Protection of Stratospheric Ozone: Adjustments to the Allowance System for Controlling HCFC Production, Import, and Export, 237-259 [2011-33456]
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Federal Register / Vol. 77, No. 2 / Wednesday, January 4, 2012 / Proposed Rules
attainment and reasonable further
progress toward attainment of the
NAAQS or any other applicable
requirement of the Act. The Colorado
SIP revisions that are proposed for
approval in this action do not interfere
with attainment of the NAAQS or any
other applicable requirement of the Act.
The revisions do not make substantive
changes that relax the stringency of the
Colorado SIP; instead, the submittal of
Section 1.11 of Colorado’s procedural
rule meets a requirement of the CAA.
Therefore, the revisions proposed for
approval satisfy section 110(l)
requirements.
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V. Proposed Action
We are proposing for approval Section
1.11 of Colorado’s procedural rule as
adopted by the Commission on January
16, 1998, and submitted to EPA on
November 5, 1999. We are also
reproposing approval of a portion of
Colorado’s January 7, 2008, submittal to
meet the ‘‘infrastructure’’ requirements
of section 110(a)(2) for the 1997 8-hour
ozone NAAQS, specifically the portion
intended to address the requirements of
section 110(a)(2)(E)(ii) of the CAA.
VI. Statutory and Executive Order
Reviews
Under the Clean Air Act, the
Administrator is required to approve a
SIP submission that complies with the
provisions of the Act and applicable
Federal regulations. 42 U.S.C. 7410(k);
40 CFR 52.02(a). Thus, in reviewing SIP
submissions, EPA’s role is to approve
state choices, provided that they meet
the criteria of the Clean Air Act.
Accordingly, this proposed action
merely approves state law as meeting
Federal requirements and does not
impose additional requirements beyond
those imposed by state law. For that
reason, this proposed action:
• Is not a ‘‘significant regulatory
action’’ subject to review by the Office
of Management and Budget under
Executive Order 12866 (58 FR 51735,
October 4, 1993);
• Does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• Is certified as not having a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act
(5 U.S.C. 601 et seq.);
• Does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4);
• Does not have Federalism
implications as specified in Executive
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Order 13132 (64 FR 43255, August 10,
1999);
• Is not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
• Is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• Is not subject to requirements of
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
application of those requirements would
be inconsistent with the Clean Air Act;
and
• Does not provide EPA with the
discretionary authority to address, as
appropriate, disproportionate human
health or environmental effects, using
practicable and legally permissible
methods, under Executive Order 12898
(59 FR 7629, February 16, 1994).
In addition, this rule does not have
tribal implications as specified by
Executive Order 13175 (65 FR 67249,
November 9, 2000), because the SIP is
not approved to apply in Indian country
located in the state, and EPA notes that
it will not impose substantial direct
costs on tribal governments or preempt
tribal law.
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Carbon monoxide,
Intergovernmental relations, Lead,
Nitrogen dioxide, Ozone, Particulate
matter, Reporting and recordkeeping
requirements, Sulfur oxides, Volatile
organic compounds.
Dated: December 23, 2011.
James B. Martin,
Regional Administrator, Region 8.
[FR Doc. 2011–33760 Filed 1–3–12; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 82
[EPA–HQ–OAR–2011–0354; FRL–9614–5]
RIN 2060–AQ98
Protection of Stratospheric Ozone:
Adjustments to the Allowance System
for Controlling HCFC Production,
Import, and Export
Environmental Protection
Agency [EPA].
ACTION: Proposed rule.
AGENCY:
EPA is proposing to adjust the
allowance system controlling U.S.
consumption and production of
hydrochlorofluorocarbons (HCFCs) as a
SUMMARY:
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237
result of a recent court decision vacating
a portion of the rule titled ‘‘Protection
of Stratospheric Ozone: Adjustments to
the Allowance System for Controlling
HCFC Production, Import, and Export;
Final Rule.’’ EPA interprets the court’s
vacatur as applying to the part of the
rule that establishes the company-bycompany baselines and calendar-year
allowances for HCFC–22 and HCFC–
142b. Following the August 5, 2011
interim final rule allocating allowances
for 2011, this action proposes to relieve
the regulatory ban on production and
consumption of these two chemicals
following the court’s vacatur by
establishing company-by-company
HCFC–22 and HCFC–142b baselines and
allocating production and consumption
allowances for 2012–2014.
DATES: Written comments on this
proposed rule must be received by the
EPA Docket on or before February 3,
2012, unless a public hearing is
requested. Any party requesting a public
hearing must notify the contact listed
below under FOR FURTHER INFORMATION
CONTACT by 5 p.m. Eastern Standard
Time on January 11, 2012. If a public
hearing is requested, the hearing would
be held on January 19, 2012 and
commenters will have until February
21, 2012 to submit comments before the
close of the comment period. If a
hearing is held, it will take place at EPA
headquarters in Washington, DC. EPA
will post a notice on our Web site,
https://www.epa.gov/ozone/
strathome.html, announcing further
information should a hearing take place.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2011–0354, by one of the
following methods:
• www.regulations.gov: Follow the
on-line instructions for submitting
comments.
• Email: a-and-r-docket@epa.gov.
• Mail: Docket # EPA–HQ–OAR–
2011–0354, Air and Radiation Docket
and Information Center, U.S.
Environmental Protection Agency, Mail
code: 6102T, 1200 Pennsylvania Ave.
NW., Washington, DC 20460.
• Hand Delivery: Docket #EPA–HQ–
OAR–2011–0354 Air and Radiation
Docket at EPA West, 1301 Constitution
Avenue NW., Room B108, Mail Code
6102T, Washington, DC 20004. Such
deliveries are only accepted during the
Docket’s normal hours of operation, and
special arrangements should be made
for deliveries of boxed information.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–OAR–2011–
0354. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
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Federal Register / Vol. 77, No. 2 / Wednesday, January 4, 2012 / Proposed Rules
made available online at
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through www.regulations.gov
or email. The www.regulations.gov Web
site is an ‘‘anonymous access’’ system,
which means EPA will not know your
identity or contact information unless
you provide it in the body of your
comment. If you send an email
comment directly to EPA without going
through www.regulations.gov, your
email address will be automatically
captured and included as part of the
comment that is placed in the public
docket and made available on the
Internet. If you submit an electronic
comment, EPA recommends that you
include your name and other contact
information in the body of your
comment and with any disk or CD–ROM
you submit. If EPA cannot read your
comment due to technical difficulties
and cannot contact you for clarification,
EPA may not be able to consider your
comment. Electronic files should avoid
the use of special characters, any form
of encryption, and be free of any defects
or viruses. For additional information
about EPA’s public docket, visit the EPA
Docket Center homepage at
www.epa.gov/epahome/dockets.htm.
FOR FURTHER INFORMATION CONTACT:
Luke H. Hall-Jordan by telephone at
(202) 343–9591, or by email at halljordan.luke@epa.gov, or by mail at U.S.
Environmental Protection Agency,
Stratospheric Protection Division,
Stratospheric Program Implementation
Branch (6205J), 1200 Pennsylvania
Avenue NW., Washington, DC 20460.
You may also visit the Ozone Protection
Web site of EPA’s Stratospheric
Protection Division at www.epa.gov/
ozone/strathome.html for further
information about EPA’s Stratospheric
Ozone Protection regulations, the
science of ozone layer depletion, and
related topics.
SUPPLEMENTARY INFORMATION:
Acronyms and Abbreviations. The
following acronyms and abbreviations
are used in this document.
CAA—Clean Air Act
CAAA—Clean Air Act Amendments of 1990
CFC—Chlorofluorocarbon
CFR—Code of Federal Regulations
EPA—Environmental Protection Agency
FR—Federal Register
HCFC—Hydrochlorofluorocarbon
HVAC—Heating, Ventilating, and Air
Conditioning
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Montreal Protocol—Montreal Protocol on
Substances that Deplete the Ozone Layer
MOP—Meeting of the Parties
MT—Metric Ton
ODP—Ozone Depletion Potential
ODS—Ozone-Depleting Substances
Party—States and regional economic
integration organizations that have
consented to be bound by the Montreal
Protocol on Substances that Deplete the
Ozone Layer
Organization of This Document. The
following outline is provided to aid in
locating information in this preamble.
I. General Information
A. Does this action apply to me?
B. What should I consider as I prepare my
comments for EPA?
1. Confidential Business Information (CBI)
2. Tips for Preparing Your Comments
II. Background
A. How does the Montreal Protocol phase
out HCFCs?
B. How does the Clean Air Act phase out
HCFCs?
C. What sections of the Clean Air Act apply
to this rulemaking?
D. How does this action relate to the recent
court decision?
E. Comments Relevant to Recovery and
Reclamation Issues in This Rulemaking
Submitted in Response to the 2011
Interim Final Rule Allocating HCFC
Allowances
III. How does EPA propose to allocate HCFC–
22 and HCFC–142b allowances for 2012–
2014?
A. What baselines does EPA propose to use
for HCFC–22 and HCFC–142b
allowances?
B. What factors did EPA consider in
proposing allocation amounts for HCFC–
22 and HCFC–142b?
1. How important is HCFC–22 relative to
HCFC–142b for servicing existing
equipment?
2. Can servicing needs be met with virgin
and recovered material?
3. How would the allocation decline?
4. How will EPA address the court’s
decision with regard to 2010 HCFC
allowances?
C. How Much HCFC–22 and HCFC–142b
would be allocated in 2012–2014?
1. How does EPA propose to allocate
HCFC–22 consumption allowances for
2012–2014?
2. How does EPA Propose to allocate
HCFC–22 production allowances for
2012–2014?
3. How does EPA propose to allocate
HCFC–142b consumption and
production allowances for 2012–2014?
4. How would the aggregate for HCFC–22
and HCFC–142b translate entity-byentity?
D. Are HCFC–141b, HCFC–123, HCFC–124,
HCFC–225ca, and HCFC–225cb
allowances affected by this rulemaking?
E. How will EPA allocate other HCFCs?
IV. How does EPA propose to change the
regulations governing transfers of
allowances of Class II Controlled
Substances?
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A. How does EPA propose to change the
regulations governing permanent
transfers of Class II Allowances?
B. How does EPA propose to change the
regulations governing transfers of Article
5 HCFC Allowances?
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 (RFA)
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
I. General Information
A. Does this action apply to me?
This rule will affect the following
categories:
—Industrial Gas Manufacturing entities
(NAICS code 325120), including
fluorinated hydrocarbon gases
manufacturers and reclaimers;
—Other Chemical and Allied Products
Merchant Wholesalers (NAICS code
422690), including chemical gases
and compressed gases merchant
wholesalers;
—Air-Conditioning and Warm Air
Heating Equipment and Commercial
and Industrial Refrigeration
Equipment Manufacturing entities
(NAICS code 333415), including airconditioning equipment and
commercial and industrial
refrigeration equipment
manufacturers;
—Air-Conditioning Equipment and
Supplies Merchant Wholesalers
(NAICS code 423730), including airconditioning (condensing unit,
compressors) merchant wholesalers;
—Electrical and Electronic Appliance,
Television, and Radio Set Merchant
Wholesalers (NAICS code 423620),
including air-conditioning (room
units) merchant wholesalers; and
—Plumbing, Heating, and AirConditioning Contractors (NAICS
code 238220), including Central airconditioning system and commercial
refrigeration installation; HVAC
contractors.
This list is not intended to be
exhaustive, but rather provides a guide
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for readers regarding entities likely to be
regulated by this action. This table lists
the types of entities that could
potentially be regulated by this action.
Other types of entities not listed in this
table could also be affected. To
determine whether your facility,
company, business organization, or
other entity is regulated by this action,
you should carefully examine these
regulations. If you have questions
regarding the applicability of this action
to a particular entity, consult the person
listed in the FOR FURTHER INFORMATION
CONTACT section.
B. What should I consider as I prepare
my comments for EPA?
1. Confidential Business Information
(CBI)
Do not submit confidential business
information (CBI) to EPA through
www.regulations.gov or email. Clearly
mark the part or all of the information
that you claim to be CBI. For CBI
information in a disk or CD–ROM that
you mail to EPA, mark the outside of the
disk or CD–ROM as CBI and then
identify electronically within the disk or
CD–ROM the specific information that
is claimed as CBI. In addition to one
complete version of the comment that
includes information claimed as CBI, a
copy of the comment that does not
contain the information claimed as CBI
must be submitted for inclusion in the
public docket. Information so marked
will not be disclosed except in
accordance with procedures set forth in
40 CFR 2.2.
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2. Tips for Preparing Your Comments
When submitting comments,
remember to do the following:
• Identify the rulemaking by docket
number and other identifying
information (subject heading, Federal
Register date and page number).
• Follow directions. The Agency may
ask you to respond to specific questions
or organize comments by referencing a
Code of Federal Regulations (CFR) part
or section number.
• Explain why you agree or disagree
with the proposal; suggest alternatives
and substitute language for your
requested changes.
• Describe any assumptions and
provide any technical information and/
or data that you used in preparing your
comments.
• If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
• Provide specific examples to
illustrate your concerns, and suggest
alternatives.
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• Explain your views as clearly as
possible, avoiding the use of profanity
or personal threats.
• Make sure to submit your
comments by the comment period
deadline identified.
II. Background
EPA is undertaking this rulemaking as
a result of the decision issued by the
U.S. Court of Appeals for the District of
Columbia Circuit (Court) in Arkema v.
EPA (618 F.3d 1, DC Cir. 2010)
regarding the December 15, 2009, final
rule titled ‘‘Protection of Stratospheric
Ozone: Adjustments to the Allowance
System for Controlling HCFC
Production, Import, and Export,’’
published at 74 FR 66413 (2009 Final
Rule). Certain allowance holders
affected by the 2009 Final Rule filed
petitions for judicial review of the rule
under section 307(b) of the Clean Air
Act. Among other arguments, the
petitioners contended that the rule was
impermissibly retroactive because in
setting the baselines for the new
regulatory period, EPA did not take into
account certain inter-pollutant baseline
transfers that petitioners had performed
during the prior regulatory period.
The Court issued a decision on
August 27, 2010, agreeing with
petitioners that ‘‘the [2009] Final Rule
unacceptably alters transactions the
EPA approved under the 2003 Rule,’’
(Arkema v. EPA, 618 F.3d at 3). The
Court vacated the rule in part, ‘‘insofar
as it operates retroactively,’’ and
remanded to EPA ‘‘for prompt
resolution,’’ (618 F.3d at 10). The Court
withheld the mandate for the decision
pending the disposition of any petition
for rehearing. EPA’s petition for
rehearing was denied on January 21,
2011. The mandate issued on February
4, 2011. More detail is provided on the
case and EPA’s interpretation of the
Court’s decision in section II.D. of this
preamble.
EPA addressed the Court’s partial
vacatur as it relates to 2011 in an August
5, 2011, interim final rule, ‘‘Protection
of Stratospheric Ozone: Adjustments to
the Allowance System for Controlling
HCFC Production, Import, and Export,’’
(2011 Interim Final Rule). This
proposed rule is a follow-on to that
action, and proposes a path forward for
the remainder of the regulatory period
ending on December 31, 2014.
A. How does the Montreal Protocol
phase out HCFCs?
The Montreal Protocol on Substances
that Deplete the Ozone Layer is the
international agreement aimed at
reducing and eventually eliminating the
production and consumption of
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239
stratospheric ozone-depleting
substances (ODS). The U.S. was one of
the original signatories to the 1987
Montreal Protocol and the U.S. ratified
the Protocol on April 12, 1988. Congress
then enacted, and President George
H.W. Bush signed into law, the Clean
Air Act Amendments of 1990 (CAAA),
which included Title VI on
Stratospheric Ozone Protection, codified
as 42 U.S.C. Chapter 85, Subchapter VI,
to ensure that the U.S. could satisfy its
obligations under the Montreal Protocol.
Title VI includes restrictions on
production, consumption, and use of
ODS that are subject to acceleration if
‘‘the Montreal Protocol is modified to
include a schedule to control or reduce
production, consumption, or use * * *
more rapidly than the applicable
schedule’’ prescribed by the statute
(CAA § 606). Both the Montreal Protocol
and the Clean Air Act (CAA) define
consumption as production plus
imports minus exports.
In 1990, as part of the London
Amendment to the Montreal Protocol,
the Parties identified HCFCs as
‘‘transitional substances’’ to serve as
temporary, lower ozone depletion
potential (ODP) substitutes for CFCs and
other ODS. EPA similarly viewed
HCFCs as ‘‘important interim substitutes
that will allow for the earliest possible
phaseout of CFCs and other Class I
substances’’1 (58 FR 65026). In 1992,
through the Copenhagen Amendment to
the Montreal Protocol, the Parties
created a detailed phaseout schedule for
HCFCs beginning with a cap on
consumption for developed countries
not operating under Article 5 of the
Montreal Protocol (non-Article 5
Parties), a schedule to which the U.S.
adheres. The consumption cap for each
non-Article 5 Party was set at 3.1
percent (later tightened to 2.8 percent)
of a Party’s CFC consumption in 1989,
plus a Party’s consumption of HCFCs in
1989 (weighted on an ODP basis). Based
on this formula, the HCFC consumption
cap for the U.S. was 15,240 ODPweighted metric tons (MT), effective
January 1, 1996. This became the U.S.
consumption baseline for HCFCs.
The 1992 Copenhagen Amendment
created a schedule with graduated
reductions and the eventual phaseout of
HCFC consumption (Copenhagen, 23–25
November, 1992, Decision IV/4). Prior to
a later adjustment in 2007, the schedule
initially called for a 35 percent
reduction of the consumption cap in
2004, followed by a 65 percent
1 Class I refers to the controlled substances listed
in appendix A to 40 CFR part 82 subpart A. Class
II refers to the controlled substances listed in
appendix B to 40 CFR part 82 subpart A.
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reduction in 2010, a 90 percent
reduction in 2015, a 99.5 percent
reduction in 2020 (restricting the
remaining 0.5 percent of baseline to the
servicing of existing refrigeration and
air-conditioning equipment), with a
total phaseout in 2030.
The Copenhagen Amendment did not
cap HCFC production. In 1999, the
Parties created a cap on production for
Non-Article 5 Parties through an
amendment to the Montreal Protocol
agreed by the Eleventh Meeting of the
Parties (Beijing, 29 November—3
December 1999, Decision XI/5). The cap
on production was set at the average of:
(a) 1989 HCFC production plus 2.8
percent of 1989 CFC production, and (b)
1989 HCFC consumption plus 2.8
percent of 1989 CFC consumption.
Based on this formula, the HCFC
production cap for the U.S. was 15,537
ODP-weighted MT, effective January 1,
2004. This became the U.S. production
baseline for HCFCs.
To further protect human health and
the environment, the Parties to the
Montreal Protocol adjusted the Montreal
Protocol’s phaseout schedule for HCFCs
at the 19th Meeting of the Parties in
September 2007. In accordance with
Article 2(9)(d) of the Montreal Protocol,
the adjustment to the phaseout schedule
was effective on May 14, 2008.2
As a result of the 2007 Montreal
Adjustment (reflected in Decision XIX/
6), the U.S. and other developed
countries are obligated to reduce HCFC
production and consumption 75 percent
below the established baseline by 2010,
rather than 65 percent as previously
required. The other milestones remain
the same. The adjustment also resulted
in a phaseout schedule for HCFC
production that parallels the
consumption phaseout schedule. All
production and consumption for NonArticle 5 Parties is phased out by 2030.
Decision XIX/6 also adjusted the
provisions for Parties operating under
paragraph 1 of Article 5 (developing
countries): (1) To set HCFC production
and consumption baselines based on the
average 2009–2010 production and
consumption, respectively; (2) to freeze
HCFC production and consumption at
those baselines in 2013; and (3) to add
stepwise reductions of 10 percent below
2 Under Article 2(9)(d) of the Montreal Protocol,
an adjustment enters into force six months from the
date the depositary (the Ozone Secretariat)
circulates it to the Parties. The depositary accepts
all notifications and documents related to the
Protocol and examines whether all formal
requirements are met. In accordance with the
procedure in Article 2(9)(d), the depositary
communicated the adjustment to all Parties on
November 14, 2007. The adjustment entered into
force and became binding for all Parties on May 14,
2008.
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baselines by 2015, 35 percent by 2020,
67.5 percent by 2025, and 97.5 percent
by 2030—allowing, between 2030 and
2040, an annual average of no more than
2.5 percent to be produced or imported
solely for servicing existing airconditioning and refrigeration
equipment. All production and
consumption for Article 5 Parties will
be phased out by 2040.
In addition, Decision XIX/6 adjusted
Article 2F to allow developed countries
to produce ‘‘up to 10 percent of baseline
levels’’ for export to Article 5 countries
‘‘in order to satisfy basic domestic
needs’’ until 2020.3 Paragraph 14 of
3 Paragraphs 4–6 of adjusted Article 2F read as
follows:
‘‘4. Each Party shall ensure that for the twelvemonth period commencing on 1 January 2010, and
in each twelve-month period thereafter, its
calculated level of consumption of the controlled
substances in Group I of Annex C does not exceed,
annually, twenty-five per cent of the sum referred
to in paragraph 1 of this Article. Each Party
producing one or more of these substances shall, for
the same periods, ensure that its calculated level of
production of the controlled substances in Group I
of Annex C does not exceed, annually, twenty-five
per cent of the calculated level referred to in
paragraph 2 of this Article. However, in order to
satisfy the basic domestic needs of the Parties
operating under paragraph 1 of Article 5, its
calculated level of production may exceed that limit
by up to ten per cent of its calculated level of
production of the controlled substances in Group I
of Annex C as referred to in paragraph 2.
5. Each Party shall ensure that for the twelvemonth period commencing on 1 January 2015, and
in each twelve-month period thereafter, its
calculated level of consumption of the controlled
substances in Group I of Annex C does not exceed,
annually, ten per cent of the sum referred to in
paragraph 1 of this Article. Each Party producing
one or more of these substances shall, for the same
periods, ensure that its calculated level of
production of the controlled substances in Group I
of Annex C does not exceed, annually, ten per cent
of the calculated level referred to in paragraph 2 of
this Article. However, in order to satisfy the basic
domestic needs of the Parties operating under
paragraph 1 of Article 5, its calculated level of
production may exceed that limit by up to ten per
cent of its calculated level of production of the
controlled substances in Group I of Annex C as
referred to in paragraph 2.
6. Each Party shall ensure that for the twelvemonth period commencing on 1 January 2020, and
in each twelve-month period thereafter, its
calculated level of consumption of the controlled
substances in Group I of Annex C does not exceed
zero. Each Party producing one or more of these
substances shall, for the same periods, ensure that
its calculated level of production of the controlled
substances in Group I of Annex C does not exceed
zero. However:
i. each Party may exceed that limit on
consumption by up to zero point five per cent of
the sum referred to in paragraph 1 of this Article
in any such twelve-month period ending before 1
January 2030, provided that such consumption
shall be restricted to the servicing of refrigeration
and air conditioning equipment existing on 1
January 2020;
ii. each Party may exceed that limit on
production by up to zero point five per cent of the
average referred to in paragraph 2 of this Article in
any such twelve-month period ending before 1
January 2030, provided that such production shall
be restricted to the servicing of refrigeration and air
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Decision XIX/6 notes that no later than
2015, the Parties would consider
‘‘further reduction of production for
basic domestic needs’’ in 2020 and
beyond. Under paragraph 13 of Decision
XIX/6, the Parties will review in 2015
and 2025, respectively, the need for the
‘‘servicing tails’’ for developed and
developing countries. The term
‘‘servicing tail’’ refers to an amount of
HCFCs used to service existing
equipment, such as certain types of airconditioning and refrigeration
appliances.
B. How does the clean air act phase out
HCFCs?
The U.S. has chosen to implement the
Montreal Protocol phaseout schedule on
a chemical-by-chemical basis. In 1992,
environmental and industry groups
petitioned EPA to implement the
required phaseout by eliminating the
most ozone-depleting HCFCs first.
