sec. 612; 40 CFR 82 subpart G). The SNAP
program has issued a final approval for HFO-1234yf only as a substitute
for use in the motor vehicle air conditioning end-use as a replacement
for ozone depleting substances (76 FR 17488, March 29, 2011; revised at
77 FR 17344, March 26, 2012). Furthermore, any significant new use of
HFO-1234yf is subject to a reporting requirement according to a
significant new use rule (SNUR) established under TSCA (75 FR 65987,
October 27, 2010; proposed for amendment at 78 FR 32617, May 31, 2013).
B. How is this preamble organized?
The information presented in this preamble is organized as follows:
I. General Information
A. Does this action apply to me?
B. How is this preamble organized?
II. Background
A. The EPA's VOC Exemption Policy
B. Petition To List HFO-1234yf as an Exempt Compound
C. Contribution to Tropospheric Ozone
D. Health and Environmental Risks
III. Proposed Action and Response to Comments
IV. Final Action
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review and
Executive Order 13563: Improving Regulation and Regulatory Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health and Safety Risks
H. Executive Order 13211: Actions That Significantly Affect
Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act
J. Executive Order 12898: Federal Actions To Address
Environmental Justice in Minority Populations and Low-Income
Populations
K. Congressional Review Act
L. Judicial Review
II. Background
A. The EPA's VOC Exemption Policy
Tropospheric ozone, commonly known as smog, is formed when VOCs and
nitrogen oxides (NOX) react in the atmosphere in the
presence of sunlight. Because of the harmful health effects of ozone,
the EPA and state governments limit the amount of VOCs that can be
released into the atmosphere. VOCs are those organic compounds of
carbon that form ozone through atmospheric photochemical reactions.
Different VOCs have different levels of reactivity. That is, they do
not react to form ozone at the same speed or do not form ozone to the
same extent. Some VOCs react slowly or form less ozone; therefore,
changes in their emissions have less and, in some cases, very limited
effects on local or regional ozone pollution episodes. It has been the
EPA's policy that organic compounds with a negligible level of
reactivity should be excluded from the regulatory definition of VOCs so
as to focus VOC control efforts on compounds that do significantly
increase ozone concentrations. The EPA also believes that exempting
such compounds creates an incentive for industry to use negligibly
reactive compounds in place of more highly reactive compounds that are
regulated as VOCs. The EPA lists compounds that it has determined to be
negligibly reactive in its regulations as being excluded from the
regulatory definition of VOCs (40 CFR 51.100(s)).
Section 302(s) of the CAA specifies that the EPA has the authority
to define the meaning of ``VOC,'' and hence what compounds shall be
treated as VOCs for regulatory purposes. The policy of excluding
negligibly reactive compounds from the regulatory definition of VOCs
was first set forth in the ``Recommended Policy on Control of Volatile
Organic Compounds'' (42 FR 35314, July 8, 1977) and was supplemented
most recently with the ``Interim Guidance on Control of Volatile
Organic Compounds in Ozone State Implementation Plans'' (Interim
Guidance) (70 FR 54046, September 13, 2005). The EPA uses the
reactivity of ethane as the threshold for determining whether a
compound has negligible reactivity. Compounds that are less reactive
than, or equally reactive to, ethane under certain assumed conditions
may be deemed negligibly reactive and therefore suitable for exemption
from the regulatory definition of VOCs. Compounds that are more
reactive than ethane continue to be considered VOCs for regulatory
purposes and therefore are subject to control requirements. The
selection of ethane as the threshold compound was based on a series of
smog chamber experiments that underlay the 1977 policy.
The EPA has used three different metrics to compare the reactivity
of a specific compound to that of ethane: (i) The reaction rate
constant (known as kOH) with the hydroxyl radical (OH); (ii)
the maximum incremental reactivity (MIR) on a reactivity per unit mass
basis; and (iii) the MIR expressed on a reactivity per mole basis. If a
compound is equally or less reactive than ethane on
[[Page 62453]]
any one of these three metrics, then under the Interim Guidance it is
considered by the EPA to be negligibly reactive in forming ozone. A
full description of each metric and how it is derived can be found in
the proposal notice for this action (76 FR 64059, October 17, 2011) and
is not repeated here.
B. Petition To List HFO-1234yf as an Exempt Compound
Honeywell Inc. submitted a petition to the EPA on June 29, 2009,
requesting that HFO-1234yf (CAS 754-12-1) be exempted from VOC control
based on its low reactivity relative to ethane. The petitioner
indicated that HFO-1234yf may be used as a refrigerant for
refrigeration and air-conditioning. Honeywell also indicated that it
expects HFO-1234yf to be widely used as a replacement for HFC-134a in
motor vehicle air-conditioners (MVAC), and that it has been
specifically developed for this purpose. Honeywell asserts that as a
replacement for use in motor vehicle air conditioners, there will be an
environmental advantage in that the global warming potential (GWP) of
HFO-1234yf is 4, which is substantially lower than the GWP for HFC-134a
(100-year GWP = 1430), which HFO-1234yf is designed to replace.
