Protection of Stratospheric Ozone: Adjustments to the Allowance System for Controlling HCFC Production, Import, and Export, 78680-78705 [E8-29965]
Download as PDF
78680
Federal Register / Vol. 73, No. 247 / Tuesday, December 23, 2008 / Proposed Rules
1. Is not a ‘‘significant regulatory
action’’ under Executive Order 12866,
2. Is not a ‘‘significant rule’’ under the
DOT Regulatory Policies and Procedures
(44 FR 11034, February 26, 1979), and
3. Will not have a significant
economic impact, positive or negative,
on a substantial number of small entities
under the criteria of the Regulatory
Flexibility Act.
You can find our regulatory
evaluation and the estimated costs of
compliance in the AD Docket.
List of Subjects in 14 CFR Part 39
Air transportation, Aircraft, Aviation
safety, Safety.
The Proposed Amendment
Accordingly, under the authority
delegated to me by the Administrator,
the FAA proposes to amend 14 CFR part
39 as follows:
PART 39—AIRWORTHINESS
DIRECTIVES
1. The authority citation for part 39
continues to read as follows:
Authority: 49 U.S.C. 106(g), 40113, 44701.
§ 39.13
[Amended]
2. The FAA amends § 39.13 by adding
the following new AD:
McDonnell Douglas: Docket No. FAA–2008–
1324; Directorate Identifier 2008–NM–
101–AD.
Comments Due Date
(a) We must receive comments by February
6, 2009.
Affected ADs
(b) None.
Applicability
(c) This AD applies to all McDonnell
Douglas airplanes identified in Table 1 of this
AD, certificated in any category.
center wing fuel tank becomes empty, and/
or electrical arc burnthrough, which could
result in a fuel tank fire or explosion.
Compliance
(e) Comply with this AD within the
compliance times specified, unless already
done.
Airplane Flight Manual (AFM) Revision
(f) Within 14 days after the effective date
of this AD, revise the Certificate Limitations
Section of the DC–8 AFM to include the
following procedures that preclude dry
running of fuel pumps and/or electrical arc
burnthrough (This may be done by inserting
a copy of this AD into the AFM):
‘‘During level flight, the applicable
alternate or center wing auxiliary tank boost
pump switch must be placed in the OFF
position no more than 5 minutes after the
auto fill light is continuously illuminated.
DO NOT reset any tripped fuel pump circuit
breakers.’’
Alternative Methods of Compliance
(AMOCs)
(g)(1) The Manager, Los Angeles Aircraft
Certification Office (ACO), FAA, ATTN:
William Bond, Aerospace Engineer,
Propulsion Branch, ANM–140L, FAA, Los
Angeles ACO, 3960 Paramount Boulevard,
Lakewood, California 90712–4137; telephone
(562) 627–5253; fax (562) 627–5210; has the
authority to approve AMOCs for this AD, if
requested using the procedures found in 14
CFR 39.19.
(2) To request a different method of
compliance or a different compliance time
for this AD, follow the procedures in 14 CFR
39.19. Before using any approved AMOC on
any airplane to which the AMOC applies,
notify your appropriate principal inspector
(PI) in the FAA Flight Standards District
Office (FSDO), or lacking a PI, your local
FSDO.
Issued in Renton, Washington, on
December 12, 2008.
Michael J. Kaszycki,
Acting Manager, Transport Airplane
Directorate, Aircraft Certification Service.
[FR Doc. E8–30521 Filed 12–22–08; 8:45 am]
FOR FURTHER INFORMATION CONTACT:
Philip A. Selleck, Regulations Program
Manager, 1849 C St., NW., Washington,
DC 20240 (202) 208–4206; e-mail
philip_selleck@nps.gov.
Correction
In proposed rule FR Doc. E8–29892,
beginning on page 76987 in the issue of
December 18, 2008, make the following
correction to the text of the proposed
rule. On page 76990, in the 2nd column,
add at the end of § 4.30 the following
paragraphs (f) and (g):
§ 4.30
Bicycles.
*
*
*
*
*
(f) A person operating a bicycle is
subject to all sections of this part that
apply to an operator of a motor vehicle,
except §§ 4.4, 4.10, 4.11 and 4.14.