Based on the available data at that time,
EPA believed the U.S. could meet, and
possibly exceed, the required Montreal
Protocol reductions through a chemicalby-chemical phaseout that employed a
‘‘worst-first’’ approach focusing on
certain chemicals earlier than others. In
1993, as authorized by section 606 of
the CAA, the U.S. established a
phaseout schedule that eliminated
HCFC–141b first and would greatly
restrict HCFC–142b and HCFC–22 next,
followed by restrictions on all other
HCFCs and ultimately a complete
phaseout (58 FR 15014, March 18, 1993;
58 FR 65018, December 10, 1993).
On January 21, 2003 (68 FR 2820),
EPA promulgated regulations (2003
Final Rule) to ensure compliance with
the first reduction milestone in the
HCFC phaseout: The requirement that
by January 1, 2004, the U.S. reduce
HCFC consumption by 35 percent and
freeze HCFC production. In the 2003
Final Rule, EPA established chemicalspecific consumption and production
baselines for HCFC–141b, HCFC–22,
and HCFC–142b for the initial
regulatory period ending December 31,
2009. Section 601(2) states that EPA
may select ‘‘a representative calendar
year’’ to serve as the company baseline
for HCFCs. In the 2003 Final Rule, EPA
concluded that because the entities
eligible for allowances had differing
production and import histories, no
single year was representative for all
companies. Therefore, EPA assigned an
individual consumption baseline year to
each company by selecting its highest
ODP-weighted consumption year from
among the years 1994 through 1997.
conditioning equipment existing on 1 January
2020.’’
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EPA assigned individual production
baseline years in the same manner. EPA
also provided for new entrants that
began importing after the end of 1997
but before April 5, 1999, the date the
advanced notice of proposed
rulemaking was published. EPA took
this action to ensure that small
businesses that might not have been
aware of the impending rulemaking
would be able to continue in the HCFC
market.
The 2003 Final Rule apportioned
production and consumption baselines
to each company in amounts equal to
the amounts in the company’s highest
‘‘production year’’ or ‘‘consumption
year,’’ as described above. It completely
phased out the production and import
of HCFC–141b by granting 0 percent of
that substance’s baseline for production
and consumption in the table at 40 CFR
82.16. EPA did, however, create a
petition process to allow applicants to
request small amounts of HCFC–141b
beyond the phaseout. The 2003 Final
Rule also granted 100 percent of the
baselines for production and
consumption of HCFC–22 and HCFC–
142b for each of the years 2003 through
2009. EPA was able to allocate
allowances for HCFC–22 and HCFC–
142b at 100 percent of baseline because,
in light of the concurrent complete
phaseout of HCFC–141b, the allocations
for HCFC–22 and HCFC–142b,
combined with projections for
consumption of all other HCFCs,
remained below the 2004 cap of 65
percent of the U.S. baseline.
EPA allocates allowances for specific
years; they are valid between January 1
and December 31 of a given control
period (i.e., calendar year). Prior to
December 15, 2009, EPA had not
allocated any HCFC allowances for year
2010 or beyond. The regulations at
section 82.15(a) and (b) only addressed
the production and import of HCFC–22
and HCFC–142b for the years 2003–
2009. Through the 2009 Final Rule (74
FR 66412), EPA addressed the
production and import of HCFC–22 and
HCFC–142b for the 2010–2014 control
periods. Absent the granting of
calendar-year allowances, section 82.15
would have prohibited the production
and import of HCFC–22 and HCFC–
142b after December 31, 2009. The 2009
Final Rule allowed for continued
production and consumption, at
specified amounts, of HCFC–142b,
HCFC–22, and other HCFCs not
previously included in the allowance
system, for the 2010–2014 control
periods.
In the U.S., an allowance is the unit
of measure that controls production and
consumption of ODS. EPA establishes
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company-by-company baselines (also
known as ‘‘baseline allowances’’) and
allocates calendar-year allowances equal
to a percentage of the baseline for
specified control periods. A calendaryear allowance represents the privilege
granted to a company to produce or
import one kilogram (not ODPweighted) of the specific substance. EPA
allocates two types of calendar-year
allowances—production allowances and
consumption allowances. ‘‘Production
allowance’’ and ‘‘consumption
allowance’’ are defined at section 82.3.
To produce an HCFC for which
allowances have been allocated, an
allowance holder must expend both
production and consumption
allowances. To import an HCFC for
which allowances have been allocated,
an allowance holder must expend
consumption allowances. An allowance
holder exporting HCFCs for which it has
expended consumption allowances may
obtain a refund of those consumption
allowances upon submittal of proper
documentation to EPA.
Since EPA is implementing the
phaseout on a chemical-by-chemical
basis, it allocates and tracks production
and consumption allowances on an
absolute kilogram basis for each
chemical. Upon EPA approval, an
allowance holder may transfer calendaryear allowances of one type of HCFC for
calendar-year allowances of another
type of HCFC, with transactions
weighted according to the ODP of the
chemicals involved. Pursuant to section
607 of the CAA, EPA applies an offset
to each HCFC transfer by deducting 0.1
percent from the transferor’s allowance
balance. The offset benefits the ozone
layer since it ‘‘results in greater total
reductions in the production in each
year of * * * class II substances than
would occur in that year in the absence
of such transactions’’ (42 U.S.C. 7671f).
The U.S. remained comfortably below
the aggregate HCFC cap through 2009.
The 2003 Final Rule announced that
EPA would allocate allowances for
2010–2014 in a subsequent action and
that those allowances would be lower in
aggregate than for 2003–2009, consistent
with the next stepwise reduction for
HCFCs under the Montreal Protocol.
EPA stated its intention to determine
the number of allowances that would be
needed for HCFC–22 and HCFC–142b,
bearing in mind that other HCFCs
would also contribute to total HCFC
consumption. EPA noted that it would
likely achieve the 2010 reduction step
by applying a percentage reduction to
the HCFC–22 and HCFC–142b baselines.
EPA subsequently monitored the market
to estimate servicing needs and market
adjustments in the use of HCFCs,
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241
including HCFCs for which EPA did not
establish baselines in the 2003 Final
Rule.
In the 2009 Final Rule, EPA
determined both the estimated demand
for HCFC–22 during the 2010–2014
regulatory period and the percentage of
that estimated demand for which it was
appropriate to allocate allowances. As
described in section III.B. of this action,
EPA determined that the percentage of
the estimated demand allocated in the
form of allowances should not remain
constant from year to year but rather
should decline on an annual basis. For
2010, EPA allocated allowances equal to
80 percent of the estimated demand for
HCFC–22, concluding that reused,
recycled, and reclaimed material could
meet the remaining 20 percent. Under
the 2009 Final Rule, the percentage of
estimated demand for which there was
no allocation, and therefore would need
to be met through recycling and
reclamation, rose from 20 percent in
2010 to 29 percent in 2014 to ensure the
U.S. market would have a viable
reclamation industry and could meet
the 2015 stepwise reduction under the
Montreal Protocol.
The determinations EPA made in the
2009 Final Rule regarding (1) the total
estimated demand for HCFC–22 in
2010–2014 and (2) the percentage of that
estimated demand that EPA would
address through an allowance allocation
were not at issue in the litigation and
are unaffected by the Court’s decision.
As such, EPA did not revisit either
determination with respect to 2011 in
the 2011 Interim Final Rule (76 FR
47451), but rather relied on the existing
record from the 2009 Final Rule (74 FR
66412). The 2011 Interim Final Rule
established new baselines that (1)
credited the 2008 inter-pollutant trades
at issue in Arkema v. EPA based on the
Court’s decision and (2) reflected intercompany, single-pollutant baseline
transfers that occurred since the 2009
Final Rule was signed. The 2011 Interim
Final Rule also (3) allocated HCFC–22
and HCFC–142b allowances for 2011,
(4) clarified EPA’s policy on all future
inter-pollutant transfers, and (5)
updated company names.
C. What sections of the Clean Air Act
apply to this rulemaking?
Several sections of the CAA apply to
this rulemaking. Section 605 of the CAA
phases out production and consumption
and restricts the use of HCFCs in
accordance with the schedule set forth
in that section. As discussed in the 2009
Final Rule (74 FR 66416), section 606
provides EPA authority to set a more
stringent phaseout schedule than the
schedule in section 605 based on an
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EPA determination regarding current
scientific information or the availability
of substitutes, or to conform to any
acceleration under the Montreal
Protocol. EPA previously set a more
stringent schedule than the section 605
schedule through a rule published
December 10, 1993 (58 FR 65018).
Through the 2009 Final Rule, EPA made
a further adjustment to the section 605
schedule based on the acceleration
under the Montreal Protocol as agreed to
at the Meeting of the Parties in
September 2007. The more stringent
schedule established in that rule is
unaffected by the recent Court decision
and is therefore still in effect.
Section 606 provides authority for
EPA to promulgate regulations that
establish a schedule for production and
consumption that is more stringent than
what is set forth in section 605 if: ‘‘(1)
based on an assessment of credible
current scientific information (including
any assessment under the Montreal
Protocol) regarding harmful effects on
the stratospheric ozone layer associated
with a class I or class II substance, the
Administrator determines that such
more stringent schedule may be
necessary to protect human health and
the environment against such effects, (2)
based on the availability of substitutes
for listed substances, the Administrator
determines that such more stringent
schedule is practicable, taking into
account technological achievability,
safety, and other relevant factors, or (3)
the Montreal Protocol is modified to
include a schedule to control or reduce
production, consumption, or use of any
substance more rapidly than the
applicable schedule under this title.’’ It
is only necessary to meet one of the
three criteria. In the 2009 Final Rule,
EPA determined that all three criteria
had been met with respect to the
schedule for phasing out production
and consumption of HCFC–22 and
HCFC–142b.
As noted in the 2009 Final Rule,
while section 606 is sufficient authority
for establishing a more stringent
schedule than the section 605 phaseout
schedule, section 614(b) of the CAA
provides that in the case of a conflict
between the CAA and the Montreal
Protocol, the more stringent provision
shall govern. Thus, section 614(b)
requires the Agency to establish
phaseout schedules at least as stringent
as the schedules contained in the
Montreal Protocol. To meet the 2010
stepdown requirement, EPA is
continuing to allocate HCFC allowances
at a level that will ensure the aggregate
HCFC production and consumption will
not exceed 25 percent of the U.S.
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baselines. For more discussion of this
point, see 74 FR 66416.
Finally, section 607 addresses
transfers of allowances both between
companies and chemicals. EPA is
further clarifying the policy and
procedures applicable to permanent
inter-pollutant transfers in this action,
and is proposing a minor change to the
regulations governing inter-pollutant
transfers to provide additional clarity to
stakeholders.
D. How does this action relate to the
recent court decision?
Certain allowance holders affected by
the 2009 Final Rule filed petitions for
review in the U.S. Court of Appeals for
the District of Columbia Circuit. Among
other arguments, the petitioners,
Arkema, Inc., Solvay Fluorides, LLC,
and Solvay Solexis, Inc., contended that
the rule was impermissibly retroactive
because in setting the baselines for the
new regulatory period, EPA did not take
into account certain inter-pollutant
baseline transfers that petitioners had
performed during the prior regulatory
period. The 2011 Interim Final Rule
contained a description of those
transfers and the EPA approvals of those
transfers. As explained in the 2011
Interim Final Rule, the transfers at issue
occurred in 2008. Solvay Solexis, Inc.
submitted two Class II Controlled
Substance Transfer Forms for
consumption allowance transfers to
Solvay Fluorides, LLC on February 15,
2008, and March 4, 2008. Arkema, Inc.
submitted two Class II Controlled
Substance Transfer Forms for
consumption and production allowance
transfers on April 18, 2008. Each
company requested EPA’s approval to
convert HCFC–142b allowances to
HCFC–22 allowances, and checked a
box on the EPA transfer form indicating
that ‘‘baseline’’ allowances would be
transferred. EPA sent non-objection
notices to both Solvay Solexis, Inc. and
Solvay Fluorides, LLC on February 21,
2008 and March 20, 2008 and to
Arkema, Inc. in April 2008. The transfer
requests and EPA’s approvals were
attached to petitioners’ court filings and
are available in the docket for this
action.
In the Notice of Proposed Rulemaking
titled ‘‘Protection of Stratospheric
Ozone: Adjustments to the Allowance
System for Controlling HCFC
Production, Import, and Export,’’
published in the Federal Register at 73
FR 78680 on December 23, 2008 (2008
Proposed Rule), EPA requested
comments on establishing baselines for
the 2010–2014 regulatory period ‘‘with
or without’’ taking into account baseline
inter-pollutant transfers made during
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the 2003–2009 regulatory period (73 FR
78687). The proposed regulatory text
accounted for the inter-pollutant
transfers discussed above. The increase
in HCFC–22 baseline allowances for
Arkema, Inc. and Solvay Fluorides, LLC
presented in the 2008 Proposed Rule
resulted in a larger amount of HCFC–22
baseline allowances overall and
therefore a lower percentage of HCFC–
22 baselines allocated across the board
in each control period. Specifically, the
proposed shift resulted in a 16 percent
decrease in allocation share for all other
HCFC–22 allowance holders, and
increases for the petitioners: Arkema
and Solvay. For more detail on the effect
of these transfers, see section III.C. of
this preamble.
In the 2009 Final Rule, after
considering comments, EPA determined
that allowing inter-pollutant transfers
from one regulatory period to become a
part of the baseline in the next
regulatory period could undermine the
Agency’s chemical-by-chemical
phaseout approach and could encourage
market manipulation. EPA also
concluded that section 607 of the CAA
was best read as limiting inter-pollutant
transfers to those conducted on an
annual basis. For these reasons, EPA did
not take the 2008 inter-pollutant
transfers into account in establishing the
baselines for the 2009 Final Rule
covering 2010–2014.
The Court issued a decision on
August 27, 2010, agreeing with
petitioners that ‘‘the [2009] Final Rule
unacceptably alters transactions the
EPA approved under the 2003 Rule’’
(Arkema v. EPA, 618 F.3d at 3). The
Court vacated the rule in part, ‘‘insofar
as it operates retroactively,’’ and
remanded to EPA ‘‘for prompt
resolution,’’ (618 F.3d at 10). The Court
withheld the mandate for the decision
pending the disposition of any petition
for rehearing. On November 12, 2010,
EPA filed a petition for rehearing, which
was denied on January 21, 2011. The
mandate issued on February 4, 2011.
Because the Court vacated the rule
only in part, without specifying which
part or parts were vacated, EPA may
adopt a reasonable interpretation of the
vacatur’s extent. In doing so, EPA is
relying on its expertise in administering
the HCFC phaseout regulations under
Title VI of the CAA. First, EPA notes
that the rule contains elements that
were not at issue in the litigation. EPA
concludes that the vacatur has no effect
on allowances for any substances other
than HCFC–142b and HCFC–22, since
the petitioners’ claims and the opinion
itself discuss only those two substances.
Similarly, EPA concludes that other
discrete portions of the rule, such as the
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provisions on use and introduction into
interstate commerce, are unaffected by
the vacatur.
The baselines for HCFC–142b and
HCFC–22 were clearly at issue in the
litigation and indeed are the focus of the
Court’s opinion. The Court found that
‘‘the Agency’s refusal to account for the
Petitioners’ baseline transfers of interpollutant allowances in the Final Rule
is impermissibly retroactive,’’ (618 F.3d
at 9). Because baseline and calendar
year allowances are inextricably
linked,4 EPA has determined that the
Court’s vacatur voided the HCFC–22
and HCFC–142b baselines in 40 CFR
82.17 and 82.19 as well as the
percentage of baseline allocated for
those specific substances in 40 CFR
82.16 for all companies listed in those
sections.5 This means that until EPA
establishes new baselines and allocates
new calendar-year allowances,
production and import of these two
substances is prohibited under 40 CFR
82.15. Recognizing this scenario, on
January 28, 2011, EPA sent letters to
affected stakeholders informing them
that the Agency would exercise
enforcement discretion for a limited
period provided their production and
import did not exceed specified levels
and provided that they adhered to
additional conditions.
In determining the meaning of the
Court’s vacatur, EPA considered
whether this interpretation was
consistent with what the Court intended
and a good fit for the specific
circumstances, which include the goals
and design of the HCFC allowance
program and the basic structure of the
2009 Final Rule. While this
4 The reason baseline and calendar-year
allocations are inextricable is because calendar-year
allocations are expressed as a percentage of
baseline, and the percentage of baseline allocated
for a specific substance varies depending on the
sum of all company baselines for that substance.
The process works as follows for each specific
HCFC: First, all the company-specific baselines
listed in the tables at 40 CFR 82.17 and 82.19 are
added to determine the aggregate amount of
baseline production and consumption, respectively.
Second, EPA determines how many consumption
allowances the market needs for a given year, taking
into account recycled, reused, and reclaimed
material, and divides that amount by the aggregate
amount of baseline allowances. The resulting
percentage listed in the table at section 82.16
becomes what each company is allowed to consume
in a given control period. For example, a company
with 100,000 kg of HCFC–22 baseline allowances
would multiply that number by the percentage
allowed for 2011 (for example, 32 percent) to
determine its calendar-year allowance is 32,000 kg.
Historically and in this proposed rule, EPA has
allocated the same percentage of baseline
allowances for production as it does for
consumption.
5 The companies’ allocations are inter-related
because, as noted in footnote 4, the percentage of
baseline allocated varies according to the sum of the
company-specific baselines.
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interpretation is appropriate in this
instance, it is possible that another
interpretation would be more
appropriate in a case involving a
program with different goals, design, or
structure.
EPA’s initial response to the Court’s
partial vacatur was to issue the 2011
Interim Final Rule (76 FR 47451).
Through today’s notice, EPA is
proposing a way to address the Court’s
decision as it relates to the remainder of
the regulatory period ending December
31, 2014. In addition, the Agency is
taking comment on whether the vacatur
and remand should be interpreted as
applying to the 2010 allocations, and if
so, how allowances might be adjusted to
reflect this. See section III.B.4. for EPA’s
proposed approach to address 2010
allowances.
E. Comments Relevant to Recovery and
Reclamation Issues in This Rulemaking
Submitted in Response to the 2011
Interim Final Rule Allocating HCFC
Allowances
The EPA received 15 submissions
from 13 commenters in response to the
2011 interim final rule. Three comments
were received late. Specifically, the
Agency had asked for comment on
several issues relevant to HCFC–22
supply and the status of recovery and
reclamation, including: (1) Previous
estimates of HCFC–22 demand; (2) the
amount of virgin HCFC–22 currently in
inventory, available for reuse and/or
waiting for import from abroad; and (3)
whether there is an overall surplus of
the gas. The Agency received comments
directly answering these questions,
along with other comments that are of
relevance to this proposed rulemaking.
EPA is not providing a complete
response to comments on the 2011
interim final rule in this preamble;
however, EPA is acknowledging the
most relevant comments here in order to
highlight certain stakeholder concerns
regarding the future implementation of
the HCFC phaseout program. It is the
Agency’s responsibility to implement
Title VI of the CAA, and its policy
objective is to do so in a way that
smoothly transitions the U.S. away from
HCFCs to non-ODS alternatives.
Therefore, EPA is particularly interested
in stakeholder input regarding the status
of HCFC–22 recovery and reclamation,
because this information applies
directly to previously-stated policy
goals. This section notes the following
three issues discussed in comments to
the 2011 Interim Final Rule.
1. Supply of HCFC–22
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243
b. Economic incentives for recovery
and emissions prevention.
c. Effect of virgin gas supplies on dryshipped condensing units.
2. Providing Allowances to Reclaimers
3. Providing Allowances to
Manufacturers of HCFC Blends
1. Supply of HCFC–22
Nine commenters submitted
comments requesting that EPA decrease
consumption allowances for 2012–2014.
Another company also supported such a
decrease, as long as updated market
conditions indicate there is a need to do
so and all allowance holders are affected
proportionally. Commenters suggested
that excess supply was due to several
factors. Additionally, commenters stated
the price of HCFC–22 is low, indicating
that virgin supplies are not constrained
to the extent that the Agency had
anticipated. Some commenters pointed
to the unused consumption allowances
for 2010 as evidence of over-supply and
the need for decreasing the total number
of consumption allowances.
(a) Economic feasibility of
reclamation: Most commenters, many of
whom are reclaimers, are concerned
about the excess supply and low price
of virgin HCFC–22 because this
situation makes reclaim financially
unfeasible. EPA understands that
reclaimers can stay in business only if
reclaimed gas can be profitably sold for
a price that does not exceed the price of
virgin gas, and the price of virgin gas
will increase only when the supply has
contracted. The Agency promotes
reclamation via separation and
distillation, which requires very little
virgin gas, and recognizes that
reclaiming without significant blending
further increases the costs of
reclamation.
(b) Economic incentives for recovery
and emissions prevention: Commenters
also pointed out that the excess supply
and low price of HCFC–22 do not
incentivize recovery in general, and
likely promote venting and poor
maintenance practices. EPA agrees that
if the gas is not valuable then there will
be little incentive to reuse it or
proactively prevent leaks, in addition to
increasing the likelihood of venting
(which is illegal under section 608 of
the CAA).
(c) Effect of virgin gas supplies on dryshipped condensing units: Two
commenters also specifically mention
the increased popularity in dry-shipped
condensing units that are eventually
charged with HCFC–22 as a symptom of
this over-supply. The Agency recognizes
that the majority of commenters believe
that there is an excess of HCFC–22 on
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the market, which has direct negative
consequence for reclaim and recovery,
and thus overall ODS emissions.
Additionally, EPA has received a
petition (included in the docket) from
the Carrier Corporation, dated February
3, 2011, concerning dry-shipped HCFC–
22 condensing units. EPA is taking
comment on whether the installation of
dry-shipped HCFC–22 condensing units
will affect the phaseout of virgin HCFC–
22 production and import.
EPA undertook an analysis to gauge
whether there is a surplus of HCFC–22
and, if so, how large the surplus is. A
memo in the docket for this rulemaking
details EPA’s analysis of the HCFC–22
market. The results indicate EPA should
consider allocating between 11 to 47
percent less per year between 2012 and
2014 relative to the amounts that
appeared in the 2009 Final Rule.
Consequently, EPA is proposing in this
rulemaking to allocate fewer HCFC–22
consumption allowances than
contemplated in the 2009 Final Rule for
2012–2014 in order to promote recovery
and reclamation and encourage
transition to non-ODS alternatives (see
section III.B. and III.C.). As stated in the
2009 Final Rule, ‘‘The Agency strongly
encourages increased recovery and
either recycling or reclamation of
HCFC–22 * * * Recovery becomes even
more important in light of the 2015
Montreal Protocol phasedown step,
when the U.S. HCFC consumption cap
is reduced from 3,810 ODP-weighted
metric tons to 1,524 ODP-weighted
metric tons,’’ (74 FR 66422).
2. Providing Allowances to Reclaimers
Two commenters requested that EPA
provide HCFC allowances to certified
reclaimers. As explained in the report
titled ‘‘Analysis of Equipment and
Practices in the Reclamation Industry,’’
which is included in the docket for this
rulemaking, ‘‘refrigerant reclamation
refers to the reprocessing and upgrading
of recovered refrigerant through such
mechanisms as filtering, drying,
distillation and chemical treatment in
order to restore the substance to
specifications outlined in the AirConditioning, Heating, and Refrigeration
Institute (AHRI)’s Standard 700–1995.’’
The commenters argue increasing
allocations to reclaimers would increase
the amount of reclaimed HCFCs
available for purchase. The comments
are similar to those submitted prior to
the finalization of the 2009 Final Rule,
which allocated HCFC allowances for
2010–2014. EPA responded to this
request at the time (74 FR 66422;
Response to Comments document for
the 2008 NPRM), but discusses the issue
further here.