C. Contribution to Tropospheric Ozone
Detailed information on the ozone reactivity of HFO-1234yf was
presented in the proposal notice for this action (76 FR 64059, October
17, 2011) and is summarized here.
HFO-1234yf has a higher kOH value than ethane, meaning
that it initially reacts more quickly in the atmosphere than ethane. A
molecule of HFO-1234yf is also more reactive than a molecule of ethane.
However, a gram of HFO-1234yf has the same reactivity as a gram of
ethane.
Under the Interim Guidance, if a compound is equally or less
reactive than ethane on any one or more of the three reactivity
metrics, it is considered by the EPA to be negligibly reactive in
forming ozone. The data submitted by Honeywell support the conclusion
that the reactivity of HFO-1234yf is equal to or lower than that of
ethane on a mass MIR basis. Thus, HFO-1234yf is eligible for exemption
from the regulatory definition of VOCs under the terms of the Interim
Guidance.
The EPA has also considered the results of a recent peer-reviewed
study of the increase in ozone that may occur as a result of the
substitution of HFO-1234yf for HFC-134a.\1\ The additional information
from this study shows that, under the assumptions used in the air
quality modeling, the use of HFO-1234yf would produce slightly more
ozone than continued use of HFC-134a, but the increase is unlikely to
have a significant impact on local air quality. The EPA believes the
very small increase (0.01 percent) in ozone concentrations that may
result from encouraging the use of HFO-1234yf via an exemption from the
regulatory definition of VOC does not constitute a sufficient reason to
depart from the Interim Guidance's reliance on MIR comparisons to
ethane as the basis for approving VOC exemption requests.
---------------------------------------------------------------------------
\1\ D. Luecken, R. Waterland, S. Papasavva, K. Taddonio, W.
Hutzell, J. Rugh, and S. Andersen. Ozone and TFA Impacts in North
America from Degradation of 2,3,3,3-Tetrafluoropropene (HFO-1234yf),
A Potential Greenhouse Gas Replacement. Environ. Sci. Technol. 44,
pp. 343-349. See 76 FR 64059 (October 17, 2011). See 76 FR 64059
(October 17, 2011) at 64062 for additional description of this study
and the EPA's assessment of it.
---------------------------------------------------------------------------
In summary, the EPA believes that this chemical qualifies as
negligibly reactive with respect to its contribution to tropospheric
ozone formation.
D. Health and Environmental Risks
The preamble to the proposal notice for this action (76 FR 64059,
October 17, 2011) provided background information on the Premanufacture
Notice (PMN) and SNAP reviews of HFO-1234yf. This information is
summarized and updated here.
After reviewing available information and public comments regarding
its safety, health and environmental risks and benefits under the SNAP
program, the EPA issued a final listing on March 29, 2011, for HFO-
1234yf as an acceptable substitute for use of ozone depleting
substances in MVAC, subject to specific use conditions, in place of
CFC-12 and HFC-134a (76 FR 174888).\2\
---------------------------------------------------------------------------
\2\ HFC-134a, which is not an ozone depleting substance, has
already largely replaced CFC-12 in motor vehicle air conditioners.
---------------------------------------------------------------------------
In the SNAP review, the EPA found that the use of HFO-1234yf in new
passenger vehicle and light-duty truck MVAC systems, subject to the use
conditions, does not present a significantly greater risk to human
health and the environment compared to the currently approved MVAC
alternatives. The 2011 SNAP rule for HFO-1234yf was amended on March
26, 2012, to incorporate by reference a revised standard for connecting
fittings from SAE International (77 FR 17344).
Under the TSCA, the EPA in 2010 completed a pre-manufacture review
for HFO-1234yf and issued a SNUR (75 FR 65987, October 27, 2010). The
2010 SNUR for HFO-1234yf requires significant new use notification to
the EPA at least 90 days before manufacturing or processing for uses
beyond air conditioning in new passenger cars and vehicles or
commercial servicing of new passenger cars and vehicles originally
designed for HFO-1234yf. In particular, under the 2010 rule,
notification is required before HFO-1234yf can be sold directly to
consumers for the purpose of servicing the MVAC system of their own
vehicles. During the notification period, the EPA can take further
action to prevent any unreasonable risk. This precautionary step was
taken because of certain animal exposure studies indicating toxicity,
and the possibility that consumers might be exposed to levels of HFO-
1234yf that would cause an unreasonable health risk. However, based on
information submitted subsequent to the 2010 rule that in the EPA's
view resolves the issue pertaining to the potential risks from consumer
exposure that was present in 2010, the EPA has proposed to amend the
SNUR for HFO-1234yf such that notification would not be required prior
to sale of HFO-1234yf-containing consumer products used to recharge the
MVAC systems in passenger cars and vehicles originally designed for
HFO-1234yf (78 FR 32617, May 31, 2013).