(g) The following are prohibited:
(1) Possessing a bicycle in a
wilderness area established by Federal
statute.
(2) Operating a bicycle during periods
of low visibility, or while traveling
through a tunnel, or between sunset and
sunrise, without exhibiting on the
operator or bicycle a white light or
reflector that is visible from a distance
of at least 500 feet to the front and with
a red light or reflector visible from at
least 200 feet to the rear.
(3) Operating a bicycle abreast of
another bicycle except where authorized
by the superintendent.
(4) Operating a bicycle while
consuming an alcoholic beverage or
carrying in hand an open container of
an alcoholic beverage.
Dated: December 18, 2008.
Lyle Laverty,
Assistant Secretary, Fish and Wildlife and
Parks.
[FR Doc. E8–30649 Filed 12–22–08; 8:45 am]
BILLING CODE 4312–52–P
BILLING CODE 4910–13–P
TABLE 1—APPLICABILITY
DEPARTMENT OF THE INTERIOR
Model
(1) DC–8–51, DC–8–52, DC–8–53, and DC–
8–55 airplanes.
(2) DC–8F–54 and DC–8F–55 airplanes.
(3) DC–8–61, DC–8–62, and DC–8–63 airplanes.
(4) DC–8–61F, DC–8–62F, and DC–8–63F
airplanes.
(5) DC–8–71, DC–8–72, and DC–8–73 airplanes.
(6) DC–8–71F, DC–8–72F, and DC–8–73F
airplanes.
Unsafe Condition
(d) This AD results from fuel system
reviews conducted by the manufacturer. We
are issuing this AD to prevent pump inlet
friction (i.e., overheating or sparking) when
the fuel pumps are continually run as the
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ENVIRONMENTAL PROTECTION
AGENCY
National Park Service
40 CFR Part 82
36 CFR Part 4
[EPA–HQ–OAR–2008–0496; FRL–8752–7]
RIN 1024–AD72
RIN 2060–A076
Vehicles and Traffic Safety
Protection of Stratospheric Ozone:
Adjustments to the Allowance System
for Controlling HCFC Production,
Import, and Export
National Park Service, Interior.
Proposed rule; correction.
AGENCY:
ACTION:
SUMMARY: The National Park Service
published a proposed rule revising 36
CFR 4.30 in the Federal Register on
December 18, 2008, 73 FR 76987,
inadvertently leaving out the last two
paragraphs. This correction restores that
text.
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AGENCY: Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
SUMMARY: EPA is proposing to adjust the
allowance system for control of U.S.
consumption and production of
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hydrochlorofluorocarbons (HCFCs) by
apportioning baselines and allocating
production and consumption
allowances for several HCFCs for which
the Agency previously allocated
allowances and other HCFCs that were
not allocated allowances previously, for
the control periods 2010–2014. The
HCFC allowance system is part of EPA’s
Clean Air Act program to phase out
ozone-depleting substances (ODSs) to
protect the stratospheric ozone layer.
Protection of the stratospheric ozone
layer helps reduce rates of skin cancer
and cataracts, as well as other health
and ecological effects. The U.S. is
obligated under the Montreal Protocol
on Substances that Deplete the Ozone
Layer (Montreal Protocol) to limit HCFC
consumption and production to a
specific level and, using stepwise
reductions, to decrease the specific level
culminating in a complete HCFC
phaseout in 2030. The next major
milestone, to occur on January 1, 2010,
is a 75 percent reduction from the
aggregate U.S. HCFC baseline for
production and consumption. In this
action EPA proposes to allocate the
allowances for 2010–2014 that will
ensure compliance with the
international stepwise reduction,
consistent with the 1990 Clean Air Act
Amendments. In addition, EPA
proposes to amend the regulatory
provisions concerning allowances for
HCFC production for developing
countries’ basic domestic needs to be
consistent with the September 2007
adjustments to the Montreal Protocol.
Also, the Agency is providing its
interpretation of a self-effectuating ban
on introduction into interstate
commerce and use of HCFCs contained
in section 605(a) of the Clean Air Act
and proposes to amend existing
regulatory provisions to facilitate
implementation of the statutory
requirements.