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The Agency’s primary concern is that
providing reclaimers with allowances
could foster unsustainable reclamation
practices that rely on blending instead
of investing in the technology to fully
reclaim HCFCs. Based on the phaseout
schedule and the decrease in annual
allocations, reclamation through
separation and distillation will be more
important in 2015 when the HCFC–22
allocation must drop by at least 45
percent from 2010 levels and absolutely
necessary by 2020, by which time
import and production of HCFC–22
must be phased out entirely. In
addition, many businesses have either
found a way to secure reliable access to
virgin HCFCs or have made investments
to reclaim HCFCs in a sustainable way,
without a direct allocation of
allowances.
EPA is also concerned that providing
allowances to reclaimers does not
address the key structural issue that the
industry and the HCFC transition are
facing: The price of HCFC–22 is too low
to foster reclamation and is not sending
the necessary signal to move consumers
to non-ODS alternatives. While
providing allowances to reclaimers
would likely decrease the cost to
recover and reclaim HCFCs, EPA is
concerned about what effect providing
allowances to reclaimers would have on
the market price of HCFC–22. EPA is
seeking comment on whether providing
allowances to reclaimers would affect
the market price of HCFC–22, and what
effect that price change would have on
the transition away from ODS and the
sustainability of the reclamation
industry.
EPA continues to believe that
allocating fewer allowances is the best
way to foster reclamation and recovery.
Thus, this proposal does not include an
allocation for reclaimers. However, the
Agency has included the relevant
comments on the Interim Final Rule in
the docket for this rulemaking and
welcomes further comment on this issue
from all interested parties.
3. Providing Allowances to
Manufacturers of HCFC Blends
One small business has informed EPA
that it cannot acquire either HCFC
allowances or the HCFCs it needs to
manufacture its HCFC blend (see the
letters from ICOR dated May 17, 2011
and September 6, 2011). The company
asserts that the cap and trade system is
in practice ‘‘cap and no trade,’’ where
companies hold onto their allowances,
even if they have no intention of using
them. The commenter argues that this
leads to artificially high prices for
HCFCs and HCFC allowances. To
remedy this situation, the commenter
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requests that EPA take unused
allowances and provide those
allowances to companies that either
purchased HCFCs or HCFC
consumption allowances in 2008 and
2009. EPA notes that the inability to
acquire allowances and/or HCFCs
themselves does not appear to be a
widespread problem, as numerous
companies have made a significant
number of transfers over the last year
alone, and no other company has
indicated it cannot acquire HCFCs.
However, EPA is taking comment on
whether other companies are having
difficulty acquiring HCFCs or HCFC
allowances.
Some historical background may help
to provide context on how EPA
provided flexibility for small businesses
when establishing the HCFC allocation
system. In the 2003 Final Rule,
published January 21, 2003, EPA
assigned individual company baselines
by considering the highest production
and consumption years for every
company between the years 1994–
1997—a four year period preceding
regulation of the production and import
of HCFCs. ‘‘Consumption’’ is defined by
the Clean Air Act as ‘‘the amount of that
substance produced in the United
States, plus the amount imported,
minus the amount exported,’’ (42 U.S.C.
7671). A company had to be
manufacturing or importing HCFCs at
that time in order to be assigned a
baseline. In addition, the EPA provided
an exception allowing new entrants
provided that they began importing after
the end of 1997, but before April 5,
1999, the date the EPA published the
advanced notice of proposed
rulemaking for the regulatory period
2003–2009. The Agency believed that
such small businesses might not have
been aware of the impending
rulemaking that would affect their
ability to continue in the HCFC market.
In addition to the exception for late
entrants made in the 2003 Final Rule,
there is significant flexibility in the
types of transfers companies can
conduct. Companies can transfer
allowances between companies and, on
a temporary basis, between chemicals. A
guidance memo, titled ‘‘Flexibility in
the HCFC Allowance System,’’
describing this flexibility further is
available in the docket and on EPA’s
Web site. Companies can also purchase
HCFCs at the wholesale price, which,
according to comments on the 2011
Interim Final Rule, has been decreasing.
The allocation system in part was
established to discourage the use of
HCFCs and companies’ continuation in
the HCFC market. As stated in the 2003
Final Rule, ‘‘businesses that desired an
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allocation of HCFC allowances would
have known the risks of jumping into
the business at this juncture’’ (66 FR
38073). Since that statement more than
nine years ago, access to information
and knowledge of the risks regarding
entering or continuing in the HCFC
market have only increased.
Furthermore, new entrants have entered
the market by purchasing consumption
allowances, as EPA predicted they
could back in 2003. All entities wishing
to enter the HCFC import or production
market can continue to purchase
allowances for HCFCs.
As the market continues to decrease
in size, EPA does not believe that
expanding the pool of allowance
holders is necessary to prevent
disruption of the continued servicing of
existing equipment. EPA explored
several options that would have
expanded the number of allowance
holders in the 2008 NPRM (73 FR
78867) and determined the current
approach with adjustment for transfers
of baseline allowances was appropriate
(74 FR 66419; Response to Comments
for the 2008 NPRM). Given EPA’s intent
to phase down, and ultimately phase
out, the use of HCFCs, consistent with
the requirements of the CAA and
obligations under the Montreal Protocol,
EPA believes it is justified in continuing
to allocate only to those entities who
participated in the market at the initial
stages, as well as those that have entered
the market by purchasing HCFC
baseline allowances in accordance with
the established practices. EPA does not
believe that providing allowances to
companies that were not importing or
producing HCFCs prior to EPA
regulation is appropriate at this time
given the disruption it would create to
the existing regulatory framework.
However, in light of the large number of
HCFC allowances that were not used in
2010 and the difficulty at least one
company is having in getting HCFCs,
EPA welcomes comments on whether
an allocation to manufacturers of HCFC
blends who are having difficulty
acquiring HCFCs or HCFC allowances
would be appropriate. Commenters
supporting such an allocation should
consider (1) how EPA might determine
the total amount of such an allocation,
(2) how EPA might determine which
companies should receive allowances,
(3) how EPA would verify that
allowance holders are refusing to sell
HCFCs and HCFC allowances, (4) how
EPA might set baselines for these
companies, (5) whether EPA should
provide allowances in addition to the
amount proposed in this rule, or as part
of the amount proposed in this rule, and
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(6) how providing allowances to an
additional set of companies would affect
the U.S. transition away from HCFCs.
III. How does EPA propose to allocate
HCFC–22 and HCFC–142b allowances
for 2012–2014?
EPA is proposing to continue the
system established in previous
rulemakings (68 FR 2820, 74 FR 66412,
76 FR 47451) to address HCFC
production and import in the U.S. The
process works as follows for each
specific HCFC: First, all the companyspecific baselines listed in the tables at
40 CFR 82.17 and 82.19 are added to
determine the aggregate amount of
baseline production and consumption,
respectively. Second, EPA determines
how many consumption allowances the
market needs for a given year, taking
into account recycled, reused, and
reclaimed material, and divides that
amount by the aggregate amount of
baseline allowances. The resulting
percentage listed in the table at section
82.16 becomes what each company is
allowed to consume in a given control
period. For example, a company with
100,000 kg of HCFC–22 baseline
allowances would multiply that number
by the percentage allowed for the year
(for example, 32 percent in 2011) to
determine its calendar-year allowance is
32,000 kg. Historically, EPA has
allocated the same percentage of
baseline allowances for production as it
does for consumption.
Specifically, EPA is proposing to (1)
establish 2012–2014 company-bycompany consumption and production
baselines for HCFC–22 and HCFC–142b
in the tables at 40 CFR 82.17 and 82.19
identical to the baselines established in
the 2011 Interim Final Rule (76 FR
47468), (2) allocate company-bycompany production and consumption
allowances for these substances for
2012–2014 by establishing percentages
of production and consumption
baselines in the table at section 82.16
and (3) revise the regulatory text at 40
CFR 82.23 to make the procedure for all
future inter-pollutant transfers clear.
EPA will address the allocations for the
control periods beyond 2014 at a later
date. All aspects of the 2009 Final Rule
promulgated on December 15, 2009 (74
FR 66412) that are not addressed in this
proposed rule are unchanged.
Additionally, EPA notes that
beginning January 1, 2015, section 605
of the CAA prohibits the use and
introduction into interstate commerce of
any HCFC unless it ‘‘(1) has been used,
recovered and recycled; (2) is used and
entirely consumed (except for trace
quantities) in the production of other
chemicals; or (3) is used as a refrigerant
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245
in appliances manufactured prior to
January 1, 2020.’’ In addition, EPA’s
regulations at 40 CFR 82.15 restrict use
and introduction into interstate
commerce of HCFC–141b, HCFC–142b,
and HCFC–22 beginning in 2010, with
limited exceptions. If entities will need
HCFCs in 2015 and beyond for uses
other than the exemptions contained in
section 605, they should contact EPA
prior to 2013. Entities should
understand that the statutory
prohibition in section 605 generally will
prevent EPA from accommodating such
needs, with the possible exception of de
minimis quantities.
A. What baselines does EPA propose to
use for HCFC–22 and HCFC–142b
allowances?
In the 2009 Final Rule, EPA presented
the allocation structure for HCFC–22
and HCFC–142b for the control periods
2010–2014: Allocating a percentage of
the baseline production and
consumption allowances. The rationale
for this system is discussed further at 74
FR 66412. The Court found no fault
with EPA’s framework for allocating
HCFCs in the 2009 Final Rule, except
the aspects of the rule deemed to be
retroactive, i.e., not taking into account
inter-pollutant baseline transfers that
occurred in the prior regulatory period
in establishing company-specific
baseline allowances. To address this,
EPA is proposing to establish baselines
for 2012–2014 identical to the HCFC–22
and HCFC–142b baselines established in
the 2011 Interim Final Rule (76 FR
47451) that reflect past inter-pollutant
baseline transfers deemed permanent by
the Court.
EPA cited several reasons why it
would prefer to set baselines without
taking into account inter-pollutant
transfers in the 2009 Final Rule (74 FR
66420), the Response to Comments
document included in the record for
that rulemaking, and the 2011 Interim
Final Rule (76 FR 47451). However, EPA
is recognizing the 2008 transfers in
establishing the baselines through 2014
in accordance with the Court’s decision.
The Agency is providing advance notice
that for the 2015–2019 regulatory
period, it would consider using more
recent production and import data than
the 1994–1997 data used to set baselines
for the first time in the 2003 Final Rule.
The Agency is particularly interested in
stakeholders’ views on whether there
would be an environmental benefit to
doing so.
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B. What factors did EPA consider in
proposing allocation amounts for
HCFC–22 and HCFC–142b?
In the 2009 Final Rule, EPA decided
to allocate HCFC–22 and HCFC–142b
allowances based on the projected
servicing needs for those compounds,
taking into account the amount of those
needs that can be met through recycling
and reclamation. EPA is not changing
that approach in this proposed
rulemaking and continues to believe it
is necessary to promote use of reused,
recycled, and reclaimed material in
anticipation of the 2015 phasedown
step. However, EPA is proposing to
allocate fewer consumption allowances
for HCFC–22 relative to the 2009 Final
Rule based on analysis of updated
market conditions. The proposed
allocation and the supporting
documentation are discussed in section
III.B.2. Regardless of the extent to which
the total number of consumption
allowances differs from the total number
allocated in the 2009 Final Rule, the
specific amounts allocated per company
will be different than the 2009 Final
Rule. In accordance with the Court’s
decision in Arkema v. EPA, the Agency
is proposing to reflect the 2008 interpollutant transfers in companies’
baselines, and EPA therefore needs to
allocate a different percentage of
company baselines in order for the
aggregate number of annual HCFC
consumption allowances to be less than
(or equal to) the 2009 Final Rule. EPA
is also proposing to allocate different
percentages of baseline for annual
consumption than for annual
production (described in the rest of the
preamble as ‘‘decoupling’’).
Separate from the proposed allocation
change, EPA is taking comment on
whether or not to provide more HCFC–
22 and/or HCFC–142b consumption
and/or production through this
rulemaking than it did in the 2009 Final
Rule as a result of the unforeseen
circumstances presented by the Court’s
decision in Arkema v. EPA. While the
Agency’s preference is not to provide
recoupment, EPA is considering an
approach to the 2013 allocation or 2013
and 2014 allocations that could allocate
allowances to account for lost
opportunities to produce and consume
in 2010, given that 2010 allowance
levels were based on baselines that are
inconsistent with the Court’s finding
(section III.B.4. discusses this in more
depth).
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1. How important is HCFC–22 relative
to HCFC–142b for servicing existing
equipment?
HCFC–22 is the most widely-used
HCFC. The demand for its use in
servicing existing equipment was the
primary factor affecting EPA’s allocation
of production and consumption
allowances of HCFCs for the current
regulatory period. Prior to issuing the
2009 Final Rule and the 2009 Servicing
Tail Report, EPA issued and sought
comment on three versions of a draft
report analyzing servicing demand for
the HCFC appliances in the U.S.
refrigeration and air-conditioning sector
projected to be in service from 2010–
2019 (all versions available at Docket
EPA–HQ–OAR–2008–0496: Published
November 4, 2005 at 70 FR 67172;
released at a stakeholder meeting on
September 29, 2006; published
December 23, 2008, with 2008 Proposed
Rule). The Servicing Tail Report focuses
on air-conditioning and refrigeration
appliances because such equipment
represents the bulk of the servicing
need. In addition, the servicing
exception to the use ban for HCFC–22
and HCFC–142b pertains only to use as
a refrigerant in such equipment. Under
40 CFR 82.15(g) nearly all other uses of
newly produced material for these two
HCFCs were banned effective January 1,
2010. HCFC–142b has primarily been
used as a foam blowing agent, a use that
was prohibited beginning in 2010 (40
CFR 82.15(g)). The projected servicing
demand for existing refrigeration
equipment containing HCFC–142b is
extremely low: Approximately 100 MT.
EPA therefore focused the analysis on
HCFC–22 because that compound is the
predominant HCFC in the installed base
of air-conditioning and refrigerant
equipment for which servicing in the
U.S. will likely continue.
As discussed in the 2009 Final Rule,
the majority of HCFC–22 equipment that
is projected to be in use from this point
onward will be air-conditioning
applications, including window units,
packaged terminal units, unitary airconditioning, chillers, dehumidifiers,
water and ground source heat pumps,
and motor vehicle air-conditioning in
buses and trains. The report projected
that approximately 145.6 million units
of all such types of HCFC–22 airconditioning equipment were in use in
2010, decreasing by about 41 percent in
2015 and 86 percent in 2020. In
addition, approximately 3.8 million
units of HCFC–22 refrigeration
equipment were in use in 2010. The
installed base of HCFC–22 refrigeration
equipment is projected to decrease from
2010 levels by about 44 percent in 2015
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and 75 percent in 2020. For more on the
Servicing Tail Report, see 74 FR 66424
and the Servicing Tail Report included
in the docket.
EPA estimates that the servicing need
for HCFC–22 will continue to decrease
each year, and consistent with the 2009
Final Rule, EPA proposes to account for
this by allocating a smaller amount for
2012 than was allocated for 2011. This
approach is described in section III.B.3.
of this action, along with more recent
market data on the need for, and
availability of, HCFC–22.
2. Can servicing needs be met with
virgin and recovered material?
In the 2009 Final Rule, the Agency
recognized that servicing demand can
be met with a combination of newlymanufactured or imported HCFCs
(virgin HCFCs) and HCFCs that have
been recovered and either reused,
recycled or reclaimed. Therefore, EPA
did not anticipate that virgin HCFC–22
would need to be produced or imported
to meet the entire HCFC–22 servicing
demand in each year between 2010 and
2014. The Servicing Tail Report
analyzes various scenarios regarding
reclamation. EPA continues to believe
that reused, recycled, and reclaimed
material can help meet HCFC–22
servicing needs and is therefore
proposing to maintain the same
approach to meeting servicing needs at
this time. While the Agency is not
changing its approach, EPA believes
that the percentage of overall demand
that can be met by reclaimed material is
higher than originally projected. EPA is
taking comment on the new projections
of reclaim capabilities outlined in the
memo included in the docket for this
rulemaking titled, ‘‘Analysis of HCFC–
22 Servicing Needs in the U.S. Air
Conditioning and Refrigeration Sector:
Additional Considerations for
Estimating Virgin Demand,’’
(Adjustment Memo).
3. How would the allocation decline?
As explained in the preamble to the
2009 Final Rule, without year-to-year
reductions in the allocations for virgin
HCFC–22, the HCFC–22 market could
be oversaturated, and the contribution
of reused, recycled, and reclaimed
refrigerant would decrease, both in the
total number of kilograms and as the
proportion of overall need.
EPA is particularly concerned with
encouraging a smooth transition to the
2015 stepdown. At that date, the U.S.
must meet a 90 percent reduction below
the baseline for all HCFCs. EPA’s
Servicing Tail Report shows that even a
20 percent recovery rate would be
insufficient to meet the demand for
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HCFC–22 in 2015. As shown in Table 4–
5 in the report, demand for HCFC–22 in
2015 was projected to be 38,800 MT
while the cap for all HCFCs equates to
27,709 MT of HCFC–22 (assuming no
allocation for any other HCFCs). In
developing the 2009 Final Rule, EPA
calculated that to meet the total demand
in 2015, the recovery rate would have to
increase to 26 percent (representing 29
percent of total servicing demand).
EPA determined in the 2009 Final
Rule a level of allocation projected to
meet the servicing demand over 2010–
2014. In addition to EPA’s request for
comment on whether to address or not
address 2010 allowances (see section
III.B.4.), the Agency is proposing to
establish lower overall HCFC–22
consumption allocation levels for 2012–
2014 than those the Agency determined
were appropriate in the 2009 Final Rule.
The Adjustment Memo in the docket to
this rulemaking discusses recent data
and stakeholder feedback that indicate
that demand for virgin HCFC–22 is
lower than originally projected, and that
the number of consumption allowances
should be 11 to 47 percent lower
relative to the 2009 Final Rule.
Specifically, the memo examines (1)
surplus inventory of HCFC–22 from past
years, (2) reclaimer capacity, and (3)
increased recovery and re-use of HCFC–
22 from the large retail food sector. EPA
is taking comment on the analysis,
supporting data, and assumptions
presented in the Adjustment Memo.
Since EPA is continuing to allow the
use of existing HCFC–22 appliances
manufactured prior to January 1, 2010,
reused, recycled, and reclaimed HCFC–
22 will become more valuable as the
phaseout progresses. The demand for
HCFC–22 to service existing equipment
will provide an economic incentive to
increase the quantities of recovered
HCFC–22 available for reuse, recycling,
and reclamation. Therefore, the Agency
believes that establishing a lower
aggregate HCFC–22 consumption
allocation for 2012–2014 than in the
2009 Final Rule is not only justified by
decreased demand and the availability
of surplus inventory from past years, but
also because a lower virgin supply will
further incentivize recovery and
reclamation. The docket for the 2009
Final Rule (EPA–HQ–OAR–2008–0496)
provides information on EPA’s past
assumptions regarding the availability
of reused, recycled and reclaimed
HCFC–22 to meet servicing demand,
while the Adjustment Memo to this
docket discusses recent changes in the
HCFC–22 market.
In the 2009 Final Rule, EPA
determined it was appropriate to
establish an annual step-down with the
assumption that the total demand to be
met from recovered HCFC–22 would
equal 12,500 MT each year. This is
approximately the amount EPA
projected would be needed to meet the
servicing demand in 2015. Using this
approach, the aggregate allocation for
consumption would equal
approximately 40,700 MT in 2012, and
decrease each year after, as shown in
Table 1. These values are derived by
subtracting 12,500 MT from the
estimated servicing demand each year.
However, in light of changes to both
virgin demand and reclaimer
capabilities, EPA believes that the
portion of demand met by recovered
HCFC–22 could range from 12,500 MT
to 19,700 MT each year (see the
Adjustment Memo), and that reduced
demand, along with surplus inventory
estimates, warrant a significantly lower
total allocation for 2012, 2013 and 2014.
While Table 1 shows how the total
allocation in the 2009 Final Rule was
determined, the Agency is now
proposing to allocate between 11 and 47
percent fewer consumption allowances
for 2012 to 2014. EPA will not issue
HCFC–22 and HCFC–142b allowances
for 2015 or later until a future
rulemaking.
TABLE 1—2009 FINAL RULE PROJECTION OF AMOUNT OF ANNUAL HCFC–22 DEMAND TO BE MET BY ALLOCATED AND
RECOVERED MATERIAL
2012
2013
2014
53,200
12,500
48,400
12,500
43,600
12,500
Total Allocation (MT) ................................................................................................
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Estimated Demand (MT) .................................................................................................
Recovered Amount (MT) .................................................................................................
40,700
35,900
31,100
As the total servicing demand
decreases, assuming the supply of
recovered HCFCs stays at a constant
level results in recovered material
comprising a greater proportion of the
total demand each year. Using this
assumption and the projected demand
level from the 2009 Final Rule, the
percentage of the total servicing demand
to be met with recovered material would
rise from 21.6 percent of total demand
in 2011 to 28.7 percent in 2014, though
the total amount of recovered material
needed would remain at 12,500 MT for
each year. In the Adjustment Memo,
EPA considers two HCFC–22 allocation
scenarios for each year. The larger
allocation scenario considers: (1) An
annual surplus inventory drawdown of
6,000 MT; (2) the same 12,500 MT of
annual recovery and reclamation used
in the 2009 Final Rule; and (3) a
minimum expected recovery and reuse
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rate of 20 percent of total demand in the
large retail food sector each year. The
smaller allocation scenario considers:
(1) The same surplus inventory
drawdown of 6,000 MT; (2) an annual
reclamation amount of 19,700 MT, or 35
percent of estimated servicing demand
in 2012; and (3) a maximum expected
recovery and reuse rate of 70 percent of
total demand in the large retail food
sector. These two scenarios indicate that
EPA should decrease annual allocations
relative to the 2009 Final Rule by
between 11 and 47 percent each year—
with the exact range varying slightly
year by year. As summarized in Table 4
of the Adjustment Memo, the Agency is
proposing to issue HCFC–22
consumption allowances as follows:
Between 25,100 and 36,200 MT in 2012
(a decrease of 11 to 38 percent); between
20,800 and 31,400 MT in 2013 (a
decrease of 13 to 42 percent) and
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between 16,400 and 26,300 MT in 2014
(a decrease of 15 to 47 percent). As
percentages of baseline, these proposed
amounts correspond to allocations of
17.7 to 25.5 percent in 2012, 14.7 to 22.1
percent in 2013, and 11.6 to 18.5
percent in 2014.
In summary, the Agency is proposing
to reduce consumption allowances
relative to the 2009 Final Rule. The
Agency is also proposing to decouple
production allowances and allocate
either the same amount of production as
in the 2009 Final Rule or the same
percentage of baseline as in the 2009
Final Rule. A memo included in the
docket for this rulemaking provides an
overview of the various scenarios (see
the Overview Memo).
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4. How will EPA address the court’s
decision with regard to 2010 HCFC
allowances?
EPA’s first step in addressing the
Court’s decision was to establish
baselines for 2011 that reflected the
2008 inter-pollutant transfers that were
at issue in the litigation and to allocate
allowances for 2011 as a percentage of
those baselines. As noted in the Interim
Final Rule (76 FR 47451), EPA
interprets the Court’s decision as
applying, at a minimum, to the baseline
and calendar-year allowances for 2011–
2014. The Agency is taking comment on
whether to interpret the decision as
applying to the 2010 allocation, and if
so, how allowances in future control
periods might be adjusted to reflect this.
The petitioners in the case, Arkema and
Solvay, have stated that EPA should
‘‘restore the allowances of which
Arkema and Solvay were deprived
unlawfully in 2010,’’ or ‘‘provide a
method to compensate Arkema and
Solvay for year 2010 allowances that
rightfully should have been available’’
(February 4, 2011 letter to Drusilla
Hufford, EPA, from William Hamel,
Arkema, and March 7, 2011 letter to
Drusilla Hufford, EPA, from Don Magid,
Solvay, both available in the docket for
this rulemaking). As a result of these
requests, EPA is considering whether to
grant additional allowances for all
companies that would have received
higher allocations in 2010 if the 2008
inter-pollutant transfers had been
reflected in the baselines published in
the 2009 Final Rule. The companies
affected, and the additional allowances
they would have received (hereinafter
described as ‘‘recoupment allowances’’),
are included in Table 2, below.