III. Proposed Action and Response to Comments
Based on the mass MIR value for HFO-1234yf being equal to or less
than that of ethane, the EPA proposed to find that HFO-1234yf is
``negligibly reactive'' and to exempt HFO-1234yf from the regulatory
definition of VOCs at 40 CFR 51.100(s) (76 FR 64059, October 17,
2011).\3\
---------------------------------------------------------------------------
\3\ In this proposal, we also proposed to exempt trans-1,3,3,3-
tetrafluoropropene (also known as HFO-1234ze) from the definition of
VOC. We have taken final action separately for HFO-1234ze on that
proposal. 77 FR 37610, June 22, 2012.
---------------------------------------------------------------------------
There were two comments regarding HFO-1234yf submitted to the
docket during the public comment period. One comment was from the
petitioner, Honeywell. Another comment came from the Alliance of
Automobile Manufacturers. Both comments were in favor of exempting HFO-
1234yf. The EPA acknowledges the commenters' support for the proposed
action.
IV. Final Action
The EPA is taking final action to approve the petition for
exemption of HFO-1234yf from the regulatory definition of VOCs.
If an entity uses or produces HFO-1234yf and is subject to the EPA
[[Page 62454]]
regulations limiting the use of VOC in a product other than an aerosol
coating, limiting the VOC emissions from a facility, or otherwise
controlling the use of VOC for purposes related to attaining the ozone
NAAQS, then the compound will not be counted as a VOC in determining
whether these regulatory obligations have been met. Emissions of this
compound will not be considered in determining whether a proposed new
or modified source triggers the applicability of Prevention of
Significant Deterioration (PSD) requirements, in areas where the PSD
program is implemented by the EPA or a delegated state, local or tribal
agency. This action may also affect whether HFO-1234yf is considered a
VOC for state regulatory purposes to reduce ozone formation, depending
on whether a state relies on the EPA's regulatory definition of VOCs.
States are not obligated to exclude from control as VOCs those
compounds that the EPA has found to be negligibly reactive. However,
states may not take credit for controlling these compounds in their
ozone control strategies.
This action is consistent with the Interim Guidance in that one of
the three reactivity metric values for HFO-1234yf compares favorably to
the corresponding value for ethane. This action is also supported by
the EPA's finding during PMN review that HFO-1234yf did not present an
unreasonable risk to human health or the environment from the expected
uses of the substance, our finding in the SNAP program review of this
chemical that use of this chemical in currently-allowed applications
poses lower or comparable overall risk to human health and the
environment than other acceptable options for the same uses and our
confidence that the SNAP program, and the requirements under TSCA will
prevent the use of this chemical in any additional applications where
such use would pose a significant risk to human health or the
environment.
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review and Executive
Order 13563: Improving Regulation and Regulatory Review
This action is not a ``significant regulatory action'' under the
terms of Executive Order 12866 (58 FR 51735, October 4, 1993) and is
therefore not subject to review under Executive Orders 12866 and 13563
(76 FR 3821, January 21, 2011).
B. Paperwork Reduction Act
This action does not impose an information collection burden under
the provisions of the Paperwork Reduction Act, 44 U.S.C. 3501 et seq.
Burden is defined at 5 CFR 1320.3(b). It does not contain any
recordkeeping or reporting requirement.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA) generally requires an agency
to prepare a regulatory flexibility analysis of any rule subject to
notice and comment rulemaking requirements under the Administrative
Procedure Act or any other statute unless the agency certifies that the
rule will not have a significant economic impact on a substantial
number of small entities. Small entities include small businesses,
small organizations and small governmental jurisdictions.
For purposes of assessing the impacts of this action on small
entities, small entity is defined as: (1) A small business as defined
by the Small Business Administration (SBA) regulation (see 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, I certify that this action will not have a significant
economic impact on a substantial number of small entities. In
determining whether a rule has a significant economic impact on a
substantial number of small entities, the impact of concern is any
significant adverse economic impact on small entities, since the
primary purpose of the regulatory flexibility analyses is to identify
and address regulatory alternatives ``which minimize any significant
economic impact of the rule on small entities.'' 5 U.S.C. 603 and 604.
Thus, an agency may certify that a rule will not have a significant
economic impact on a substantial number of small entities if the rule
relieves regulatory burden, or otherwise has a positive economic effect
on all of the small entities subject to the rule. This final rule
removes HFO-1234yf from the regulatory definition of VOCs and thereby
relieves users from requirements to control emissions of the compound.