DATES: Comments must be received on
or before February 23, 2009, unless a
public hearing is requested. If a public
hearing is requested, comments must
then be received on or before March 9,
2009. Any party requesting a public
hearing must notify the contact listed
below under FOR FURTHER INFORMATION
CONTACT by 5 p.m. Eastern Daylight
Time on January 2, 2009. If a hearing is
held, it will take place on January 7,
2009 and the comment period will then
close on March 9, 2009.
Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2008–0496, by one of the
following methods:
ADDRESSES:
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• https://www.regulations.gov: Follow
the on-line instructions for submitting
comments.
• E-mail: a-and-r-Docket@epa.gov.
• Fax: 202–566–1741.
• Mail: Docket #, 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–2008–0496 Air and Radiation
Docket at EPA West, 1301 Constitution
Avenue, NW., Room B108, Mail Code
6102T, Washington, DC 20460. 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–2008–
0496. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
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 e-mail. The https://
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 e-mail comment directly
to EPA without going through https://
www.regulations.gov your e-mail
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 https://
www.epa.gov/epahome/dockets.htm.
FOR FURTHER INFORMATION CONTACT:
Cindy Axinn Newberg, EPA,
Stratospheric Protection Division, Office
of Atmospheric Programs, Office of Air
and Radiation (6205J), 1200
PO 00000
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78681
Pennsylvania Avenue, NW.,
Washington, DC 20460, (202) 343–9729,
newberg.cindy@epa.gov.
SUPPLEMENTARY INFORMATION: Under the
Montreal Protocol on Substances that
Deplete the Ozone Layer (Montreal
Protocol), as amended, the U.S. and
other industrialized countries that are
Parties to the Protocol have agreed to
limit production and consumption of
hydrochlorofluorocarbons (HCFCs), and
to phase out production and
consumption in a step-wise fashion over
time, culminating in a general phaseout
by 2020 while permitting a small
amount of HCFC production to continue
solely for servicing existing appliances
until 2030. Title VI of the Clean Air Act
Amendments of 1990 (CAAA of 1990)
also mandates restrictions on HCFCs,
culminating in a complete production
and consumption phaseout in 2030. For
purposes of both the Montreal Protocol
and the Clean Air Act, ‘‘consumption’’
is defined as production plus imports
minus exports. Sections 605 and 606 of
the Clean Air Act authorize EPA to
promulgate regulations to manage the
consumption and production of HCFCs
until the terminal phaseout. In 1993
EPA established a chemical-bychemical, ‘‘worst-first,’’ approach to
implement the Montreal Protocol’s
graduated phaseout in overall HCFC
levels (58 FR 65018). Key concepts in
the ‘‘worst-first’’ approach included
‘‘distinguishing among HCFCs based on
their [ozone depletion potential (ODP)]
and phasing out use in new equipment
prior to use for servicing existing
equipment’’ (58 FR 65026). The
consumption cap became effective in
1996, and HCFC consumption in the
U.S. remained about 15 percent below
the cap for the first two years. In 1998
and 1999, consumption rose to levels
that approached the cap. On January 21,
2003, EPA established an allowance
tracking system for HCFCs (68 FR 2820),
noting at that time that EPA would
again pursue a notice-and-comment
rulemaking to implement a 2010
stepwise reduction. EPA promulgated
minor amendments to these regulations
on June 17, 2004 (69 FR 34024), and
July 20, 2006 (71 FR 41163).
In this action, EPA proposes the next
step in the chemical-by-chemical
phaseout the United States uses to meet
its international obligations.
Specifically, EPA proposes for HCFC–
141b, HCFC–22, and HCFC–142b, to
grant specified percentages of the
consumption and production baselines
for the control periods 2010–2014; and
for other HCFCs to apportion companyby-company consumption and
production baselines as well as grant
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Federal Register / Vol. 73, No. 247 / Tuesday, December 23, 2008 / Proposed Rules
specified percentages of the
consumption and production baselines
for the control periods 2010–2014. EPA
is also proposing to amend the
provisions for HCFC production
allowances to meet the basic domestic
needs of developing countries. In
addition, EPA is proposing regulatory
changes to complete the implementation
of the section 605(a) ban on
introduction into interstate commerce or
use of HCFCs and clarifies its
interpretation of this Clean Air Act
provision.