TABLE 2—PROPOSED RECOUPMENT ALLOWANCES
Consumption
(kg)
Chemical
Arkema .....................................................................
DuPont ......................................................................
Honeywell .................................................................
Solvay Fluorides .......................................................
Solvay Solexis ..........................................................
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Company
HCFC–22 ..................................................................
HCFC–142b ..............................................................
HCFC–142b ..............................................................
HCFC–22 ..................................................................
HCFC–142b ..............................................................
EPA is taking comment on four
possible options with regard to this
issue: (1) Providing recoupment
allowances in 2013 in addition to the
aggregate level of production and
consumption specified in the 2009 Final
Rule; (2) allocating recoupment
allowances over two years (2013–2014)
in addition to the aggregate level of
production and consumption specified
in the 2009 Final Rule; (3) allocating
recoupment allowances from the
aggregate level of production and
consumption specified in the 2009 Final
Rule over two years (2013–2014); and
(4) treating missed allowances from
2010 as impossible to recoup. EPA is
also taking comment on: (1) Whether it
should provide recoupment for HCFC–
22 and HCFC–142b, or just HCFC–22
allowances; and (2) whether it should
provide recoupment for production and
consumption, or just consumption
allowances. EPA is seeking comment on
these two points because: (1) The
Court’s decision only addresses the
losses of the petitioners Arkema and
Solvay, who appear to be most
concerned with recoupment for HCFC–
22 allowances; (2) neither of the
petitioners has specifically requested
recoupment for production allowances;
and (3) while Solvay Solexis could
receive recoupment allowances for
HCFC–142b production (see Table 2), it
would receive nearly ten times more
HCFC–142b production allowances
under this proposed rule absent
recoupment than the 2009 Final Rule,
which could avoid the need for HCFC–
142b production allowance recoupment.
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When considering the options included
in this section, commenters should
consider options 1–4 providing or not
providing recoupment for HCFC–142b
and providing or not providing
recoupment for production allowances.
Additionally, EPA recognizes that any
option to provide recoupment in
addition to the aggregate level of
consumption is, to some extent, in
tension with the proposal to decrease
the aggregate allocation and might
impede the intended effects of
allocating fewer HCFC–22 allowances.
If EPA provides recoupment, the
Agency is proposing to address this
issue in addition to the proposed
establishment of baselines reflecting the
Court’s decision on past inter-pollutant
transfers, and the proposed allocation of
HCFC–22 production and consumption
allowances. Under each of these
approaches, the U.S. would still be well
below its HCFC cap under the Montreal
Protocol. EPA is not proposing a
recoupment option that would begin in
2012 because waiting until 2013
provides companies that may receive
recoupment allowances time to prepare
for the increase in calendar-year
allowances.
Under option 1, each company would
get the percentage of baseline listed in
proposed section 82.16(a)(1). The
companies listed in Table 2 would
receive an additional one-time
allocation in 2013 of the amount
specified in the table. Granting
recoupment allowances under option 1
would add 329 ODP-weighted MT of
allowed HCFC consumption and 280
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Sfmt 4702
4,749,692
2,339
58,291
1,157,895
0
Production
(kg)
4,611,848
0
107,097
0
289,800
ODP-weighted MT of allowed HCFC
production in 2013. The result is an
increase in allowed HCFC consumption
and production (ODP-weighted) by 17
percent and 15 percent, respectively,
beyond that allowed in the 2009 Final
Rule, assuming constant levels of
overall consumption and production.
While the number of allowances would
be higher in 2013 than envisioned in the
2009 Final Rule, it would not increase
environmental damage during the
regulatory period from 2010–2014
relative to the projections in the 2009
Final Rule: Approximately 425 ODPweighted MT of HCFC consumption
allowances and approximately 930
ODP-weighted MT of HCFC production
allowances were not used by allowance
holders in 2010 (source: EPA’s ODS
Tracking System). This one-year
increase in allowances in 2013 would
keep the aggregate level of consumption
and production for 2010–2014 below
the level envisioned in the 2009 Final
Rule. Since the 2014 allocation would
be unchanged from (or less than) the
2009 Final Rule level, option 1 could be
preferable to a two-year recoupment
option because it could smooth the
transition to the 2015 stepdown under
the Montreal Protocol. Option 1 would
also restore the companies’ lost
opportunity to produce or consume in
2010 without reducing the amount of
allowances other companies receive
further.
Option 1 is not without
disadvantages. First, it would increase
the number of allowances available for
use in 2013, which might impede the
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development of a viable reclamation
industry and hamper the transition to
the 2015 stepdown. Second, this option
significantly increases the number of
allowances in 2013 for certain
companies receiving recoupment,
meaning that those companies arguably
could have difficulty selling the full
amount of HCFC–22 produced or
imported with allowances that year.
However, if companies receiving extra
allowances all in one year cannot sell
the full amount in that year, they may
store produced and/or imported
material for sale or use in later years, or
sell the allowances to other producers or
importers for use in that same year.
Third, companies not receiving
recoupment would have the same
number of allowances as they would
under a no-recoupment scenario, but
they would have a smaller share of all
allowances allocated under this option
compared to a no recoupment scenario.
Under the second option, recoupment
allowances would be provided over two
years (2013–2014) instead of one year as
in option 1. Each entity listed in Table
2 would receive half of the amount
listed in the table in 2013 and 2014 in
addition to the percentage of baseline as
listed in proposed section 82.16(a)(1).
Option 2 would increase allowed
consumption and production relative to
the 2009 Final Rule levels by 8 percent
in 2013 and by 10 percent and 9
percent, respectively, in 2014. This
options shares some of the advantages of
option 1: (1) The amount allocated
between 2010 and 2014 is still below
the amount envisioned as total usage
during that period in the 2009 Final
Rule when taking into consideration the
number of allowances not used in 2010,
and (2) it restores the companies’ lost
opportunity to produce or consume in
2010 without reducing the amount of
allowances other companies would
receive under no recoupment.
A significant downside to this option
is that it increases the number of
allowances available in 2013 and 2014,
and may hamper the smooth transition
in 2015 to 10 percent of baseline under
the Montreal Protocol, since the
decrease between the 2014 allocation
and 2015 allocation for HCFC–22 would
be larger under this option than in
option 1. Also, like option 1, companies
who would not receive recoupment
would have a smaller share of all
allowances compared to a no
recoupment scenario.
Under option 3, EPA could provide
recoupment allowances as part of the
aggregate allocation level. The letters
included in the docket from Don Magid,
Solvay Fluorides, to Drusilla Hufford,
EPA, dated March 7, 2011, and from
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William Hamel, Arkema, to Drusilla
Hufford, EPA, dated February 4, 2011,
express support for this option. One
way to do this would be to allocate
HCFC–22 allowances (both recoupment
for 2010 and their allotted percentage of
baseline for 2013 and 2014) to the
companies listed in Table 2, and then
allocate the remainder to all other
allowance holders by revising the
percentage of baseline allocated. A
memo to the docket explains this
approach in more detail (see ‘‘Memo:
Recoupment Options’’). Providing all
recoupment from the allocated level in
the 2009 Final Rule (or a lesser amount)
in one year is not possible because there
are too few allowances to provide
recoupment and regular allowances for
HCFC–142b. Additionally, the memo
explains that if the Agency provides
recoupment for HCFC–142b production
allowances, the Agency will have no
choice but to increase the aggregate
number of production allowances.
The primary benefit of option 3 is that
it keeps the overall consumption
allocation at the same level (or less) as
that in the 2009 Final Rule, and should
therefore not negatively affect the
transition to the 2015 stepdown or
recovery and reclamation. However, for
the years during which recoupment
occurred, companies not receiving
recoupment under this option would
receive fewer allowances, and a smaller
share of overall allowances, than under
the other recoupment scenarios. The
amount of allowances received by these
companies also would be smaller than
the amount they would have received
under the 2008 Proposed Rule, and
would decrease further if EPA decides
to allocate less than the amounts in the
2009 Final Rule.
EPA is also considering option 4,
under which the Agency would not
provide recoupment allowances. As part
of the evaluation of this option, EPA is
considering the effect of the Court’s
partial vacatur and remand on the 2010
allocation. The Court issued its decision
on August 27, 2010, but stayed the
mandate pending resolution of any
petition for rehearing. The 2009 Final
Rule remained in effect during 2010.
EPA’s petition for rehearing was denied
on January 21, 2011, and the mandate
issued on February 4, 2011. While EPA
has not interpreted the vacatur as
nullifying 2010 allowances, EPA is
considering whether to address the 2010
allocation on remand even if the partial
vacatur does not apply to 2010.
EPA notes that all 2010 allowances
expired on December 31, 2010 and
therefore have no value in later years.
See 74 FR 66415 (‘‘EPA allocates
allowances for specific years; they are
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249
valid between January 1 and December
31 of a given control period (i.e.,
calendar year)’’). 40 CFR Part 82 also
makes it clear that allowances are tied
to a specified control period. Section
82.16(a) states that ‘‘In each control
period * * * each person is granted the
specified percentage of baseline
production allowances and baseline
consumption allowances for the
specified class II controlled substances
apportioned under §§ 82.17 and 82.19.’’
Furthermore, the definitions of
unexpended allowances in section 82.3
specify that allowances are valid for
specific control periods. The protection
of stratospheric ozone allowance system
at 40 CFR part 82 does not allow
banking or borrowing of allowances.
Since the Court’s mandate issued on
February 4, 2011, no company could
have possessed 2010 allowances on the
date the mandate issued, because all
unexpended 2010 allowances had
already expired.
EPA seeks comment on whether it is
possible to put the petitioners in
Arkema v. EPA in the position they
would have been in had they received
the full amount of 2010 allowances to
which they believed they were entitled.
If EPA were to grant the petitioners
additional 2010 allowances now, those
allowances would have no value, as
2010 allowances can be expended only
in 2010. The three recoupment options
discussed above assume that by
providing recoupment allowances in
2013, or 2013–2014, EPA can make up
for the lost opportunity to provide or
consume a specific amount of HCFC,
which might either have been sold
during 2010 or placed in inventory for
sale during a subsequent year.
Advantages of not providing
recoupment allowances include (1) not
increasing the amount of HCFC–22 on
the market, which has advantages for
the environment, public health, and for
fostering a viable reclamation industry
in advance of the 2015 stepdown, and
(2) not decreasing the actual number or
share of allowances for other allowance
holders. Given the considerations above,
including the structure of the program
and the policy advantages noted, EPA’s
preference is not to provide recoupment
allowances.
If EPA decides to provide
recoupment, the Agency prefers option
1 because it has a minimal impact on
the 2015 stepdown to 10 percent of
baseline, addresses the Court’s decision
in the simplest manner, and does not
further decrease the number of
allowances companies would have
received had EPA taken the 2008 interpollutant transfers into account in its
2009 Final Rule. EPA welcomes
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comment on the matter. A memo in the
docket for this rulemaking shows how
EPA would effectuate each of the
options in the regulatory text at 40 CFR
part 82 (see ‘‘Memo: Recoupment
Options’’). To effectuate this option, the
regulatory text at 40 CFR 82.16(a) would
be amended to add paragraph (a)(2) as
set forth in the regulatory text of this
proposed rule.
Any recoupment allowances allocated
for 2013 or 2014 would function in the
same way as other calendar-year
allowances: For example, they could be
used only in the calendar year for which
they were issued and would expire at
the end of that calendar year.
wreier-aviles on DSK3TPTVN1PROD with PROPOSALS
C. How much HCFC–22 and HCFC–142b
would be allocated in 2012–2014?
As discussed previously, EPA is
proposing to revise the tables in 40 CFR
82 that together specify the production
and consumption allowances available
during specified control periods. The
tables at sections 82.17 and 82.19
apportion baseline production
allowances and baseline consumption
allowances, respectively, to individual
companies for specific HCFCs during a
particular regulatory period.
Complementing these tables, the table at
section 82.16 lists the percentage of
baseline allocated to allowance holders
for specific control periods. EPA is
proposing to (1) retain this framework of
complementary tables, (2) respond to
the Court’s remand by establishing
baselines for 2012–2014 identical to
those established in the 2011 Interim
Final Rule (76 FR 47451), and (3) grant
allowances based on percentages of
baselines in a manner that achieves the
2010 phaseout step and lays the
groundwork for the next phaseout step
in 2015 (which could mean fewer 2012–
2014 consumption allowances with or
without fewer 2012–2014 production
allowances as compared to the 2009
Final Rule). EPA has published an
Overview Memo in the docket clarifying
how the various options presented in
this proposed rule might work
separately or in combination.
In the 2009 Final Rule, 34.1 percent,
30.1 percent, and 26.1 percent of each
company’s HCFC–22 baselines were
allocated for 2012, 2013, and 2014,
respectively. As discussed above, EPA
interprets the Court’s vacatur as
applying to the HCFC–22 and HCFC–
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142b allocations for each of these years.
EPA intends to put in place new
allocations through this rulemaking.
EPA is proposing, at maximum, to
allocate 28.7 percent, 25.3 percent and
21.9 percent of the HCFC–22 baseline
for 2012, 2013 and 2014 consumption,
respectively. EPA is also proposing an
11 to 47 percent reduction to this
maximum amount for each year, which
would correspond to annual
consumption allowances of 17.7 to 25.5
percent of baseline in 2012, 14.7 to 22.1
percent in 2013, and 11.6 to 18.5
percent in 2014. The reduction could
apply to consumption only or to
consumption and production, if EPA
chooses not to decouple consumption
and production allowances.
The percent allocation for HCFC–142b
was 0.47 percent of baseline in the 2009
Final Rule for 2012–2014. EPA is
proposing to allocate 4.9 percent of
HCFC–142b baseline for 2012–2014. As
a reminder, the percentages allocated for
2013 and 2014 could be different if EPA
decides to provide recoupment.
The 2009 Final Rule, which did not
include the 2008 transfers of HCFC–
142b to HCFC–22 baseline allowances
in the baselines for the next regulatory
period, had a total HCFC–22
consumption baseline of 119,384 MT.
EPA is reflecting the baseline transfers
in section 82.17 and 82.19 in
accordance with the Court’s decision.
As a result, the aggregate HCFC–22
consumption baseline has increased to
141,865 MT. Since the aggregate HCFC–
22 baseline is now higher due to the
increase in the number of HCFC–22
baseline allowances for Arkema, Inc.
and Solvay Fluorides, LLC, EPA is
allocating a smaller percentage of the
company-specific baselines (even
without the proposed decrease in
allocation) than in the 2009 Final Rule
to achieve the same total number of
HCFC–22 allowances. Thus, 40,700 MT
of HCFC–22 consumption (the aggregate
allocation amount for 2012 in the 2009
Final Rule) is equal to 34.1 percent of
119,384 MT (baseline) of HCFC–22 in
the 2009 Final Rule, and 28.7 percent of
141,865 MT (baseline) for 2012 in this
proposed rule. An 11 to 47 percent
reduction in consumption allowances
would change the percentage of baseline
allocated to between 17.7 and 25.5
percent for 2012. The aggregate HCFC–
22 production baseline is also
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Sfmt 4702
increasing, from 110,619 MT in the 2009
Final Rule to 129,093 MT, to reflect
Arkema, Inc.’s transfer of HCFC–142b
baseline production allowances to
HCFC–22 baseline production
allowances.
The opposite is true for HCFC–142b,
which had a larger aggregate
consumption baseline in the proposed
rule (21,089 MT), but now has a smaller
consumption baseline (2,047 MT) since
EPA is accounting for inter-pollutant
transfers from HCFC–142b to HCFC–22.
Thus, 100 MT of HCFC–142b
consumption allowances (the aggregate
allocation amount in each year between
2012 and 2014) is equal to 0.47 percent
of 21,089 MT of HCFC–142b in the 2009
Final Rule, and 4.9 percent of 2,047 MT
in this proposed rule. Aggregate HCFC–
142b baseline production allowances
are decreasing from 25,090 MT in the
2009 Final Rule to 9,444 MT in this
proposed rule to reflect Arkema, Inc.’s
transfer of HCFC–142b baseline
production allowances.
In summary, EPA is proposing (1) to
establish production and consumption
baselines for 2012–2014 identical to
those established in the 2011 Interim
Final Rule (76 FR 47451) for HCFC–22
and HCFC–142b in the tables at sections
82.17 and 82.19. EPA is also proposing
(2) to add new specified percentages of
baseline for those substances to the table
in section 82.16 for the 2012–2014
control periods. Without recoupment,
the maximum proposed allocation
amounts for consumption are specified
in Table 1. Relative to the 2009 Final
Rule, EPA is proposing to (3) allocate
fewer HCFC–22 consumption
allowances, the same amount or more
HCFC–22 production allowances, and
the same amount of HCFC–142b
production and consumption
allowances. If EPA chooses to provide
recoupment allowances, the percentage
of HCFC–22 baseline allocated to
consumption could be 3.3 percent lower
if EPA decides to provide recoupment
from the total allocation in 2013 and
2014—regardless of the total allocation.
The percentage of HCFC–22 baseline
allocated to production could be 2.8
percent lower. The percentage of HCFC–
142b baseline allocated to production
and consumption could be 4.5 percent
lower. Table 3 reflects the range of
allocation percentages, including
recoupment.
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TABLE 3—PROPOSED PHASEOUT SCHEDULE FOR HCFC–22 AND HCFC–142B BETWEEN 2012 AND 2014 6
HCFC–22 Consumption
Control period
High
%
2012 .................................
2013 .................................
2014 .................................
Low
%
28.7
25.3
21.9
Consistent with the 2009 Final Rule,
EPA is allocating different baseline
percentages for HCFC–22 and HCFC–
142b because EPA projects that the
needs will differ for servicing airconditioning and refrigeration
appliances during the 2012–2014
control periods.
wreier-aviles on DSK3TPTVN1PROD with PROPOSALS
1. How does EPA propose to allocate
HCFC–22 consumption allowances for
2012–2014?
For 2012, the 2009 Final Rule
allocated HCFC–22 consumption
allowances to meet about 76.5 percent
of the servicing need, which translated
into approximately 40,700 MT, or 59
percent of the total HCFC consumption
cap for the 2012 control period. In this
rulemaking, EPA is proposing to
allocate 11 to 47 percent less for 2012
relative to the 2009 Final Rule; see the
Adjustment Memo in the docket for a
discussion of recent updates to
estimated servicing demand and how
much of that demand could reasonably
be met by recovered or reclaimed
refrigerant. In the 2009 Final Rule, 2013
and 2014 consumption allocations were
35,900 MT and 31,100 MT, respectively.
The Agency is proposing to allocate 11
to 47 percent less for those years as
well. Along with any reduction in
consumption allowances, the final
allocations in 2013 and 2014 will
depend on which recoupment option
the Agency chooses (including no
recoupment). If the Agency issues
recoupment, its preferred option is to
allocate all recoupment (5,907 MT) in
6 Table 3 shows the highest and lowest percentage
of baseline allocated being proposed in this rule.
The high HCFC–22 consumption scenario shows
the percentage allocated if EPA provides the same
number of allowances relative to the 2009 Final
Rule. The high HCFC–22 production scenario
shows an increase in overall production allowances
if EPA allocates the same percentage of baseline as
in the 2009 Final Rule. The low HCFC–22
production and consumption scenarios take into
consideration a reduction in allowances relative to
the 2009 Final Rule and recoupment from the
aggregate allocation in 2013 and 2014. Additionally,
the low scenario for HCFC–22 production shows
the percentage allocated if EPA does not decouple
production and consumption. For HCFC–142b, the
high percentage reflects the same thinking used in
the 2011 Interim Final Rule. The low scenario
incorporates consumption recoupment from the
aggregate amount for 2013 and 2014.
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HCFC–22 Production
High
%
17.7
11.4
8.3
Low
%
34.1
30.1
26.1
2013 and do so in addition to the overall
consumption allocation—regardless of
whether the annual allocations are
decreased relative to the 2009 Final
Rule or not. In each year between 2012
and 2014, EPA’s total HCFC
consumption allocation including
recoupment would be at least 36 percent
below the Montreal Protocol cap, and
would be below servicing demand as
estimated in the Servicing Tail Report.
Section III.B.4. of this preamble also
discusses other recoupment options.
2. How does EPA propose to allocate
HCFC–22 production allowances for
2012–2014?
In the 2009 Final Rule, EPA decided
to use the same percentages for
production and consumption
allocations—deriving the percentages
based on estimated need for each
individual HCFC. In this rulemaking,
EPA is proposing to decouple the
percentage of baseline allocated for
production and consumption
allowances. The Agency is taking
comment on two options with regard to
decoupling production allowances: (1)
Allocating the same aggregate number of
HCFC–22 production allowances as in
the 2009 Final Rule for 2012–2014, and
(2) using the same baseline percentages
as in the 2009 Final Rule to allocate
HCFC–22 production allowances in
2012–2014. The proposal to decrease
consumption allowances by 11 to 47
percent relative to the 2009 Final Rule
would also apply to production
allowances should the Agency decide
not to decouple production allowances
from consumption allowances.
Under option 1, EPA would decouple
the percentage of baseline allocated for
production from the percentage of
baseline allocated for consumption. A
range of percentages is provided in
Table 3. EPA would effectuate this
change in its regulations by replacing
the table at 40 CFR 82.16 with two
tables. One would allocate a percent of
baseline for consumption allowances. In
the other, EPA would allocate 28.7
percent of production baseline in 2012,
25.3 percent in 2013, and 21.9 percent
in 2014. The resulting allocation would
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HCFC–142b Consumption and
production
Sfmt 4702
High
%
17.7
11.4
8.3
Low
%
4.9
4.9
4.9
4.9
0.4
0.4
provide 37,050 MT of HCFC–22
production allowances in 2012. This
aggregate allocation in 2012 is
approximately two percent lower than
the amount allocated in the 2009 Final
Rule (37,050 MT in this proposed rule
vs. 37,721 MT in the 2009 Final Rule)
because the aggregate amount of
baseline production allowances in this
rulemaking did not increase by the same
relative amount as aggregate baseline
consumption allowances. Because
Solvay did not transfer its HCFC–142b
production allowances to HCFC–22
production allowances, HCFC–22
baseline consumption allowances are
18.8 percent higher in this rule, while
baseline production allowances are only
16.7 percent higher. The memo to the
docket for this rulemaking titled
‘‘Effects of HCFC–22 and HCFC–142b
Baseline Changes: 2009 Final Rule vs.
2011 Proposed Rule,’’ (Baseline Memo)
discusses the slight differences in
allocation amounts in more detail.
Absent recoupment, EPA would allocate
32,660 MT of HCFC–22 production
allowances in 2013, and 28,271 MT of
HCFC–22 production allowances in
2014 under option 1.
Under option 2, EPA would also
decouple the percentage of baseline
allocated for production from the
percentage of baseline allocated for
consumption. EPA would effectuate this
change in its regulations by replacing
the table at 40 CFR 82.16 with two
tables. One would allocate a percentage
of baseline for consumption allowances.
The other would allocate 34.1 percent,
30.1 percent and 26.1 percent of
baseline for production allowances in
2012, 2013, and 2014, respectively,
consistent with the 2009 Final Rule.
This approach would still provide the
petitioners in Arkema v. EPA the benefit
of their 2008 baseline transfers while
giving other companies with production
baselines approximately the same
number of production allowances as
they received in the 2009 Final Rule.
Compared to the 2009 Final Rule, the
net result of this option would increase
allowed production by 6,299 MT in
2012, 5,560 MT in 2013, and 4,821 MT
in 2014.