We have, therefore, concluded that today's final rule will relieve
regulatory burden for all affected small entities.
D. Unfunded Mandates Reform Act
This action contains no federal mandates under the provisions of
Title II of the Unfunded Mandates Reform Act of 1995 (UMRA), 2 U.S.C.
1531-1538 for state, local or tribal governments or the private sector.
The action imposes no enforceable duty on any state, local or tribal
governments or the private sector. Therefore, this action is not
subject to the requirements of sections 202 and 205 of the UMRA.
This action is also not subject to the requirements of section 203
of UMRA because it contains no regulatory requirements that might
significantly or uniquely affect small governments. This final rule
removes HFO-1234yf from the regulatory definition of VOCs and thereby
relieves users of the compound from requirements to control emissions
of the compound.
E. Executive Order 13132: Federalism
This action does not have federalism implications. It will not 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, as
specified in Executive Order 13132. This final rule removes HFO-1234yf
from the regulatory definition of VOCs and thereby relieves users from
requirements to control emissions of the compound. Thus, Executive
Order 13132 does not apply to this rule.
F. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
This action does not have tribal implications, as specified in
Executive Order 13175 (65 FR 67249, November 9, 2000). It would not
have substantial direct effects on tribal governments, on the
relationship between the federal government and Indian Tribes, or on
the distribution of power and responsibilities 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
This action is not subject to EO 13045 (62 FR 19885, April 23,
1997) because it is not economically significant as defined in EO
12866. While this final rule is not subject to the Executive Order, the
EPA has reason to believe that ozone has a disproportionate effect on
active children who play outdoors (62 FR 38856; 38859, July 18, 1997).
The
[[Page 62455]]
EPA has not identified any specific studies on whether or to what
extent HFO-1234yf may affect children's health.
H. Executive Order 13211: Actions That Significantly Affect Energy
Supply, Distribution or Use
This action is not subject to Executive Order 13211 (66 FR 28355
(May 22, 2001)), because it is not a significant regulatory action
under Executive Order 12866.
I. National Technology Transfer and Advancement Act
Section 12(d) of the National Technology Transfer and Advancement
Act of 1995 (``NTTAA''), Public Law 104-113, section 12(d), (15 U.S.C.
272 note) directs the 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 the
EPA to provide Congress, through OMB, explanations when the agency
decides not to use available and applicable voluntary consensus
standards. This rulemaking does not involve technical standards.
Therefore, the EPA has not considered the use of any voluntary
consensus standards.
J. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations
Executive Order (EO) 12898 (59 FR 7629, February 16, 1994)
establishes federal executive policy on environmental justice. Its main
provision directs federal agencies, to the greatest extent practicable
and permitted by law, to make environmental justice part of their
mission by identifying and addressing, as appropriate,
disproportionately high and adverse human health or environmental
effects of their programs, policies and activities on minority
populations and low-income populations in the United States.
The EPA has determined that this final rule will not have
disproportionately high and adverse human health or environmental
effects on minority or low-income populations because it will not
affect the level of protection provided to human health or the
environment.
K. 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 on November 21, 2013.
L. 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 District of Columbia Circuit Court within 60 days from the date the
final action is published in the Federal Register.
Filing a petition for review by the Administrator of this final
action does not affect the finality of this action for the purposes of
judicial review nor does it extend the time within which a petition for
judicial review must be final, and shall not postpone the effectiveness
of such action. Thus, any petitions for review of this action related
to the exemption of HFO-1234yf from the regulatory definition of VOCs
must be filed in the Court of Appeals for the District of Columbia
Circuit within 60 days from the date final action is published in the
Federal Register.
List of Subjects in 40 CFR Part 51
Environmental protection, Administrative practice and procedure,
Air pollution control, Ozone, Reporting and recordkeeping requirements,
Volatile organic compounds.
Dated: September 19, 2013.
Gina McCarthy,
EPA Administrator.
For reasons set forth in the preamble, part 51 of chapter I of
title 40 of the Code of Federal Regulations is amended as follows:
PART 51--REQUIREMENTS FOR PREPARATION, ADOPTION, AND SUBMITTAL OF
IMPLEMENTATION PLANS
Subpart F--[Amended]
0
1. The authority citation for part 51, Subpart F, continues to read as
follows:
Authority: 42 U.S.C. 7401, 7411, 7412, 7413, 7414, 7470-7479,
7501-7508, 7601, and 7602.
Sec. 51.100 [Amended]
0
2. Section 51.100 is amended at the end of paragraph (s)(1)
introductory text by removing the words ``and perfluorocarbon compounds
which fall into these classes:'' and adding in their place the words
``2,3,3,3-tetrafluoropropene; and perfluorocarbon compounds which fall
into these classes:''.
[FR Doc. 2013-23783 Filed 10-21-13; 8:45 am]
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