Abbreviations and Acronyms Used in
this Document
CAA—Clean Air Act
CAAA—Clean Air Act Amendments of
1990
CFC—chlorofluorocarbon
EPA—Environmental Protection Agency
HCFC—hydrochlorofluorocarbon
Montreal Protocol—Montreal Protocol
on Substances that Deplete the Ozone
Layer
NPRM—Notice of Proposed Rulemaking
ODP—ozone depletion potential
ODS—ozone-depleting substance
Party—States and regional economic
integration organizations that have
consented to be bound by the
Montreal Protocol on Substances that
Deplete the Ozone Layer
SNAP—Significant New Alternatives
Policy
UNEP—United Nations Environment
Programme
Tips for Preparing Your Comments
When submitting comments,
remember to:
• Identify the rulemaking by docket
number and other identifying
information (subject heading, Federal
Register date and page number).
Category
• 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;
suggest alternatives and substitute
language for your requested changes.
• Describe any assumptions and
provide any technical information and/
or data that you used.
• 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.
Table of Contents
I. Regulated Entities
II. Background
A. How Do the Montreal Protocol and
Clean Air Act Phase Out HCFCs?
B. What Sections of the Clean Air Act
Apply to This Rulemaking?
III. This Proposal
A. How Does EPA Propose to Issue
Production and Consumption
Allowances for 2010–2014?
1. What Actions Did EPA Take in the 2003
Allocation Rule?
2. How Will EPA Allocate 2010–2014
Allowances for HCFC–22 and HCFC–
142b?
3. How Should EPA Consider Servicing
Needs for Existing Equipment?
4. How Will the Allocated Allowances
Appear in the Regulations?
NAICS code
SIC code
Chlorofluorocarbon gas manufacturing.
Chlorofluorocarbon gas importers ...
325120
2869
325120
2869
Chlorofluorocarbon gas exporters ...
325120
2869
Manufacturers of air conditioners
and refrigerators.
Importers of air conditioners and refrigerators.
333415
........................
333415
3585
This table is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
regulated by this action. This table lists
the types of entities that EPA is now
aware potentially could be regulated by
this action. Other types of entities not
listed in this table could also be
affected. To determine whether your
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I. Regulated Entities
These proposed amendments will
affect the following categories:
Examples of regulated entities
Chlorodifluoromethane manufacturers; Dichlorofluoroethane
turers; Chlorodifluoroethane manufacturers.
Chlorodifluoromethane importers; Dichlorofluoroethane
Chlorodifluoroethane importers.
Chlorodifluoromethane exporters; Dichlorofluoroethane
Chlorodifluoroethane exporters.
Air-Conditioning Equipment and Commercial and Industrial
tion Equipment manufacturers.
Air-Conditioning Equipment and Commercial and Industrial
tion Equipment importers.
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.
PO 00000
5. What Other Methods Could Be Used to
Determine the Allocation for HCFC–22
and HCFC–142b Allowances?
6. How Important Is HCFC–22 in
Determining the Allocation of
Allowances?
7. HCFC–22 Allowances for 2010–2014
8. HCFC–142b Allowances for 2010–2014
9. How Does the Aggregate for HCFC–22
and HCFC–142b Translate to Entity-byEntity?
10. Baselines for HCFC–123, HCFC–124,
HCFC–225ca, and HCFC–225cb
11. What Percentage of the Baseline Will
EPA Allocate for HCFC–123, HCFC–124,
HCFC–225ca, and HCFC–225cb for the
Control Periods 2010–2014?
12. What About Other HCFCs?
B. Does the Article 5 Allowance Provision
Change Given the Adjustments to the
Montreal Protocol?
C. How Does EPA Interpret ‘‘Introduce into
Interstate Commerce or Use?’’