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EPA is interested in comments on a
number of issues with regard to these
two options. From a policy perspective,
EPA is interested in comments on
whether an increase in the total number
of HCFC–22 production allowances
would result in greater total HCFC
production, either in the U.S. or
globally. EPA notes that production of
1 kilogram of an HCFC requires both a
production allowance and a
consumption allowance (82.15(a)(1),
(2)). Thus, an increase in production
allowances without a corresponding
increase in consumption allowances
does not automatically result in greater
production. The most likely scenario is
that an increase in production
allowances would result in greater U.S.
production for export. This is because as
stated in 82.20(a), ‘‘A person may obtain
at any time during the control period
* * * consumption allowances
equivalent to the quantity of class II
controlled substances that the person
exported from the U.S. and its territories
to a foreign state * * * when that
quantity of class II controlled substance
was produced in the U.S. * * * with
expended consumption allowances.’’ In
effect, current EPA regulations allow
exporters to receive a refund of one
consumption allowance for each
kilogram they export if they show one
consumption and one production
allowance were expended for the
material exported. Therefore, an
increase in production allowances
would not be expected to result in
greater HCFC consumption in the U.S.
As an aside, the Agency also allows for
additional production for export to
Article 5 countries under the Montreal
Protocol through its allotment of Article
5 allowances. Until December 31, 2019,
companies are allowed to produce up to
10 percent of their HCFC–22, HCFC–
141b and HCFC–142b production
baselines annually so long as the
produced material is exported to an
Article 5 country. Article 5 allowances
and their proper use are described in
more detail at 82.18(a)(2).
EPA welcomes comment on whether,
relative to the 2009 Final Rule, an
increase in the total number of
production allowances, as proposed
under option 2, would result in (1) an
increase in U.S. consumption, (2) an
increase in U.S. production, either for
domestic use or for export, and/or (3) an
increase in worldwide production and/
or consumption of HCFCs. Moreover,
given that one potential outcome might
be an increase in U.S. exports of HCFC–
22, EPA invites comment on the
implications of such an increase for the
U.S. economy and the global
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environment, particularly as it relates to
the smooth U.S. phaseout of HCFC–22.
EPA also requests comments on
whether section 605(c) would preclude
allocating a different percentage of
baseline for production than for
consumption. Section 605(c) states that
EPA must ‘‘promulgate regulations
phasing out the production * * * of
class II substances in accordance with
[section 605],’’ subject to any
acceleration under section 606. It
further states that EPA must
‘‘promulgate regulations to insure that
the consumption of class II substances
in the United States is phased out and
terminated in accordance with the same
schedule * * * as is applicable to the
phase-out and termination of
production of class II substances under
[Title VI].’’ EPA is considering three
possible interpretations of the term
‘‘schedule’’ as referenced in section
605(c): (1) The schedule that appears on
the face of section 605, which contains
no deadlines until 2015; (2) the
schedule that appears on the face of
section 605, as accelerated under
section 606; and (3) the specific
allocation percentages or amounts
established by EPA through rulemaking
for each control period. EPA believes
that the second interpretation is the
most consistent with the statutory
language and purpose. The Agency
requested comment on this issue in the
2011 Interim Final Rule (76 FR 47451)
and received four comments in favor of
increasing production allowances, and
two comments in opposition. Only one
commenter responded specifically to
EPA’s interpretation of section 605, and
the commenter agreed with the second
interpretation presented.
In past actions, the Agency has made
the initial schedule in section 605 more
stringent to reflect modifications to the
Montreal Protocol phaseout schedule for
HCFCs. Under the 2007 Montreal
Adjustment (reflected in Decision XIX/
6), the U.S. is obligated to reduce HCFC
production and consumption 75 percent
below its aggregate baseline by 2010.
EPA is not proposing to increase
production to an amount that would be
inconsistent with that obligation.
Instead, EPA is taking comment on
whether to allow production to increase
relative to consumption, without
encroaching on the cap.
Under option 2, the U.S. would still
be below the Montreal Protocol’s
production cap (when all HCFCs are
included) by at least 33 percent in each
year, even when including recoupment
(the memo to the docket entitled,
‘‘Montreal Protocol Compliance,’’
contains more detailed information on
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the implications of each option relative
to the Montreal Protocol cap).
In summary, EPA seeks comment on
whether to decouple production from
consumption, and if so, which
decoupling option to choose. EPA is
also seeking comment on whether
increasing production allowances above
the 2009 Final Rule level, as in option
2, would negatively affect the transition
to the 2015 phaseout step, under which
the U.S. is obligated to reduce HCFC
production and consumption 90 percent
below its aggregate baseline.
3. How does EPA propose to allocate
HCFC–142b allowances for 2012–2014?
Establishing HCFC–142b baseline
allowances that take into account the
2008 inter-pollutant transfers discussed
in section II.D. results in 2,047 MT of
aggregate baseline consumption
allowances and 9,444 MT of aggregate
baseline production allowances.
Consistent with the 2009 Final Rule,
EPA is proposing to allocate 100 percent
of the projected servicing need for
HCFC–142b identified in that rule: 100
MT of consumption. To get to that level
of consumption, EPA is proposing to
allocate 4.9 percent of the aggregate
consumption baseline, as reflected in
the table at section 82.16. The aggregate
allocation number for consumption is
the same as in the 2009 Final Rule.
Using the same percentage (4.9
percent), EPA is proposing to allocate
463 MT of HCFC–142b production
allowances for each control period
between 2012 and 2014. The aggregate
allocation for production is higher than
the amount allocated in the 2009 Final
Rule (463 MT in this proposed rule vs.
118 MT in the 2009 Final Rule). The
proposed allocation is 292 percent
higher than in the 2009 Final Rule
because the aggregate amount of
baseline HCFC–142b consumption
allowances in this rulemaking decreased
by a significantly larger amount than
aggregate baseline HCFC–142b
production allowances. HCFC–142b
baseline consumption allowances are
90.3 percent lower in this rule, while
baseline production allowances are only
62.4 percent lower. The difference
between the change in production and
consumption baselines is a result of
Arkema trading most of its HCFC–142b
production allowances, while Solvay
did not. This higher amount of calendaryear production does not affect the
U.S.’s ability to meet its obligations
under the Montreal Protocol. The
Baseline Memo in the docket for this
rulemaking discusses the differences in
more detail.
As discussed in section III.B.4. of this
preamble, EPA is considering options to
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allocate recoupment allowances in 2013
or 2013–2014 in addition to the 4.9
percent of baseline described above. If
finalized, the 2013 option would result
in an additional 61 MT of HCFC–142b
consumption allowances and 397 MT of
HCFC–142b production allowances. The
2013–2014 option would result in 30
MT of additional HCFC–142b
consumption allowances and 198 MT of
HCFC–142b production allowances each
year.
4. How would the aggregate for HCFC–
22 and HCFC–142b translate entity-byentity?
For 2012, EPA is proposing to allocate
(1) at maximum, approximately 40,700
MT of HCFC–22 consumption
allowances, (2) 37,050 MT of HCFC–22
production allowances (with possible
adjustments), (3) approximately 100 MT
of HCFC–142b consumption allowances
and (4) 463 MT of HCFC–142b
production allowances. However, EPA
actually allocates allowances to
individual companies (i.e., legal
entities). Company-specific production
and consumption baselines (also
referred to as ‘‘baseline allowances’’) for
HCFC–142b and HCFC–22 are listed at
sections 82.17 and 82.19, respectively.
The range of percentages of baseline
each entity would receive for HCFC–22
and HCFC–142b in 2012 through 2014
is shown in Table 3 above. For the low
percentage of baseline allocated, Table 3
shows how the proposed allocation
combined with recoupment option 3
(recoupment provided from the total
allocation, not in addition to the
allocation) would affect allowances. For
the high percentage of baseline
allocated, Table 3 shows no change
relative to the 2009 Final Rule on the
consumption side and an increase in
allowances on the production side. The
percentages included in the proposed
regulatory text at the end of this
preamble are at the lower end of the
range EPA is proposing to allocate.
Allowances allocated for individual
control periods are called ‘‘calendaryear allowances’’ to distinguish them
from the baseline production or
consumption allowances. For 2012–
2014, EPA is proposing to apportion
production and consumption baselines
for HCFC–22 and HCFC–142b on the
same basis as in the 2009 Final Rule,
except that EPA is making adjustments
to reflect (1) the 2008 inter-pollutant
transfers of baseline allowances deemed
permanent by the Court, (2) intercompany, single-pollutant transfers of
baseline allowances that occurred in
2010, and (3) changes in company
names that occurred after the 2009 Final
Rule was signed. All of these changes
were made in the 2011 Interim Final
Rule (76 FR 47451), and EPA is
proposing to do the same for 2012–2014.
Applying the approach described above,
EPA would apportion production and
consumption baselines for HCFC–22
and HCFC–142b to the following
entities in the following amounts:
TABLE 4—BASELINE PRODUCTION ALLOWANCES OF HCFC–22 AND HCFC–142B IN 40 CFR 82.17
Person
Controlled substance
Arkema .................................................................................................................................................
HCFC–22 ..................
HCFC–142b ...............
HCFC–22 ..................
HCFC–22 ..................
HCFC–142b ...............
HCFC–22 ..................
HCFC–142b ..............
DuPont .................................................................................................................................................
Honeywell ............................................................................................................................................
MDA Manufacturing .............................................................................................................................
Solvay Solexis .....................................................................................................................................
Allowances (kg)
46,692,336
484,369
42,638,049
37,378,252
2,417,534
2,383,835
6,541,764
TABLE 5—BASELINE CONSUMPTION ALLOWANCES OF HCFC–22 AND HCFC–142B IN 40 CFR 82.19
Person
Controlled substance
ABCO Refrigeration Supply .................................................................................................................
Altair Partners ......................................................................................................................................
Arkema .................................................................................................................................................
HCFC–22 ..................
HCFC–22 ..................
HCFC–22 ..................
HCFC–142b ...............
HCFC–22 ..................
HCFC–22 ..................
HCFC–22 ..................
HCFC–142b ...............
HCFC–22 ..................
HCFC–22 ..................
HCFC–142b ...............
HCFC–22 ..................
HCFC–22 ..................
HCFC–22 ..................
HCFC–22 ..................
HCFC–22 ..................
HCFC–22 ..................
HCFC–22 ..................
HCFC–22 ..................
HCFC–22 ..................
HCFC–22 ..................
HCFC–142b ..............
HCFC–22 ..................
Carrier Corporation ..............................................................................................................................
Coolgas Investment Property ..............................................................................................................
DuPont .................................................................................................................................................
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H.G. Refrigeration Supply ....................................................................................................................
Honeywell ............................................................................................................................................
Mexichem Fluor Inc .............................................................................................................................
Kivlan & Company ...............................................................................................................................
MDA Manufacturing .............................................................................................................................
Mondy Global .......................................................................................................................................
National Refrigerants ...........................................................................................................................
Refricenter of Miami ............................................................................................................................
Refricentro ...........................................................................................................................................
R-Lines .................................................................................................................................................
Saez Distributors .................................................................................................................................
Solvay Fluorides ..................................................................................................................................
Solvay Solexis .....................................................................................................................................
USA Refrigerants .................................................................................................................................
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04JAP1
Allowances (kg)
279,366
302,011
48,637,642
483,827
54,088
1,040,458
38,814,862
52,797
40,068
35,392,492
1,315,819
2,546,305
2,081,018
2,541,545
281,824
5,528,316
381,293
45,979
63,172
37,936
3,781,691
194,536
14,865
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The proposed baselines listed above
are identical to the tables presented in
the 2011 Interim Final Rule (76 FR
47451).
wreier-aviles on DSK3TPTVN1PROD with PROPOSALS
D. Are HCFC–141b, HCFC–123, HCFC–
124, HCFC–225ca, and HCFC–225cb
allowances affected by this rulemaking?
Since the Court’s decision did not
vacate this portion of the 2009 Final
Rule, EPA is not proposing to change
baselines and percentages of baseline
allocated as calendar-year allowances
for HCFC–141b, HCFC–123, HCFC–124,
HCFC–225ca, and HCFC–225cb, except
to make adjustments for inter-company,
single-pollutant transfers of baseline
allowances, as reflected in the 2011
Interim Final Rule (76 FR 47451). In the
case of HCFC–141b, EPA is continuing
to allocate 0 percent of baseline for U.S.
consumption and production, consistent
with 40 CFR 82.16(b).
E. How will EPA allocate other HCFCs?
As a result of EPA’s allocation
process, which is largely based on
projected demand for HCFC–22 and
HCFC–142b, minus an amount of
HCFC–22 that is assumed to be reused,
recycled, or reclaimed, the total
allocation is lower than the aggregate
HCFC cap under the Montreal Protocol.
EPA recognizes that there could be some
additional need for HCFCs not
specifically included in this rule. While
some niche applications in the U.S. use
other HCFCs, such as HCFC–21, EPA is
not aware of additional need for
production or import of these
substances at this time, as adequate
amounts appear to be in inventory.
However, EPA is not foreclosing the
possibility of additional production or
import for these niche uses. Also, some
amount of HCFC–141b will likely
continue to be produced or imported via
the petition process during 2012–2014.
EPA believes there is sufficient room
under the cap for such continued
production and import. The current
regulations at 40 CFR 82.15 ban the
production and import of class II
substances for which EPA has
apportioned baseline production and
consumption allowances in excess of
allowances held by the producer or
importer, but do not ban the production
and import of class II substances for
which EPA has not apportioned
baseline production and consumption
allowances. This rule does not alter the
current regulations in that respect. The
producer or importer of an HCFC that is
not subject to the allowance system
would be required to report to EPA
consistent with the existing
recordkeeping and reporting
requirements. If necessary, EPA could
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amend the regulations to set and
apportion baselines and issue
allowances for these HCFCs. Therefore,
retaining room under the cap could
provide the benefit of accounting for
unanticipated growth in HCFCs that do
not have allocations or other unforeseen
events. However, EPA is not reserving
room under the cap for the abovedescribed reasons. EPA is allocating
allowances based on modeled demand
for virgin and recovered material in
preparation for the next major stepdown
period under the Montreal Protocol in
2015.
IV. How does EPA propose to change
the regulations governing allowance
transfers of Class II Controlled
Substances?
The Agency is concerned about the
possibility of companies undermining
the HCFC chemical-by-chemical
phaseout by performing inter-pollutant
transfers in advance of future phaseout
steps. EPA interprets the 2003 Final
Rule, which established the transfer
provisions at 40 CFR 82.23, as allowing
only single-pollutant, inter-company
transfers to be made on a permanent
basis. Nevertheless, EPA recognizes that
in Arkema v. EPA, the Court found that
‘‘EPA’s practice under the 2003 Rule
was to allow petitioners’ baseline
transfers of inter-pollutant allowances’’
(618 F.3d at 8). Therefore, EPA clarified
its current policy on inter-pollutant
transfers in the 2011 Interim Final Rule
(76 FR 47459) and is repeating that
clarification in this action. EPA is also
proposing to modify the regulatory text
in order to dispel any possibility of
confusion in the future. In addition to
modifying the regulatory text to address
the duration of inter-pollutant transfers,
EPA is also proposing to revise the
regulatory text to reflect prior Agency
statements pertaining to inter-pollutant
transfers of Article 5 allowances.
A. How does EPA propose to change the
regulations governing permanent
transfers of Class II Allowances?
Sections 607(b) and (c) of the CAA
address inter-pollutant and intercompany transfers of allowances,
respectively. Inter-pollutant transfers
are the transfer of an allowance of one
substance to an allowance of another
substance on an ODP-weighted basis.
Inter-company transfers are transfers of
allowances for the same ODS from one
company to another company. Section
607(c) also authorizes inter-company
transfers combined with inter-pollutant
transfers, so long as the requirements of
both are met. The corresponding
regulatory provisions for HCFCs appear
at 40 CFR 82.23.
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The 2009 Final Rule updated the
baselines for HCFC–22 and HCFC–142b
to reflect name changes and intercompany baseline transfers, i.e.,
transfers of baseline for a specific type
of HCFC from one company to another.
Doing so reflected the changes in the
marketplace that had occurred since
EPA promulgated the 2003 Final Rule.
Inter-company baseline transfers
provide a mechanism for new entrants
to join the HCFC market and for other
companies to expand their business.
EPA recognizes that in some cases,
entities are no longer actively involved
in HCFC production, import, and/or
export activities. EPA retained the
baseline for such entities, noting that
this had been a mechanism by which
new entrants had entered the HCFC
allowance system in the past.
The 2009 Final Rule also addressed
four inter-pollutant baseline transfers
made during the prior regulatory period
(see section II.D. and the transfer forms
in the docket for this action for more
detail). EPA had proposed to adjust the
company baselines to reflect these four
inter-pollutant baseline transfers in the
2008 Proposed Rule. Eight commenters
opposed, and two commenters
supported, these proposed adjustments.
At issue was whether the inter-pollutant
baseline transfers should be part of the
companies’ baseline allowances in the
next regulatory period.
After reviewing the comments, EPA
concluded that adjusting the baselines
to reflect inter-pollutant baseline
transfers could create incentives for
future manipulation of the allocation
system in anticipation of future control
periods. EPA remains concerned about
the potential for such future
manipulation if inter-pollutant baseline
transfers during the current regulatory
period change a company’s baseline for
future regulatory periods. For example,
in 2020 EPA will no longer be issuing
HCFC–22 production or consumption
allowances (see section 82.16(e)). EPA
expects that companies with HCFC–22
allowances would no longer be in the
HCFC market at that date if they did not
hold allowances for other HCFCs that
may still be produced after 2020. If EPA
were to allow inter-pollutant baseline
transfers that carried forward into the
new regulatory period, companies with
HCFC–22 baselines in 2019 could
convert them all to baselines for HCFC–
123. Perpetuating the HCFC–22
baselines in a new form would be
counter to the design of the chemicalby-chemical phaseout, under which the
baseline allowances for a particular
chemical are intended to drop out of the
system upon the phase-out of that
chemical.
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As another example, in 2015, a
producer or importer that previously
had not participated in the HCFC–123
market could dominate that market by
converting its HCFC–22 baseline in
2014 to HCFC–123 baseline. Given the
different ODPs of HCFC–22 and HCFC–
123 (0.055 and 0.02, respectively),
converting one baseline allowance of
HCFC–22 would result in 2.75 baseline
allowances of HCFC–123. Also, since
companies hold many more HCFC–22
baseline allowances than HCFC–123
baseline allowances, converting those
HCFC–22 baseline allowances would
have an overwhelming effect on the
current HCFC–123 baseline allowance
holders and the overall market. EPA
agrees with commenters on the 2008
Proposed Rule that taking interpollutant baseline transfers into account
in setting baselines could have the effect
of moving the U.S. HCFC phasedown
from a chemical-by-chemical phaseout,
as established under the ‘‘worst-first’’
approach in the 1993 Final Rule,
towards an ODP-weighted phasedown.
Thus, there are important policy reasons
going forward for not taking interpollutant transfers into account in
establishing baselines for new
regulatory periods.
Some commenters on the 2008
Proposed Rule stated that modifying the
baselines by taking into account interpollutant transfers would be contrary to
the CAA. One commenter argued that
section 607 of the CAA allows EPA to
approve inter-pollutant transfers of
allowances only on a year-to-year basis.
That commenter pointed to language in
section 607(b) stating that EPA
regulations are to permit ‘‘a production
allowance for a substance for any year
to be transferred for a production
allowance for another substance for the
same year on an ozone depletion
weighted basis.’’ The commenter also
discussed the legislative history of the
1990 CAA Amendments.
EPA does not agree with the
commenter that the language of section
607(b) is clear on its face. However,
where the statutory language is
ambiguous, EPA has discretion to
choose a reasonable interpretation of
that language. EPA determined in the
2009 Final Rule that section 607(b) is
best read as permitting only year-byyear inter-pollutant transfers. EPA
continues to believe that this is the best
interpretation of the statutory language.
Section 607(b) states that EPA’s rules
are to permit ‘‘a production allowance
for a substance for any year to be
transferred for a production allowance
for another substance for the same
year.’’ This language emphasizes the
year-by-year nature of such transactions.
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No parallel language appears in section
607(c). That section does, however,
provide that any inter-pollutant
transfers between two or more persons
must meet the requirements of section
607(b).
As the Court noted, ‘‘the Agency is
certainly entitled to * * * institute a
program that forbids baseline interpollutant transfers in the future,’’
(Arkema v. EPA, 618 F.3d at 9). Hence,
EPA concludes that requiring all interpollutant transfers to be conducted on a
yearly—and thus temporary—basis
going forward is the approach most
consistent with the wording of section
607(b). Further discussion of the reasons
for limiting inter-pollutant transfers to
those conducted on a calendar-year
basis is available in the Response to
Comments on the 2008 Proposed Rule
(included in the docket for this
rulemaking).
Consistent with the Court’s decision
regarding past inter-pollutant transfers
(those conducted during the prior
regulatory period), the baselines
established in this action for 2012–2014
take into account the 2008 interpollutant baseline transfers. EPA is
clarifying, however, that it has not
approved any inter-pollutant transfers of
baseline allowances in the current
regulatory period, and for the reasons
given in the 2009 Final Rule and in this
action, in the future, EPA intends to
approve inter-pollutant transfers only
on a year-by-year basis. Thus, in the
context of the allowance system for
protection of stratospheric ozone,
companies should not expect that any
inter-pollutant transfers they conduct
will affect their baselines either in the
current regulatory period or any future
regulatory period.
EPA proposes to revise the regulations
to avoid any further dispute about the
Agency’s position on this issue. In
addition, EPA is proposing to clarify the
procedures that apply to permanent,
single-pollutant transfers. Specifically,
EPA proposes to add a sentence at the
beginning and end of section 82.23(d) of
40 CFR Part 82, so the text reads: ‘‘(d)
Permanent transfers. The procedures in
paragraph (a) of this section apply to
permanent inter-company transfers of
baseline production allowances or
baseline consumption allowances. A
person receiving a permanent transfer of
baseline production allowances or
baseline consumption allowances (the
transferee) for a specific class II
controlled substance will be the person
who has their baseline allowances
adjusted in accordance with phaseout
schedules in this subpart. No person
may conduct permanent inter-pollutant
transfers of baseline production
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255
allowances or baseline consumption
allowances.’’
B. How does EPA propose to change the
regulations governing transfers of
Article 5 HCFC allowances?
Article 5 allowances for Class II
substances are the privileges granted
under 40 CFR 82.18(a) to produce the
specified HCFC for export only to
countries listed in 40 CFR Subpart A,
Appendix C, Annex 4. The countries
listed in that annex are developing
countries whose control obligations
under the Montreal Protocol are
addressed in Article 5 of the treaty and
hence are referred to as ‘‘Article 5
Parties.’’ EPA is proposing to revise the
regulations at 40 CFR 82.23(b) to reflect
its previously stated intent to allow
inter-pollutant transfers of Article 5
allowances. The regulations currently
provide clarity on inter-company
(single-pollutant) transfers of Article 5
allowances in section 82.23(a) by stating
‘‘a person * * * may transfer to any
other person * * * any quantity of the
transferor’s class II * * * Article 5
allowances for the same type of
allowances * * *’’ While 82.23(a)
specifically includes Article 5
allowances in the list of allowances that
may be transferred to another entity,
82.23(b), which governs inter-pollutant
transfers, makes no mention of Article 5
allowances.
Section 82.23 was promulgated as
part of the 2003 Final Rule (68 FR 2820).
EPA specifically discussed the interpollutant transfer of Article 5
allowances at 68 FR 2834 stating, ‘‘For
example, after the 2003 phaseout of
HCFC–141b and before 2010, a company
receiving * * * Article 5 allowances for
HCFC–141b could engage in intercompany transfers of those allowances,
but not in inter-pollutant transfers
[because no other HCFC Article 5
allowances would be available during
that period]. In 2010, when * * *
Article 5 allowances for HCFC–22 and
HCFC–142b become available, these
allowances will be transferable with the
ones for HCFC–141b.’’ These statements
indicate that the Agency intended for
companies to be able to perform interpollutant transfers of Article 5
allowances. The omission of Article 5
allowances from section 82.23(b)
appears to have been an oversight.
Therefore, EPA is proposing to revise
the regulations to specifically provide
for the inter-pollutant transfers of
Article 5 allowances through this
rulemaking. As with other types of
inter-pollutant transfers, these transfers
would be limited in duration to a single
year.
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EPA is also proposing to change the
text at 82.23(a)(ii) for consistency with
its previously stated policy on offsets for
transfers of Article 5 allowances.
Section 607(a) requires that transfers of
production allowances ‘‘will result in
greater total reductions in the
production in each year of * * * class
II substances than would occur in that
year in the absence of such
transactions.’’ In a November 10, 1994,
Federal Register notice, EPA stated its
interpretation that the section 607 offset
requirement applies to Article 5
allowance transfers (59 FR 56287):
‘‘Inter-pollutant transfers of Article 5
allowances will continue to require a
one percent offset, as required by
section 607 of the CAA * * *’’ In the
May 10, 1995 final rule at 60 FR 24980,
EPA stated that ‘‘With today’s action,
EPA permits inter-pollutant and intercompany transfers of Article 5
allowances as proposed * * *’’
meaning EPA intended to require an
offset for transfers of Article 5
allowances in the class I allowance
system.
This intent to require an offset is also
reflected in certain provisions of the
class II allowance system in 40 CFR 82.
Section 82.23(a)(i)(G) specifically
requires an offset for Article 5 allowance
inter-company transfers, stating that the
transfer claim must set forth: ‘‘For trades
of consumption allowances, production
allowances, export production
allowances, or Article 5 allowances, the
quantity of the 0.1 percent offset applied
to the unweighted quantity traded that
will be deducted from the transferor’s
allowance balance.’’ The offset is also
mentioned at section 82.23(a)(iii): ‘‘In
the case of transfers of * * * Article 5
allowances, EPA will reduce the
transferor’s balance of unexpended
allowances by the quantity (in
kilograms) to be converted plus 0.1
percent of that quantity.’’ This contrasts
with section 82.23(a)(ii)(A), which states
that in the case of Article 5 allowances,
‘‘EPA will reduce the transferor’s
balance of unexpended allowances
* * * by the quantity to be transferred,’’
with no mention of an offset. In
addition, in the introductory text for
82.23(a)(ii), Article 5 allowances are not
mentioned: ‘‘The transfer claim is the
quantity (in kilograms) to be transferred
plus, in the case of transfers of
production or consumption allowances,
0.1 percent of that quantity;’’ EPA is
proposing to amend 82.23(a)(ii) and
82.23(a)(ii)(A) to require an offset for
transfers of Article 5 allowances. This
will make section 82.23(a) consistent
throughout. Section 82.23(b) currently
requires an offset of 0.1 percent for all
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inter-pollutant transfers. Thus, if EPA
adds Article 5 allowances to section
82.23(b), an offset will automatically
apply.
To reflect EPA’s intent to allow interpollutant transfers of Article 5
allowances, and the requirement that an
offset be deducted when an entity is
transferring Article 5 allowances, the
Agency is proposing to modify the
regulatory text. EPA is proposing to
modify the text at 40 CFR 82.23(a)(ii) to
read as set forth in the regulatory text of
this proposed rule.
The Agency is also proposing to
modify the text at 40 CFR 82.23(b) by
adding Article 5 allowances to the list
of allowances that can be traded
between pollutants. The text would read
as set forth in the regulatory text of this
proposed rule.
V. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
Under Executive Order (EO) 12866
(58 FR 51735, October 4, 1993), this
action is a ‘‘significant regulatory
action’’ since it raises ‘‘novel legal or
policy issues.’’ Accordingly, EPA
submitted this action to the Office of
Management and Budget (OMB) for
review under Executive Orders 12866
and 13563 (76 FR 3821, January 21,
2011) and any changes made in
response to OMB recommendations
have been documented in the docket for
this action.
EPA did not conduct a specific
analysis of the benefits and costs
associated with this action. Many
previous analyses provide a wealth of
information on the costs and benefits of
the U.S. HCFC phaseout including:
• The 1993 Addendum to the 1992
Phaseout Regulatory Impact Analysis:
Accelerating the Phaseout of CFCs,
Halons, Methyl Chloroform, Carbon
Tetrachloride, and HCFCs.
• The 1999 Report Costs and Benefits
of the HCFC Allowance Allocation
System.
• The 2000 Memorandum Cost/
Benefit Comparison of the HCFC
Allowance Allocation System.
• The 2005 Memorandum
Recommended Scenarios for HCFC
Phaseout Costs Estimation.
• The 2006 ICR Reporting and
Recordkeeping Requirements of the
HCFC Allowance System.
• The 2007 Memorandum
Preliminary Estimates of the
Incremental Cost of the HCFC Phaseout
in Article 5 Countries.
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• The 2007 Memorandum Revised
Ozone and Climate Benefits Associated
with the 2010 HCFC Production and
Consumption Stepwise Reductions and
a Ban on HCFC Pre-charged Imports.
A memorandum summarizing these
analyses is available in the docket.
B. Paperwork Reduction Act
This action does not impose any new
information collection burden. EPA
already requires recordkeeping and
reporting for HCFCs, and this action
does not amend those provisions. The
Office of Management and Budget
(OMB) has previously approved the
information collection requirements
contained in the existing regulations at
40 CFR part 82, subpart A under the
provisions of the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. and has
assigned OMB control number 2060–
0498. The OMB control numbers for
EPA’s regulations in 40 CFR are listed
in 40 CFR part 9.
C. Regulatory Flexibility Act (RFA)
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. We have considered the
economic impacts of this proposed rule
on small entities. For purposes of
assessing the impacts of this rule on
small entities, a small entity is defined
as: (1) A small business as defined by
the Small Business Administration’s
(SBA) 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-forprofit enterprise which is independently
owned and operated and is not
dominant in its field.
This action will affect the following
categories:
—Industrial Gas Manufacturing entities
(NAICS code 325120), including
fluorinated hydrocarbon gases
manufacturers and reclaimers;
—Other Chemical and Allied Products
Merchant Wholesalers (NAICS code
422690), including chemical gases
and compressed gases merchant
wholesalers;
—Air-Conditioning and Warm Air
Heating Equipment and Commercial
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and Industrial Refrigeration
Equipment Manufacturing entities
(NAICS code 333415), including airconditioning equipment and
commercial and industrial
refrigeration equipment
manufacturers;
—Air-Conditioning Equipment and
Supplies Merchant Wholesalers
(NAICS code 423730), including airconditioning (condensing unit,
compressors) merchant wholesalers;
—Electrical and Electronic Appliance,
Television, and Radio Set Merchant
Wholesalers (NAICS code 423620),
including air-conditioning (room
units) merchant wholesalers; and
—Plumbing, Heating, and AirConditioning Contractors (NAICS
code 238220), including Central airconditioning system and commercial
refrigeration installation; HVAC
contractors.
After considering the economic
impacts of this proposed rule on small
entities, I certify this action will not
have a significant economic impact on
a substantial number of small entities as
it relieves a regulatory ban on
production and consumption that
would otherwise apply in the wake of
the Court’s vacatur. EPA is continuing
to allocate production and consumption
allowances using the same approach
described in the 2009 Final Rule with
adjustments to reflect (1) 2008 interpollutant transfers of baseline
allowances deemed permanent by the
Court, (2) inter-company, singlepollutant transfers of baseline
allowances that occurred in 2010,
(3) changes in company names that
occurred after the 2009 Final Rule was
signed and (4) an updated picture on the
demand for HCFC–22. EPA is not
modifying the recordkeeping or
reporting provisions and thus is not
increasing the burden to small
businesses. EPA’s HCFC Phaseout
Benefits and Costs Memo, included in
this docket, provides a summary of
previous small business analyses, as
well as the most recent cost and benefit
data used for the 2009 Final Rule. We
continue to be interested in the
potential impacts of the proposed rule
on small entities and welcome
comments on issues related to such
impacts.
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.
UMRA does not apply to rules that are
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necessary for the national security or the
ratification or implementation of
international treaty obligations. This
rule implements the 2010 milestone for
the phase-out of HCFCs under the
Montreal Protocol. Therefore, this action
is not subject to the requirements of
sections 202 or 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
action apportions production and
consumption allowances and
establishes baselines for private entities,
not small governments.
E. Executive Order 13132: Federalism
Executive Order 13132, titled
‘‘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 action does not have federalism
implications. It does 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 action is
expected to primarily affect producers,
importers, and exporters of HCFCs.
Thus, the requirements of section 6 of
the Executive Order do not apply.
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). This action does not significantly
or uniquely affect the communities of
Indian tribal governments. It does not
impose any enforceable duties on
communities of Indian tribal
governments. Thus, Executive Order
13175 does not apply to this action.
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
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257
defined in EO 12866. The Agency
nonetheless has reason to believe that
the environmental health or safety risk
addressed by this action may have a
disproportionate effect on children.
Depletion of stratospheric ozone results
in greater transmission of the sun’s
ultraviolet (UV) radiation to the earth’s
surface. The following studies describe
the effects of excessive exposure to UV
radiation on children: (1) Westerdahl J,
Olsson H, Ingvar C. ‘‘At what age do
sunburn episodes play a crucial role for
the development of malignant
melanoma,’’ Eur J Cancer 1994: 30A:
1647–54; (2) Elwood JM Japson J.
‘‘Melanoma and sun exposure: an
overview of published studies,’’ Int J
Cancer 1997; 73:198–203; (3) Armstrong
BK, ‘‘Melanoma: childhood or lifelong
sun exposure,’’ In: Grobb JJ, Stern RS
Mackie RM, Weinstock WA, eds.
‘‘Epidemiology, causes and prevention
of skin diseases,’’ 1st ed. London,
England: Blackwell Science, 1997: 63–6;
(4) Whiteman D., Green A. ‘‘Melanoma
and Sunburn,’’ Cancer Causes Control,
1994: 5:564–72; (5) Heenan, PJ. ‘‘Does
intermittent sun exposure cause basal
cell carcinoma? A case control study in
Western Australia,’’ Int J Cancer 1995;
60: 489–94; (6) Gallagher, RP, Hill, GB,
Bajdik, CD, et. al. ‘‘Sunlight exposure,
pigmentary factors, and risk of
nonmelanocytic skin cancer I, Basal cell
carcinoma,’’ Arch Dermatol 1995; 131:
157–63; (7) Armstrong, DK. ‘‘How sun
exposure causes skin cancer: an
epidemiological perspective,’’
Prevention of Skin Cancer. 2004. 89–
116.
This action implements the U.S.
commitment to reduce the total basket
of HCFCs produced and imported to a
level that is 75 percent below the
respective baselines. While on an ODPweighted basis, this is not as large a step
as previous actions, such as the 1996
Class I phaseout, it is one of the most
significant remaining actions the U.S.
can take to complete the overall
phaseout of ODS and further decrease
impacts on children’s health from
stratospheric ozone depletion.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not a ‘‘significant
energy action’’ as defined in Executive
Order 13211 (66 FR 28355 (May 22,
2001)), because it is not likely to have
a significant adverse effect on the
supply, distribution, or use of energy.
The rule issues allowances for the
production and consumption of HCFCs.
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Federal Register / Vol. 77, No. 2 / Wednesday, January 4, 2012 / Proposed Rules
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, 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. This
action does not involve technical
standards. Therefore, EPA did not
consider 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 (Feb. 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 U.S.
EPA has determined that this action
will not have disproportionately high
and adverse human health or
environmental effects on minority or
low-income populations because the
2010 phaseout step increases the level
of environmental protection for all
affected populations without having any
disproportionately high and adverse
human health or environmental effects
on any population, including any
minority or low-income population.
This action continues the
implementation of the U.S. commitment
to reduce the total basket of HCFCs
produced and imported to a level that
is 75 percent below the respective
baselines. While on an ODP-weighted
basis, this is not as large a step as
previous actions, such as the 1996 Class
I phaseout, it is one of the most
significant remaining actions the U.S.
can take to complete the overall
phaseout of ODS and further lessen the
adverse human health effects for the
entire population.
List of Subjects in 40 CFR Part 82
Environmental protection,
Administrative practice and procedure,
Air pollution control, Chemicals,
Exports, Hydrochlorofluorocarbons,
Imports.
Dated: December 22, 2011.
Lisa P. Jackson,
Administrator.
40 CFR part 82 is proposed to be
amended to read as follows:
PART 82—PROTECTION OF
STRATOSPHERIC OZONE
1. The authority citation for part 82
continues to read as follows:
Authority: 42 U.S.C. 7414, 7601, 7671–
7671q.
2. Amend § 82.16 by revising
paragraph (a) to read as follows:
§ 82.16 Phaseout schedule of class II
controlled substances.
(a) Calendar-year Allowances. (1) In
each control period as indicated in the
following tables, each person is granted
the specified percentage of baseline
production allowances and baseline
consumption allowances for the
specified class II controlled substances
apportioned under §§ 82.17 and 82.19:
CALENDAR-YEAR HCFC PRODUCTION ALLOWANCES
Control period
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
2013
2014
Percent of
HCFC–141b
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
Percent of
HCFC–22
0
0
0
0
0
0
0
0
0
0
0
0
Percent of
HCFC–142b
100
100
100
100
100
100
100
41.9
32.0
17.7
14.7
11.6
100
100
100
100
100
100
100
0.47
4.9
4.9
4.9
4.9
Percent of
HCFC–123
Percent of
HCFC–124
Percent of
HCFC–225ca
Percent of
HCFC–225cb
........................
........................
........................
........................
........................
........................
........................
125
125
125
125
125
........................
........................
........................
........................
........................
........................
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125
125
125
125
125
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125
125
125
125
125
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........................
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125
125
125
125
125
CALENDAR-YEAR HCFC CONSUMPTION ALLOWANCES
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Control period
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
2013
2014
Percent of
HCFC–141b
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
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HCFC–22
0
0
0
0
0
0
0
0
0
0
0
0
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HCFC–142b
100
100
100
100
100
100
100
41.9
32.0
17.7
14.7
11.6
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100
100
100
100
100
100
0.47
4.9
4.9
4.9
4.9
Fmt 4702
Percent of
HCFC–123
Percent of
HCFC–124
Percent of
HCFC–225ca
Percent of
HCFC–225cb
........................
........................
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125
125
125
125
125
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125
125
125
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(2) Recoupment allowances. In the
control period beginning January 1,
2013 and ending December 31, 2013, the
following companies are granted a onetime amount of HCFC consumption and
production allowances in addition to
the percentage of baseline listed in the
table at paragraph (a)(1) of this section:
4,749,692 kg of HCFC–22 consumption
allowances and 4,611,848 kg of HCFC–
22 production allowances to Arkema;
2,339 kg of HCFC–142b consumption
allowances to DuPont; 58,291 kg of
HCFC–142b consumption allowances
and 107,097 kg of production
allowances to Honeywell; 1,157,895 kg
of HCFC–22 consumption allowances to
Solvay Fluorides; and 289,800 kg of
HCFC–142b production allowances to
Solvay Solexis.
*
*
*
*
*
3. Amend § 82.23 by revising
paragraphs (a)(ii) introductory text,
(a)(ii)(A), (b)(1), and (d) to read as
follows:
§ 82.23 Transfers of allowances of class II
controlled substances.
wreier-aviles on DSK3TPTVN1PROD with PROPOSALS
(a) * * * (ii) The Administrator will
determine whether the records
maintained by EPA indicate that the
transferor possesses unexpended
allowances sufficient to cover the
transfer claim on the date the transfer
claim is processed. The transfer claim is
the quantity (in kilograms) to be
transferred plus 0.1 percent of that
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14:52 Jan 03, 2012
Jkt 226001
quantity. The Administrator will take
into account any previous transfers, any
production, and allowable imports and
exports of class II controlled substances
reported by the transferor. Within three
working days of receiving a complete
transfer claim, the Administrator will
take action to notify the transferor and
transferee as follows:
(A) The Administrator will issue a
notice indicating that EPA does not
object to the transfer if EPA’s records
show that the transferor has sufficient
unexpended allowances to cover the
transfer claim. In the case of transfers of
production or consumption allowances,
EPA will reduce the transferor’s balance
of unexpended allowances by the
quantity to be transferred plus 0.1
percent of that quantity. In the case of
transfers of export production or Article
5 allowances, EPA will reduce the
transferor’s balance of unexpended
allowances, respectively, by the
quantity to be transferred plus 0.1
percent of that quantity. The transferor
and the transferee may proceed with the
transfer when EPA issues a no objection
notice. However, if EPA ultimately finds
that the transferor did not have
sufficient unexpended allowances to
cover the claim, the transferor and
transferee, where applicable, will be
held liable for any knowing violations of
the regulations of this subpart that occur
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259
as a result of, or in conjunction with, the
improper transfer.
*
*
*
*
*
(b) Inter-pollutant transfers. (1)
Effective January 1, 2003, a person
(transferor) may convert consumption
allowances, production allowances or
Article 5 allowances for one class II
controlled substance to the same type of
allowance for another class II controlled
substance listed in Appendix B of this
subpart, following the procedures
described in paragraph (b)(3) of this
section.
*
*
*
*
*
(d) Permanent transfers. The
procedures in paragraph (a) of this
section apply to permanent intercompany transfers of baseline
production allowances or baseline
consumption allowances. A person
receiving a permanent transfer of
baseline production allowances or
baseline consumption allowances (the
transferee) for a specific class II
controlled substance will be the person
who has their baseline allowances
adjusted in accordance with phaseout
schedules in this subpart. No person
may conduct permanent inter-pollutant
transfers of baseline production
allowances or baseline consumption
allowances.
*
*
*
*
*
[FR Doc. 2011–33456 Filed 1–3–12; 8:45 am]
BILLING CODE 6560–50–P
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Agencies
[Federal Register Volume 77, Number 2 (Wednesday, January 4, 2012)]
[Proposed Rules]
[Pages 237-259]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-33456]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 82
[EPA-HQ-OAR-2011-0354; FRL-9614-5]
RIN 2060-AQ98
Protection of Stratospheric Ozone: Adjustments to the Allowance
System for Controlling HCFC Production, Import, and Export
AGENCY: Environmental Protection Agency [EPA].
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: EPA is proposing to adjust the allowance system controlling
U.S. consumption and production of hydrochlorofluorocarbons (HCFCs) as
a result of a recent court decision vacating a portion of the rule
titled ``Protection of Stratospheric Ozone: Adjustments to the
Allowance System for Controlling HCFC Production, Import, and Export;
Final Rule.'' EPA interprets the court's vacatur as applying to the
part of the rule that establishes the company-by-company baselines and
calendar-year allowances for HCFC-22 and HCFC-142b. Following the
August 5, 2011 interim final rule allocating allowances for 2011, this
action proposes to relieve the regulatory ban on production and
consumption of these two chemicals following the court's vacatur by
establishing company-by-company HCFC-22 and HCFC-142b baselines and
allocating production and consumption allowances for 2012-2014.
DATES: Written comments on this proposed rule must be received by the
EPA Docket on or before February 3, 2012, unless a public hearing is
requested. Any party requesting a public hearing must notify the
contact listed below under FOR FURTHER INFORMATION CONTACT by 5 p.m.
Eastern Standard Time on January 11, 2012. If a public hearing is
requested, the hearing would be held on January 19, 2012 and commenters
will have until February 21, 2012 to submit comments before the close
of the comment period. If a hearing is held, it will take place at EPA
headquarters in Washington, DC. EPA will post a notice on our Web site,
https://www.epa.gov/ozone/strathome.html, announcing further information
should a hearing take place.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
OAR-2011-0354, by one of the following methods:
www.regulations.gov: Follow the on-line instructions for
submitting comments.
Email: a-and-r-docket@epa.gov.
Mail: Docket EPA-HQ-OAR-2011-0354, Air and
Radiation Docket and Information Center, U.S. Environmental Protection
Agency, Mail code: 6102T, 1200 Pennsylvania Ave. NW., Washington, DC
20460.
Hand Delivery: Docket EPA-HQ-OAR-2011-0354 Air
and Radiation Docket at EPA West, 1301 Constitution Avenue NW., Room
B108, Mail Code 6102T, Washington, DC 20004. Such deliveries are only
accepted during the Docket's normal hours of operation, and special
arrangements should be made for deliveries of boxed information.
Instructions: Direct your comments to Docket ID No. EPA-HQ-OAR-
2011-0354. EPA's policy is that all comments received will be included
in the public docket without change and may be
[[Page 238]]
made available online at www.regulations.gov, including any personal
information provided, unless the comment includes information claimed
to be Confidential Business Information (CBI) or other information
whose disclosure is restricted by statute. Do not submit information
that you consider to be CBI or otherwise protected through
www.regulations.gov or email. The www.regulations.gov Web site is an
``anonymous access'' system, which means EPA will not know your
identity or contact information unless you provide it in the body of
your comment. If you send an email comment directly to EPA without
going through www.regulations.gov, your email address will be
automatically captured and included as part of the comment that is
placed in the public docket and made available on the Internet. If you
submit an electronic comment, EPA recommends that you include your name
and other contact information in the body of your comment and with any
disk or CD-ROM you submit. If EPA cannot read your comment due to
technical difficulties and cannot contact you for clarification, EPA
may not be able to consider your comment. Electronic files should avoid
the use of special characters, any form of encryption, and be free of
any defects or viruses. For additional information about EPA's public
docket, visit the EPA Docket Center homepage at www.epa.gov/epahome/dockets.htm.
FOR FURTHER INFORMATION CONTACT: Luke H. Hall-Jordan by telephone at
(202) 343-9591, or by email at hall-jordan.luke@epa.gov, or by mail at
U.S. Environmental Protection Agency, Stratospheric Protection
Division, Stratospheric Program Implementation Branch (6205J), 1200
Pennsylvania Avenue NW., Washington, DC 20460. You may also visit the
Ozone Protection Web site of EPA's Stratospheric Protection Division at
www.epa.gov/ozone/strathome.html for further information about EPA's
Stratospheric Ozone Protection regulations, the science of ozone layer
depletion, and related topics.
SUPPLEMENTARY INFORMATION:
Acronyms and Abbreviations. The following acronyms and
abbreviations are used in this document.
CAA--Clean Air Act
CAAA--Clean Air Act Amendments of 1990
CFC--Chlorofluorocarbon
CFR--Code of Federal Regulations
EPA--Environmental Protection Agency
FR--Federal Register
HCFC--Hydrochlorofluorocarbon
HVAC--Heating, Ventilating, and Air Conditioning
Montreal Protocol--Montreal Protocol on Substances that Deplete the
Ozone Layer
MOP--Meeting of the Parties
MT--Metric Ton
ODP--Ozone Depletion Potential
ODS--Ozone-Depleting Substances
Party--States and regional economic integration organizations that
have consented to be bound by the Montreal Protocol on Substances
that Deplete the Ozone Layer
Organization of This Document. The following outline is provided to
aid in locating information in this preamble.
I. General Information
A. Does this action apply to me?
B. What should I consider as I prepare my comments for EPA?
1. Confidential Business Information (CBI)
2. Tips for Preparing Your Comments
II. Background
A. How does the Montreal Protocol phase out HCFCs?
B. How does the Clean Air Act phase out HCFCs?
C. What sections of the Clean Air Act apply to this rulemaking?
D. How does this action relate to the recent court decision?
E. Comments Relevant to Recovery and Reclamation Issues in This
Rulemaking Submitted in Response to the 2011 Interim Final Rule
Allocating HCFC Allowances
III. How does EPA propose to allocate HCFC-22 and HCFC-142b
allowances for 2012-2014?
A. What baselines does EPA propose to use for HCFC-22 and HCFC-
142b allowances?
B. What factors did EPA consider in proposing allocation amounts
for HCFC-22 and HCFC-142b?
1. How important is HCFC-22 relative to HCFC-142b for servicing
existing equipment?
2. Can servicing needs be met with virgin and recovered
material?
3. How would the allocation decline?
4. How will EPA address the court's decision with regard to 2010
HCFC allowances?
C. How Much HCFC-22 and HCFC-142b would be allocated in 2012-
2014?
1. How does EPA propose to allocate HCFC-22 consumption
allowances for 2012-2014?
2. How does EPA Propose to allocate HCFC-22 production
allowances for 2012-2014?
3. How does EPA propose to allocate HCFC-142b consumption and
production allowances for 2012-2014?
4. How would the aggregate for HCFC-22 and HCFC-142b translate
entity-by-entity?
D. Are HCFC-141b, HCFC-123, HCFC-124, HCFC-225ca, and HCFC-225cb
allowances affected by this rulemaking?
E. How will EPA allocate other HCFCs?
IV. How does EPA propose to change the regulations governing
transfers of allowances of Class II Controlled Substances?
A. How does EPA propose to change the regulations governing
permanent transfers of Class II Allowances?
B. How does EPA propose to change the regulations governing
transfers of Article 5 HCFC Allowances?
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 (RFA)
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
I. General Information
A. Does this action apply to me?
This rule will affect the following categories:
--Industrial Gas Manufacturing entities (NAICS code 325120), including
fluorinated hydrocarbon gases manufacturers and reclaimers;
--Other Chemical and Allied Products Merchant Wholesalers (NAICS code
422690), including chemical gases and compressed gases merchant
wholesalers;
--Air-Conditioning and Warm Air Heating Equipment and Commercial and
Industrial Refrigeration Equipment Manufacturing entities (NAICS code
333415), including air-conditioning equipment and commercial and
industrial refrigeration equipment manufacturers;
--Air-Conditioning Equipment and Supplies Merchant Wholesalers (NAICS
code 423730), including air-conditioning (condensing unit, compressors)
merchant wholesalers;
--Electrical and Electronic Appliance, Television, and Radio Set
Merchant Wholesalers (NAICS code 423620), including air-conditioning
(room units) merchant wholesalers; and
--Plumbing, Heating, and Air-Conditioning Contractors (NAICS code
238220), including Central air-conditioning system and commercial
refrigeration installation; HVAC contractors.
This list is not intended to be exhaustive, but rather provides a guide
[[Page 239]]
for readers regarding entities likely to be regulated by this action.
This table lists the types of entities that could potentially be
regulated by this action. Other types of entities not listed in this
table could also be affected. To determine whether your facility,
company, business organization, or other entity is regulated by this
action, you should carefully examine these regulations. If you have
questions regarding the applicability of this action to a particular
entity, consult the person listed in the FOR FURTHER INFORMATION
CONTACT section.
B. What should I consider as I prepare my comments for EPA?
1. Confidential Business Information (CBI)
Do not submit confidential business information (CBI) to EPA
through www.regulations.gov or email. Clearly mark the part or all of
the information that you claim to be CBI. For CBI information in a disk
or CD-ROM that you mail to EPA, mark the outside of the disk or CD-ROM
as CBI and then identify electronically within the disk or CD-ROM the
specific information that is claimed as CBI. In addition to one
complete version of the comment that includes information claimed as
CBI, a copy of the comment that does not contain the information
claimed as CBI must be submitted for inclusion in the public docket.
Information so marked will not be disclosed except in accordance with
procedures set forth in 40 CFR 2.2.
2. Tips for Preparing Your Comments
When submitting comments, remember to do the following:
Identify the rulemaking by docket number and other
identifying information (subject heading, Federal Register date and
page number).
Follow directions. The Agency may ask you to respond to
specific questions or organize comments by referencing a Code of
Federal Regulations (CFR) part or section number.
Explain why you agree or disagree with the proposal;
suggest alternatives and substitute language for your requested
changes.
Describe any assumptions and provide any technical
information and/or data that you used in preparing your comments.
If you estimate potential costs or burdens, explain how
you arrived at your estimate in sufficient detail to allow for it to be
reproduced.
Provide specific examples to illustrate your concerns, and
suggest alternatives.
Explain your views as clearly as possible, avoiding the
use of profanity or personal threats.
Make sure to submit your comments by the comment period
deadline identified.
II. Background
EPA is undertaking this rulemaking as a result of the decision
issued by the U.S. Court of Appeals for the District of Columbia
Circuit (Court) in Arkema v. EPA (618 F.3d 1, DC Cir. 2010) regarding
the December 15, 2009, final rule titled ``Protection of Stratospheric
Ozone: Adjustments to the Allowance System for Controlling HCFC
Production, Import, and Export,'' published at 74 FR 66413 (2009 Final
Rule). Certain allowance holders affected by the 2009 Final Rule filed
petitions for judicial review of the rule under section 307(b) of the
Clean Air Act. Among other arguments, the petitioners contended that
the rule was impermissibly retroactive because in setting the baselines
for the new regulatory period, EPA did not take into account certain
inter-pollutant baseline transfers that petitioners had performed
during the prior regulatory period.
The Court issued a decision on August 27, 2010, agreeing with
petitioners that ``the [2009] Final Rule unacceptably alters
transactions the EPA approved under the 2003 Rule,'' (Arkema v. EPA,
618 F.3d at 3). The Court vacated the rule in part, ``insofar as it
operates retroactively,'' and remanded to EPA ``for prompt
resolution,'' (618 F.3d at 10). The Court withheld the mandate for the
decision pending the disposition of any petition for rehearing. EPA's
petition for rehearing was denied on January 21, 2011. The mandate
issued on February 4, 2011. More detail is provided on the case and
EPA's interpretation of the Court's decision in section II.D. of this
preamble.
EPA addressed the Court's partial vacatur as it relates to 2011 in
an August 5, 2011, interim final rule, ``Protection of Stratospheric
Ozone: Adjustments to the Allowance System for Controlling HCFC
Production, Import, and Export,'' (2011 Interim Final Rule). This
proposed rule is a follow-on to that action, and proposes a path
forward for the remainder of the regulatory period ending on December
31, 2014.
A. How does the Montreal Protocol phase out HCFCs?
The Montreal Protocol on Substances that Deplete the Ozone Layer is
the international agreement aimed at reducing and eventually
eliminating the production and consumption of stratospheric ozone-
depleting substances (ODS). The U.S. was one of the original
signatories to the 1987 Montreal Protocol and the U.S. ratified the
Protocol on April 12, 1988. Congress then enacted, and President George
H.W. Bush signed into law, the Clean Air Act Amendments of 1990 (CAAA),
which included Title VI on Stratospheric Ozone Protection, codified as
42 U.S.C. Chapter 85, Subchapter VI, to ensure that the U.S. could
satisfy its obligations under the Montreal Protocol. Title VI includes
restrictions on production, consumption, and use of ODS that are
subject to acceleration if ``the Montreal Protocol is modified to
include a schedule to control or reduce production, consumption, or use
* * * more rapidly than the applicable schedule'' prescribed by the
statute (CAA Sec. 606). Both the Montreal Protocol and the Clean Air
Act (CAA) define consumption as production plus imports minus exports.
In 1990, as part of the London Amendment to the Montreal Protocol,
the Parties identified HCFCs as ``transitional substances'' to serve as
temporary, lower ozone depletion potential (ODP) substitutes for CFCs
and other ODS. EPA similarly viewed HCFCs as ``important interim
substitutes that will allow for the earliest possible phaseout of CFCs
and other Class I substances''\1\ (58 FR 65026). In 1992, through the
Copenhagen Amendment to the Montreal Protocol, the Parties created a
detailed phaseout schedule for HCFCs beginning with a cap on
consumption for developed countries not operating under Article 5 of
the Montreal Protocol (non-Article 5 Parties), a schedule to which the
U.S. adheres. The consumption cap for each non-Article 5 Party was set
at 3.1 percent (later tightened to 2.8 percent) of a Party's CFC
consumption in 1989, plus a Party's consumption of HCFCs in 1989
(weighted on an ODP basis). Based on this formula, the HCFC consumption
cap for the U.S. was 15,240 ODP-weighted metric tons (MT), effective
January 1, 1996. This became the U.S. consumption baseline for HCFCs.
---------------------------------------------------------------------------
\1\ Class I refers to the controlled substances listed in
appendix A to 40 CFR part 82 subpart A. Class II refers to the
controlled substances listed in appendix B to 40 CFR part 82 subpart
A.
---------------------------------------------------------------------------
The 1992 Copenhagen Amendment created a schedule with graduated
reductions and the eventual phaseout of HCFC consumption (Copenhagen,
23-25 November, 1992, Decision IV/4). Prior to a later adjustment in
2007, the schedule initially called for a 35 percent reduction of the
consumption cap in 2004, followed by a 65 percent
[[Page 240]]
reduction in 2010, a 90 percent reduction in 2015, a 99.5 percent
reduction in 2020 (restricting the remaining 0.5 percent of baseline to
the servicing of existing refrigeration and air-conditioning
equipment), with a total phaseout in 2030.
The Copenhagen Amendment did not cap HCFC production. In 1999, the
Parties created a cap on production for Non-Article 5 Parties through
an amendment to the Montreal Protocol agreed by the Eleventh Meeting of
the Parties (Beijing, 29 November--3 December 1999, Decision XI/5). The
cap on production was set at the average of: (a) 1989 HCFC production
plus 2.8 percent of 1989 CFC production, and (b) 1989 HCFC consumption
plus 2.8 percent of 1989 CFC consumption. Based on this formula, the
HCFC production cap for the U.S. was 15,537 ODP-weighted MT, effective
January 1, 2004. This became the U.S. production baseline for HCFCs.
To further protect human health and the environment, the Parties to
the Montreal Protocol adjusted the Montreal Protocol's phaseout
schedule for HCFCs at the 19th Meeting of the Parties in September
2007. In accordance with Article 2(9)(d) of the Montreal Protocol, the
adjustment to the phaseout schedule was effective on May 14, 2008.\2\
---------------------------------------------------------------------------
\2\ Under Article 2(9)(d) of the Montreal Protocol, an
adjustment enters into force six months from the date the depositary
(the Ozone Secretariat) circulates it to the Parties. The depositary
accepts all notifications and documents related to the Protocol and
examines whether all formal requirements are met. In accordance with
the procedure in Article 2(9)(d), the depositary communicated the
adjustment to all Parties on November 14, 2007. The adjustment
entered into force and became binding for all Parties on May 14,
2008.
---------------------------------------------------------------------------
As a result of the 2007 Montreal Adjustment (reflected in Decision
XIX/6), the U.S. and other developed countries are obligated to reduce
HCFC production and consumption 75 percent below the established
baseline by 2010, rather than 65 percent as previously required. The
other milestones remain the same. The adjustment also resulted in a
phaseout schedule for HCFC production that parallels the consumption
phaseout schedule. All production and consumption for Non-Article 5
Parties is phased out by 2030.
Decision XIX/6 also adjusted the provisions for Parties operating
under paragraph 1 of Article 5 (developing countries): (1) To set HCFC
production and consumption baselines based on the average 2009-2010
production and consumption, respectively; (2) to freeze HCFC production
and consumption at those baselines in 2013; and (3) to add stepwise
reductions of 10 percent below baselines by 2015, 35 percent by 2020,
67.5 percent by 2025, and 97.5 percent by 2030--allowing, between 2030
and 2040, an annual average of no more than 2.5 percent to be produced
or imported solely for servicing existing air-conditioning and
refrigeration equipment. All production and consumption for Article 5
Parties will be phased out by 2040.
In addition, Decision XIX/6 adjusted Article 2F to allow developed
countries to produce ``up to 10 percent of baseline levels'' for export
to Article 5 countries ``in order to satisfy basic domestic needs''
until 2020.\3\ Paragraph 14 of Decision XIX/6 notes that no later than
2015, the Parties would consider ``further reduction of production for
basic domestic needs'' in 2020 and beyond. Under paragraph 13 of
Decision XIX/6, the Parties will review in 2015 and 2025, respectively,
the need for the ``servicing tails'' for developed and developing
countries. The term ``servicing tail'' refers to an amount of HCFCs
used to service existing equipment, such as certain types of air-
conditioning and refrigeration appliances.
---------------------------------------------------------------------------
\3\ Paragraphs 4-6 of adjusted Article 2F read as follows:
``4. Each Party shall ensure that for the twelve-month period
commencing on 1 January 2010, and in each twelve-month period
thereafter, its calculated level of consumption of the controlled
substances in Group I of Annex C does not exceed, annually, twenty-
five per cent of the sum referred to in paragraph 1 of this Article.
Each Party producing one or more of these substances shall, for the
same periods, ensure that its calculated level of production of the
controlled substances in Group I of Annex C does not exceed,
annually, twenty-five per cent of the calculated level referred to
in paragraph 2 of this Article. However, in order to satisfy the
basic domestic needs of the Parties operating under paragraph 1 of
Article 5, its calculated level of production may exceed that limit
by up to ten per cent of its calculated level of production of the
controlled substances in Group I of Annex C as referred to in
paragraph 2.
5. Each Party shall ensure that for the twelve-month period
commencing on 1 January 2015, and in each twelve-month period
thereafter, its calculated level of consumption of the controlled
substances in Group I of Annex C does not exceed, annually, ten per
cent of the sum referred to in paragraph 1 of this Article. Each
Party producing one or more of these substances shall, for the same
periods, ensure that its calculated level of production of the
controlled substances in Group I of Annex C does not exceed,
annually, ten per cent of the calculated level referred to in
paragraph 2 of this Article. However, in order to satisfy the basic
domestic needs of the Parties operating under paragraph 1 of Article
5, its calculated level of production may exceed that limit by up to
ten per cent of its calculated level of production of the controlled
substances in Group I of Annex C as referred to in paragraph 2.
6. Each Party shall ensure that for the twelve-month period
commencing on 1 January 2020, and in each twelve-month period
thereafter, its calculated level of consumption of the controlled
substances in Group I of Annex C does not exceed zero. Each Party
producing one or more of these substances shall, for the same
periods, ensure that its calculated level of production of the
controlled substances in Group I of Annex C does not exceed zero.
However:
i. each Party may exceed that limit on consumption by up to zero
point five per cent of the sum referred to in paragraph 1 of this
Article in any such twelve-month period ending before 1 January
2030, provided that such consumption shall be restricted to the
servicing of refrigeration and air conditioning equipment existing
on 1 January 2020;
ii. each Party may exceed that limit on production by up to zero
point five per cent of the average referred to in paragraph 2 of
this Article in any such twelve-month period ending before 1 January
2030, provided that such production shall be restricted to the
servicing of refrigeration and air conditioning equipment existing
on 1 January 2020.''
---------------------------------------------------------------------------
B. How does the clean air act phase out HCFCs?
The U.S. has chosen to implement the Montreal Protocol phaseout
schedule on a chemical-by-chemical basis. In 1992, environmental and
industry groups petitioned EPA to implement the required phaseout by
eliminating the most ozone-depleting HCFCs first. Based on the
available data at that time, EPA believed the U.S. could meet, and
possibly exceed, the required Montreal Protocol reductions through a
chemical-by-chemical phaseout that employed a ``worst-first'' approach
focusing on certain chemicals earlier than others. In 1993, as
authorized by section 606 of the CAA, the U.S. established a phaseout
schedule that eliminated HCFC-141b first and would greatly restrict
HCFC-142b and HCFC-22 next, followed by restrictions on all other HCFCs
and ultimately a complete phaseout (58 FR 15014, March 18, 1993; 58 FR
65018, December 10, 1993).
On January 21, 2003 (68 FR 2820), EPA promulgated regulations (2003
Final Rule) to ensure compliance with the first reduction milestone in
the HCFC phaseout: The requirement that by January 1, 2004, the U.S.
reduce HCFC consumption by 35 percent and freeze HCFC production. In
the 2003 Final Rule, EPA established chemical-specific consumption and
production baselines for HCFC-141b, HCFC-22, and HCFC-142b for the
initial regulatory period ending December 31, 2009. Section 601(2)
states that EPA may select ``a representative calendar year'' to serve
as the company baseline for HCFCs. In the 2003 Final Rule, EPA
concluded that because the entities eligible for allowances had
differing production and import histories, no single year was
representative for all companies. Therefore, EPA assigned an individual
consumption baseline year to each company by selecting its highest ODP-
weighted consumption year from among the years 1994 through 1997.
[[Page 241]]
EPA assigned individual production baseline years in the same manner.
EPA also provided for new entrants that began importing after the end
of 1997 but before April 5, 1999, the date the advanced notice of
proposed rulemaking was published. EPA took this action to ensure that
small businesses that might not have been aware of the impending
rulemaking would be able to continue in the HCFC market.
The 2003 Final Rule apportioned production and consumption
baselines to each company in amounts equal to the amounts in the
company's highest ``production year'' or ``consumption year,'' as
described above. It completely phased out the production and import of
HCFC-141b by granting 0 percent of that substance's baseline for
production and consumption in the table at 40 CFR 82.16. EPA did,
however, create a petition process to allow applicants to request small
amounts of HCFC-141b beyond the phaseout. The 2003 Final Rule also
granted 100 percent of the baselines for production and consumption of
HCFC-22 and HCFC-142b for each of the years 2003 through 2009. EPA was
able to allocate allowances for HCFC-22 and HCFC-142b at 100 percent of
baseline because, in light of the concurrent complete phaseout of HCFC-
141b, the allocations for HCFC-22 and HCFC-142b, combined with
projections for consumption of all other HCFCs, remained below the 2004
cap of 65 percent of the U.S. baseline.
EPA allocates allowances for specific years; they are valid between
January 1 and December 31 of a given control period (i.e., calendar
year). Prior to December 15, 2009, EPA had not allocated any HCFC
allowances for year 2010 or beyond. The regulations at section 82.15(a)
and (b) only addressed the production and import of HCFC-22 and HCFC-
142b for the years 2003-2009. Through the 2009 Final Rule (74 FR
66412), EPA addressed the production and import of HCFC-22 and HCFC-
142b for the 2010-2014 control periods. Absent the granting of
calendar-year allowances, section 82.15 would have prohibited the
production and import of HCFC-22 and HCFC-142b after December 31, 2009.
The 2009 Final Rule allowed for continued production and consumption,
at specified amounts, of HCFC-142b, HCFC-22, and other HCFCs not
previously included in the allowance system, for the 2010-2014 control
periods.
In the U.S., an allowance is the unit of measure that controls
production and consumption of ODS. EPA establishes company-by-company
baselines (also known as ``baseline allowances'') and allocates
calendar-year allowances equal to a percentage of the baseline for
specified control periods. A calendar-year allowance represents the
privilege granted to a company to produce or import one kilogram (not
ODP-weighted) of the specific substance. EPA allocates two types of
calendar-year allowances--production allowances and consumption
allowances. ``Production allowance'' and ``consumption allowance'' are
defined at section 82.3. To produce an HCFC for which allowances have
been allocated, an allowance holder must expend both production and
consumption allowances. To import an HCFC for which allowances have
been allocated, an allowance holder must expend consumption allowances.
An allowance holder exporting HCFCs for which it has expended
consumption allowances may obtain a refund of those consumption
allowances upon submittal of proper documentation to EPA.
Since EPA is implementing the phaseout on a chemical-by-chemical
basis, it allocates and tracks production and consumption allowances on
an absolute kilogram basis for each chemical. Upon EPA approval, an
allowance holder may transfer calendar-year allowances of one type of
HCFC for calendar-year allowances of another type of HCFC, with
transactions weighted according to the ODP of the chemicals involved.
Pursuant to section 607 of the CAA, EPA applies an offset to each HCFC
transfer by deducting 0.1 percent from the transferor's allowance
balance. The offset benefits the ozone layer since it ``results in
greater total reductions in the production in each year of * * * class
II substances than would occur in that year in the absence of such
transactions'' (42 U.S.C. 7671f).
The U.S. remained comfortably below the aggregate HCFC cap through
2009. The 2003 Final Rule announced that EPA would allocate allowances
for 2010-2014 in a subsequent action and that those allowances would be
lower in aggregate than for 2003-2009, consistent with the next
stepwise reduction for HCFCs under the Montreal Protocol. EPA stated
its intention to determine the number of allowances that would be
needed for HCFC-22 and HCFC-142b, bearing in mind that other HCFCs
would also contribute to total HCFC consumption. EPA noted that it
would likely achieve the 2010 reduction step by applying a percentage
reduction to the HCFC-22 and HCFC-142b baselines. EPA subsequently
monitored the market to estimate servicing needs and market adjustments
in the use of HCFCs, including HCFCs for which EPA did not establish
baselines in the 2003 Final Rule.
In the 2009 Final Rule, EPA determined both the estimated demand
for HCFC-22 during the 2010-2014 regulatory period and the percentage
of that estimated demand for which it was appropriate to allocate
allowances. As described in section III.B. of this action, EPA
determined that the percentage of the estimated demand allocated in the
form of allowances should not remain constant from year to year but
rather should decline on an annual basis. For 2010, EPA allocated
allowances equal to 80 percent of the estimated demand for HCFC-22,
concluding that reused, recycled, and reclaimed material could meet the
remaining 20 percent. Under the 2009 Final Rule, the percentage of
estimated demand for which there was no allocation, and therefore would
need to be met through recycling and reclamation, rose from 20 percent
in 2010 to 29 percent in 2014 to ensure the U.S. market would have a
viable reclamation industry and could meet the 2015 stepwise reduction
under the Montreal Protocol.
The determinations EPA made in the 2009 Final Rule regarding (1)
the total estimated demand for HCFC-22 in 2010-2014 and (2) the
percentage of that estimated demand that EPA would address through an
allowance allocation were not at issue in the litigation and are
unaffected by the Court's decision. As such, EPA did not revisit either
determination with respect to 2011 in the 2011 Interim Final Rule (76
FR 47451), but rather relied on the existing record from the 2009 Final
Rule (74 FR 66412). The 2011 Interim Final Rule established new
baselines that (1) credited the 2008 inter-pollutant trades at issue in
Arkema v. EPA based on the Court's decision and (2) reflected inter-
company, single-pollutant baseline transfers that occurred since the
2009 Final Rule was signed. The 2011 Interim Final Rule also (3)
allocated HCFC-22 and HCFC-142b allowances for 2011, (4) clarified
EPA's policy on all future inter-pollutant transfers, and (5) updated
company names.
C. What sections of the Clean Air Act apply to this rulemaking?
Several sections of the CAA apply to this rulemaking. Section 605
of the CAA phases out production and consumption and restricts the use
of HCFCs in accordance with the schedule set forth in that section. As
discussed in the 2009 Final Rule (74 FR 66416), section 606 provides
EPA authority to set a more stringent phaseout schedule than the
schedule in section 605 based on an
[[Page 242]]
EPA determination regarding current scientific information or the
availability of substitutes, or to conform to any acceleration under
the Montreal Protocol. EPA previously set a more stringent schedule
than the section 605 schedule through a rule published December 10,
1993 (58 FR 65018). Through the 2009 Final Rule, EPA made a further
adjustment to the section 605 schedule based on the acceleration under
the Montreal Protocol as agreed to at the Meeting of the Parties in
September 2007. The more stringent schedule established in that rule is
unaffected by the recent Court decision and is therefore still in
effect.
Section 606 provides authority for EPA to promulgate regulations
that establish a schedule for production and consumption that is more
stringent than what is set forth in section 605 if: ``(1) based on an
assessment of credible current scientific information (including any
assessment under the Montreal Protocol) regarding harmful effects on
the stratospheric ozone layer associated with a class I or class II
substance, the Administrator determines that such more stringent
schedule may be necessary to protect human health and the environment
against such effects, (2) based on the availability of substitutes for
listed substances, the Administrator determines that such more
stringent schedule is practicable, taking into account technological
achievability, safety, and other relevant factors, or (3) the Montreal
Protocol is modified to include a schedule to control or reduce
production, consumption, or use of any substance more rapidly than the
applicable schedule under this title.'' It is only necessary to meet
one of the three criteria. In the 2009 Final Rule, EPA determined that
all three criteria had been met with respect to the schedule for
phasing out production and consumption of HCFC-22 and HCFC-142b.
As noted in the 2009 Final Rule, while section 606 is sufficient
authority for establishing a more stringent schedule than the section
605 phaseout schedule, section 614(b) of the CAA provides that in the
case of a conflict between the CAA and the Montreal Protocol, the more
stringent provision shall govern. Thus, section 614(b) requires the
Agency to establish phaseout schedules at least as stringent as the
schedules contained in the Montreal Protocol. To meet the 2010 stepdown
requirement, EPA is continuing to allocate HCFC allowances at a level
that will ensure the aggregate HCFC production and consumption will not
exceed 25 percent of the U.S. baselines. For more discussion of this
point, see 74 FR 66416.
Finally, section 607 addresses transfers of allowances both between
companies and chemicals. EPA is further clarifying the policy and
procedures applicable to permanent inter-pollutant transfers in this
action, and is proposing a minor change to the regulations governing
inter-pollutant transfers to provide additional clarity to
stakeholders.
D. How does this action relate to the recent court decision?
Certain allowance holders affected by the 2009 Final Rule filed
petitions for review in the U.S. Court of Appeals for the District of
Columbia Circuit. Among other arguments, the petitioners, Arkema, Inc.,
Solvay Fluorides, LLC, and Solvay Solexis, Inc., contended that the
rule was impermissibly retroactive because in setting the baselines for
the new regulatory period, EPA did not take into account certain inter-
pollutant baseline transfers that petitioners had performed during the
prior regulatory period. The 2011 Interim Final Rule contained a
description of those transfers and the EPA approvals of those
transfers. As explained in the 2011 Interim Final Rule, the transfers
at issue occurred in 2008. Solvay Solexis, Inc. submitted two Class II
Controlled Substance Transfer Forms for consumption allowance transfers
to Solvay Fluorides, LLC on February 15, 2008, and March 4, 2008.
Arkema, Inc. submitted two Class II Controlled Substance Transfer Forms
for consumption and production allowance transfers on April 18, 2008.
Each company requested EPA's approval to convert HCFC-142b allowances
to HCFC-22 allowances, and checked a box on the EPA transfer form
indicating that ``baseline'' allowances would be transferred. EPA sent
non-objection notices to both Solvay Solexis, Inc. and Solvay
Fluorides, LLC on February 21, 2008 and March 20, 2008 and to Arkema,
Inc. in April 2008. The transfer requests and EPA's approvals were
attached to petitioners' court filings and are available in the docket
for this action.
In the Notice of Proposed Rulemaking titled ``Protection of
Stratospheric Ozone: Adjustments to the Allowance System for
Controlling HCFC Production, Import, and Export,'' published in the
Federal Register at 73 FR 78680 on December 23, 2008 (2008 Proposed
Rule), EPA requested comments on establishing baselines for the 2010-
2014 regulatory period ``with or without'' taking into account baseline
inter-pollutant transfers made during the 2003-2009 regulatory period
(73 FR 78687). The proposed regulatory text accounted for the inter-
pollutant transfers discussed above. The increase in HCFC-22 baseline
allowances for Arkema, Inc. and Solvay Fluorides, LLC presented in the
2008 Proposed Rule resulted in a larger amount of HCFC-22 baseline
allowances overall and therefore a lower percentage of HCFC-22
baselines allocated across the board in each control period.
Specifically, the proposed shift resulted in a 16 percent decrease in
allocation share for all other HCFC-22 allowance holders, and increases
for the petitioners: Arkema and Solvay. For more detail on the effect
of these transfers, see section III.C. of this preamble.
In the 2009 Final Rule, after considering comments, EPA determined
that allowing inter-pollutant transfers from one regulatory period to
become a part of the baseline in the next regulatory period could
undermine the Agency's chemical-by-chemical phaseout approach and could
encourage market manipulation. EPA also concluded that section 607 of
the CAA was best read as limiting inter-pollutant transfers to those
conducted on an annual basis. For these reasons, EPA did not take the
2008 inter-pollutant transfers into account in establishing the
baselines for the 2009 Final Rule covering 2010-2014.
The Court issued a decision on August 27, 2010, agreeing with
petitioners that ``the [2009] Final Rule unacceptably alters
transactions the EPA approved under the 2003 Rule'' (Arkema v. EPA, 618
F.3d at 3). The Court vacated the rule in part, ``insofar as it
operates retroactively,'' and remanded to EPA ``for prompt
resolution,'' (618 F.3d at 10). The Court withheld the mandate for the
decision pending the disposition of any petition for rehearing. On
November 12, 2010, EPA filed a petition for rehearing, which was denied
on January 21, 2011. The mandate issued on February 4, 2011.
Because the Court vacated the rule only in part, without specifying
which part or parts were vacated, EPA may adopt a reasonable
interpretation of the vacatur's extent. In doing so, EPA is relying on
its expertise in administering the HCFC phaseout regulations under
Title VI of the CAA. First, EPA notes that the rule contains elements
that were not at issue in the litigation. EPA concludes that the
vacatur has no effect on allowances for any substances other than HCFC-
142b and HCFC-22, since the petitioners' claims and the opinion itself
discuss only those two substances. Similarly, EPA concludes that other
discrete portions of the rule, such as the
[[Page 243]]
provisions on use and introduction into interstate commerce, are
unaffected by the vacatur.
The baselines for HCFC-142b and HCFC-22 were clearly at issue in
the litigation and indeed are the focus of the Court's opinion. The
Court found that ``the Agency's refusal to account for the Petitioners'
baseline transfers of inter-pollutant allowances in the Final Rule is
impermissibly retroactive,'' (618 F.3d at 9). Because baseline and
calendar year allowances are inextricably linked,\4\ EPA has determined
that the Court's vacatur voided the HCFC-22 and HCFC-142b baselines in
40 CFR 82.17 and 82.19 as well as the percentage of baseline allocated
for those specific substances in 40 CFR 82.16 for all companies listed
in those sections.\5\ This means that until EPA establishes new
baselines and allocates new calendar-year allowances, production and
import of these two substances is prohibited under 40 CFR 82.15.
Recognizing this scenario, on January 28, 2011, EPA sent letters to
affected stakeholders informing them that the Agency would exercise
enforcement discretion for a limited period provided their production
and import did not exceed specified levels and provided that they
adhered to additional conditions.
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\4\ The reason baseline and calendar-year allocations are
inextricable is because calendar-year allocations are expressed as a
percentage of baseline, and the percentage of baseline allocated for
a specific substance varies depending on the sum of all company
baselines for that substance. The process works as follows for each
specific HCFC: First, all the company-specific baselines listed in
the tables at 40 CFR 82.17 and 82.19 are added to determine the
aggregate amount of baseline production and consumption,
respectively. Second, EPA determines how many consumption allowances
the market needs for a given year, taking into account recycled,
reused, and reclaimed material, and divides that amount by the
aggregate amount of baseline allowances. The resulting percentage
listed in the table at section 82.16 becomes what each company is
allowed to consume in a given control period. For example, a company
with 100,000 kg of HCFC-22 baseline allowances would multiply that
number by the percentage allowed for 2011 (for example, 32 percent)
to determine its calendar-year allowance is 32,000 kg. Historically
and in this proposed rule, EPA has allocated the same percentage of
baseline allowances for production as it does for consumption.
\5\ The companies' allocations are inter-related because, as
noted in footnote 4, the percentage of baseline allocated varies
according to the sum of the company-specific baselines.
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In determining the meaning of the Court's vacatur, EPA considered
whether this interpretation was consistent with what the Court intended
and a good fit for the specific circumstances, which include the goals
and design of the HCFC allowance program and the basic structure of the
2009 Final Rule. While this interpretation is appropriate in this
instance, it is possible that another interpretation would be more
appropriate in a case involving a program with different goals, design,
or structure.
EPA's initial response to the Court's partial vacatur was to issue
the 2011 Interim Final Rule (76 FR 47451). Through today's notice, EPA
is proposing a way to address the Court's decision as it relates to the
remainder of the regulatory period ending December 31, 2014. In
addition, the Agency is taking comment on whether the vacatur and
remand should be interpreted as applying to the 2010 allocations, and
if so, how allowances might be adjusted to reflect this. See section
III.B.4. for EPA's proposed approach to address 2010 allowances.
E. Comments Relevant to Recovery and Reclamation Issues in This
Rulemaking Submitted in Response to the 2011 Interim Final Rule
Allocating HCFC Allowances
The EPA received 15 submissions from 13 commenters in response to
the 2011 interim final rule. Three comments were received late.
Specifically, the Agency had asked for comment on several issues
relevant to HCFC-22 supply and the status of recovery and reclamation,
including: (1) Previous estimates of HCFC-22 demand; (2) the amount of
virgin HCFC-22 currently in inventory, available for reuse and/or
waiting for import from abroad; and (3) whether there is an overall
surplus of the gas. The Agency received comments directly answering
these questions, along with other comments that are of relevance to
this proposed rulemaking.
EPA is not providing a complete response to comments on the 2011
interim final rule in this preamble; however, EPA is acknowledging the
most relevant comments here in order to highlight certain stakeholder
concerns regarding the future implementation of the HCFC phaseout
program. It is the Agency's responsibility to implement Title VI of the
CAA, and its policy objective is to do so in a way that smoothly
transitions the U.S. away from HCFCs to non-ODS alternatives.
Therefore, EPA is particularly interested in stakeholder input
regarding the status of HCFC-22 recovery and reclamation, because this
information applies directly to previously-stated policy goals. This
section notes the following three issues discussed in comments to the
2011 Interim Final Rule.
1. Supply of HCFC-22
a. Economic feasibility of reclamation.
b. Economic incentives for recovery and emissions prevention.
c. Effect of virgin gas supplies on dry-shipped condensing units.
2. Providing Allowances to Reclaimers
3. Providing Allowances to Manufacturers of HCFC Blends
1. Supply of HCFC-22
Nine commenters submitted comments requesting that EPA decrease
consumption allowances for 2012-2014. Another company also supported
such a decrease, as long as updated market conditions indicate there is
a need to do so and all allowance holders are affected proportionally.
Commenters suggested that excess supply was due to several factors.
Additionally, commenters stated the price of HCFC-22 is low, indicating
that virgin supplies are not constrained to the extent that the Agency
had anticipated. Some commenters pointed to the unused consumption
allowances for 2010 as evidence of over-supply and the need for
decreasing the total number of consumption allowances.
(a) Economic feasibility of reclamation: Most commenters, many of
whom are reclaimers, are concerned about the excess supply and low
price of virgin HCFC-22 because this situation makes reclaim
financially unfeasible. EPA understands that reclaimers can stay in
business only if reclaimed gas can be profitably sold for a price that
does not exceed the price of virgin gas, and the price of virgin gas
will increase only when the supply has contracted. The Agency promotes
reclamation via separation and distillation, which requires very little
virgin gas, and recognizes that reclaiming without significant blending
further increases the costs of reclamation.
(b) Economic incentives for recovery and emissions prevention:
Commenters also pointed out that the excess supply and low price of
HCFC-22 do not incentivize recovery in general, and likely promote
venting and poor maintenance practices. EPA agrees that if the gas is
not valuable then there will be little incentive to reuse it or
proactively prevent leaks, in addition to increasing the likelihood of
venting (which is illegal under section 608 of the CAA).
(c) Effect of virgin gas supplies on dry-shipped condensing units:
Two commenters also specifically mention the increased popularity in
dry-shipped condensing units that are eventually charged with HCFC-22
as a symptom of this over-supply. The Agency recognizes that the
majority of commenters believe that there is an excess of HCFC-22 on
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the market, which has direct negative consequence for reclaim and
recovery, and thus overall ODS emissions. Additionally, EPA has
received a petition (included in the docket) from the Carrier
Corporation, dated February 3, 2011, concerning dry-shipped HCFC-22
condensing units. EPA is taking comment on whether the installation of
dry-shipped HCFC-22 condensing units will affect the phaseout of virgin
HCFC-22 production and import.
EPA undertook an analysis to gauge whether there is a surplus of
HCFC-22 and, if so, how large the surplus is. A memo in the docket for
this rulemaking details EPA's analysis of the HCFC-22 market. The
results indicate EPA should consider allocating between 11 to 47
percent less per year between 2012 and 2014 relative to the amounts
that appeared in the 2009 Final Rule. Consequently, EPA is proposing in
this rulemaking to allocate fewer HCFC-22 consumption allowances than
contemplated in the 2009 Final Rule for 2012-2014 in order to promote
recovery and reclamation and encourage transition to non-ODS
alternatives (see section III.B. and III.C.). As stated in the 2009
Final Rule, ``The Agency strongly encourages increased recovery and
either recycling or reclamation of HCFC-22 * * * Recovery becomes even
more important in light of the 2015 Montreal Protocol phasedown step,
when the U.S. HCFC consumption cap is reduced from 3,810 ODP-weighted
metric tons to 1,524 ODP-weighted metric tons,'' (74 FR 66422).
2. Providing Allowances to Reclaimers
Two commenters requested that EPA provide HCFC allowances to
certified reclaimers. As explained in the report titled ``Analysis of
Equipment and Practices in the Reclamation Industry,'' which is
included in the docket for this rulemaking, ``refrigerant reclamation
refers to the reprocessing and upgrading of recovered refrigerant
through such mechanisms as filtering, drying, distillation and chemical
treatment in order to restore the substance to specifications outlined
in the Air-Conditioning, Heating, and Refrigeration Institute (AHRI)'s
Standard 700-1995.'' The commenters argue increasing allocations to
reclaimers would increase the amount of reclaimed HCFCs available for
purchase. The comments are similar to those submitted prior to the
finalization of the 2009 Final Rule, which allocated HCFC allowances
for 2010-2014. EPA responded to this request at the time (74 FR 66422;
Response to Comments document for the 2008 NPRM), but discusses the
issue further here.
The Agency's primary concern is that providing reclaimers with
allowances could foster unsustainable reclamation practices that rely
on blending instead of investing in the technology to fully reclaim
HCFCs. Based on the phaseout schedule and the decrease in annual
allocations, reclamation through separation and distillation will be
more important in 2015 when the HCFC-22 allocation must drop by at
least 45 percent from 2010 levels and absolutely necessary by 2020, by
which time import and production of HCFC-22 must be phased out
entirely. In addition, many businesses have either found a way to
secure reliable access to virgin HCFCs or have made investments to
reclaim HCFCs in a sustainable way, without a direct allocation of
allowances.
EPA is also concerned that providing allowances to reclaimers does
not address the key structural issue that the industry and the HCFC
transition are facing: The price of HCFC-22 is too low to foster
reclamation and is not sending the necessary signal to move consumers
to non-ODS alternatives. While providing allowances to reclaimers would
likely decrease the cost to recover and reclaim HCFCs, EPA is concerned
about what effect providing allowances to reclaimers would have on the
market price of HCFC-22. EPA is seeking comment on whether providing
allowances to reclaimers would affect the market price of HCFC-22, and
what effect that price change would have on the transition away from
ODS and the sustainability of the reclamation industry.
EPA continues to believe that allocating fewer allowances is the
best way to foster reclamation and recovery. Thus, this proposal does
not include an allocation for reclaimers. However, the Agency has
included the relevant comments on the Interim Final Rule in the docket
for this rulemaking and welcomes further comment on this issue from all
interested parties.
3. Providing Allowances to Manufacturers of HCFC Blends
One small business has informed EPA that it cannot acquire either
HCFC allowances or the HCFCs it needs to manufacture its HCFC blend
(see the letters from ICOR dated May 17, 2011 and September 6, 2011).
The company asserts that the cap and trade system is in practice ``cap
and no trade,'' where companies hold onto their allowances, even if
they have no intention of using them. The commenter argues that this
leads to artificially high prices for HCFCs and HCFC allowances. To
remedy this situation, the commenter requests that EPA take unused
allowances and provide those allowances to companies that either
purchased HCFCs or HCFC consumption allowances in 2008 and 2009. EPA
notes that the inability to acquire allowances and/or HCFCs themselves
does not appear to be a widespread problem, as numerous companies have
made a significant number of transfers over the last year alone, and no
other company has indicated it cannot acquire HCFCs. However, EPA is
taking comment on whether other companies are having difficulty
acquiring HCFCs or HCFC allowances.
Some historical background may help to provide context on how EPA
provided flexibility for small businesses when establishing the HCFC
allocation system. In the 2003 Final Rule, published January 21, 2003,
EPA assigned individual company baselines by considering the highest
production and consumption years for every company between the years
1994-1997--a four year period preceding regulation of the production
and import of HCFCs. ``Consumption'' is defined by the Clean Air Act as
``the amount of that substance produced in the United States, plus the
amount imported, minus the amount exported,'' (42 U.S.C. 7671). A
company had to be manufacturing or importing HCFCs at that time in
order to be assigned a baseline. In addition, the EPA provided an
exception allowing new entrants provided that they began importing
after the end of 1997, but before April 5, 1999, the date the EPA
published the advanced notice of proposed rulemaking for the regulatory
period 2003-2009. The Agency believed that such small businesses might
not have been aware of the impending rulemaking that would affect their
ability to continue in the HCFC market.
In addition to the exception for late entrants made in the 2003
Final Rule, there is significant flexibility in the types of transfers
companies can conduct. Companies can transfer allowances between
companies and, on a temporary basis, between chemicals. A guidance
memo, titled ``Flexibility in the HCFC Allowance System,'' describing
this flexibility further is available in the docket and on EPA's Web
site. Companies can also purchase HCFCs at the wholesale price, which,
according to comments on the 2011 Interim Final Rule, has been
decreasing. The allocation system in part was established to discourage
the use of HCFCs and companies' continuation in the HCFC market. As
stated in the 2003 Final Rule, ``businesses that desired an
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allocation of HCFC allowances would have known the risks of jumping
into the business at this juncture'' (66 FR 38073). Since that
statement more than nine years ago, access to information and knowledge
of the risks regarding entering or continuing in the HCFC market have
only increased. Furthermore, new entrants have entered the market by
purchasing consumption allowances, as EPA predicted they could back in
2003. All entities wishing to enter the HCFC import or production
market can continue to purchase allowances for HCFCs.
As the market continues to decrease in size, EPA does not believe
that expanding the pool of allowance holders is necessary to prevent
disruption of the continued servicing of existing equipment. EPA
explored several options that would have expanded the number of
allowance holders in the 2008 NPRM (73 FR 78867) and determined the
current approach with adjustment for transfers of baseline allowances
was appropriate (74 FR 66419; Response to Comments for the 2008 NPRM).
Given EPA's intent to phase down, and ultimately phase out, the use of
HCFCs, consistent with the requirements of the CAA and obligations
under the Montreal Protocol, EPA believes it is justified in continuing
to allocate only to those entities who participated in the market at
the initial stages, as well as those that have entered the market by
purchasing HCFC baseline allowances in accordance with the established
practices. EPA does not believe that providing allowances to companies
that were not importing or producing HCFCs prior to EPA regulation is
appropriate at this time given the disruption it would create to the
existing regulatory framework. However, in light of the large number of
HCFC allowances that were not used in 2010 and the difficulty at least
one company is having in getting HCFCs, EPA welcomes comments on
whether an allocation to manufacturers of HCFC blends who are having
difficulty acquiring HCFCs or HCFC allowances would be appropriate.
Commenters supporting such an allocation should consider (1) how EPA
might determine the total amount of such an allocation, (2) how EPA
might determine which companies should receive allowances, (3) how EPA
would verify that allowance holders are refusing to sell HCFCs and HCFC
allowances, (4) how EPA might set baselines for these companies, (5)
whether EPA should provide allowances in addition to the amount
proposed in this rule, or as part of the amount proposed in this rule,
and (6) how providing allowances to an additional set of companies
would affect the U.S. transition away from HCFCs.
III. How does EPA propose to allocate HCFC-22 and HCFC-142b allowances
for 2012-2014?
EPA is proposing to continue the system established in previous
rulemakings (68 FR 2820, 74 FR 66412, 76 FR 47451) to address HCFC
production and import in the U.S. The process works as follows for each
specific HCFC: First, all the company-specific baselines listed in the
tables at 40 CFR 82.17 and 82.19 are added to determine the aggregate
amount of baseline production and consumption, respectively. Second,
EPA determines how many consumption allowances the market needs for a
given year, taking into account recycled, reused, and reclaimed
material, and divides that amount by the aggregate amount of baseline
allowances. The resulting percentage listed in the table at section
82.16 becomes what each company is allowed to consume in a given
control period. For example, a company with 100,000 kg of HCFC-22
baseline allowances would multiply that number by the percentage
allowed for the year (for example, 32 percent in 2011) to determine its
calendar-year allowance is 32,000 kg. Historically, EPA has allocated
the same percentage of baseline allowances for production as it does
for consumption.
Specifically, EPA is proposing to (1) establish 2012-2014 company-
by-company consumption and production baselines for HCFC-22 and HCFC-
142b in the tables at 40 CFR 82.17 and 82.19 identical to the baselines
established in the 2011 Interim Final Rule (76 FR 47468), (2) allocate
company-by-company production and consumption allowances for these
substances for 2012-2014 by establishing percentages of production and
consumption baselines in the table at section 82.16 and (3) revise the
regulatory text at 40 CFR 82.23 to make the procedure for all future
inter-pollutant transfers clear. EPA will address the allocations for
the control periods beyond 2014 at a later date. All aspects of the
2009 Final Rule promulgated on December 15, 2009 (74 FR 66412) that are
not addressed in this proposed rule are unchanged.
Additionally, EPA notes that beginning January 1, 2015, section 605
of the CAA prohibits the use and introduction into interstate commerce
of any HCFC unless it ``(1) has been used, recovered and recycled; (2)
is used and entirely consumed (except for trace quantities) in the
production of other chemicals; or (3) is used as a refrigerant in
appliances manufactured prior to January 1, 2020.'' In addition, EPA's
regulations at 40 CFR 82.15 restrict use and introduction into
interstate commerce of HCFC-141b, HCFC-142b, and HCFC-22 beginning in
2010, with limited exceptions. If entities will need HCFCs in 2015 and
beyond for uses other than the exemptions contained in section 605,
they should contact EPA prior to 2013. Entities should understand that
the statutory prohibition in section 605 generally will prevent EPA
from accommodating such needs, with the possible exception of de
minimis quantities.
A. What baselines does EPA propose to use for HCFC-22 and HCFC-142b
allowances?
In the 2009 Final Rule, EPA presented the allocation structure for
HCFC-22 and HCFC-142b for the control periods 2010-2014: Allocating a
percentage of the baseline production and consumption allowances. The
rationale for this system is discussed further at 74 FR 66412. The
Court found no fault with EPA's framework for allocating HCFCs in the
2009 Final Rule, except the aspects of the rule deemed to be
retroactive, i.e., not taking into account inter-pollutant baseline
transfers that occurred in the prior regulatory period in establishing
company-specific baseline allowances. To address this, EPA is proposing
to establish baselines for 2012-2014 identical to the HCFC-22 and HCFC-
142b baselines established in the 2011 Interim Final Rule (76 FR 47451)
that reflect past inter-pollutant baseline transfers deemed permanent
by the Court.
EPA cited several reasons why it would prefer to set baselines
without taking into account inter-pollutant transfers in the 2009 Final
Rule (74 FR 66420), the Response to Comments document included in the
record for that rulemaking, and the 2011 Interim Final Rule (76 FR
47451). However, EPA is recognizing the 2008 transfers in establishing
the baselines through 2014 in accordance with the Court's decision. The
Agency is providing advance notice that for the 2015-2019 regulatory
period, it would consider using more recent production and import data
than the 1994-1997 data used to set baselines for the first time in the
2003 Final Rule. The Agency is particularly interested in stakeholders'
views on whether there w