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and 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
Advancement Act
J. Executive Order 12898: Federal Actions
to Address Environmental Justice in
Minority Populations and Low-Income
Populations
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manufacimporters;
exporters;
RefrigeraRefrigera-
II. Background
A. How Do the Montreal Protocol and
Clean Air Act 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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stratospheric ozone-depleting
substances. 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 of
1990), which included Title VI on
Stratospheric Ozone Protection, codified
as 42 U.S.C. Chapter 85, Subchapter VI,
to ensure that the United States could
satisfy its obligations under the
Montreal Protocol. Title VI includes
restrictions on production,
consumption, and use of ozonedepleting substances 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. Both the
Montreal Protocol and the Clean Air Act
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-ODP substitutes for
CFCs and other ODSs. 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 industrialized (Article 2) Parties, a
schedule to which the United States
adheres. The consumption cap for each
Article 2 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, 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
the 2007 adjustment, the schedule
called for a 35 percent reduction of the
consumption cap in 2004, followed by
a 65 percent reduction in 2010, a 90
percent reduction in 2015, a 99.5
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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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,
however, the Parties created a cap on
production for Article 2 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 metric tons, effective
January 1, 2004. This became the U.S.
production baseline for 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 that 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).
EPA explained that its action modified
the schedule contained in paragraphs (a)
and (b) of section 605 (58 FR 65025).
Paragraph (a) addresses use and
introduction into interstate commerce,
while paragraph (b) addresses
production.
On January 21, 2003 (68 FR 2820),
EPA promulgated regulations to ensure
compliance with the first 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 that rule
EPA established chemical-specific
consumption and production baselines
for HCFC–141b, HCFC–22, and HCFC–
142b. To further carry out the 1993
phaseout schedule, EPA issued
calendar-year allowances equal to 100
percent of baseline for HCFC–22 and
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HCFC–142b for each control period 2
from 2003 through 2009. For those same
control periods EPA issued calendaryear allowances equal to zero for HCFC–
141b; under the 1993 rule HCFC–141b
was subject to a complete phaseout on
January 1, 2003, which allowed the
United States to meet and exceed the
2004 stepwise reduction of 35 percent
below the baseline for all HCFCs. EPA
did, however, create a petition process
to allow applicants to request very small
amounts of HCFC–141b beyond the
phaseout. EPA considered establishing
baselines for all HCFCs in that rule but
deferred such action for all but HCFC–
141b, HCFC–142b, and HCFC–22. These
regulations were amended with a
technical correction on July 16, 2003 (68
FR 41925), and with direct final rules
adopting minor amendments on June
17, 2004 (69 FR 34024) and July 20,
2006 (71 FR 41163).
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, 2008.3
As a result of the 2007 Montreal
Adjustment (reflected in Decision XIX/
6), the United States and other
industrialized countries are obligated to
reduce HCFC production and
consumption 75 percent below the
established baseline by 2010, rather
than 65 percent as was the previous
requirement. The other milestones
remain the same: 90 percent below the
baseline by 2015, and 99.5 percent
below the baseline by 2020—allowing,
during 2020 to 2030, production and
consumption at only 0.5 percent of
baseline solely for servicing existing airconditioning and refrigeration
equipment. The adjustment also
resulted in a phaseout schedule for
HCFC production that parallels the
consumption phaseout schedule. All
production and consumption for Article
2 Parties is phased out by 2030.
Decision XIX/6 also adjusted the
provisions for Parties operating under
2 A control period, as defined at 40 CFR 82.3, is
a twelve-month period from January 1 through
December 31.
3 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 become binding for all Parties on May 14,
2008.
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paragraph 1 of Article 5 (developing
countries): (1) To set production and
consumption baselines based on the
average 2009–2010 production and
consumption, respectively; (2) to freeze
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 airconditioning and refrigeration
equipment. All production and
consumption for Article 5 Parties is
phased out by 2040.
In addition, Decision XIX/6 adjusted
Article 2F to allow industrialized
countries to produce ‘‘up to 10 percent
of baseline levels’’ for export to Article
5 countries ‘‘in order to satisfy basic
domestic needs’’ until 2020.4 Paragraph
4 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
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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 industrialized 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. What Sections of the Clean Air Act
Apply to This Rulemaking?
Several sections of the Clean Air Act
apply to this proposed rulemaking.
Section 605 of the Clean Air Act phases
out production and consumption and
restricts the use of HCFCs in accordance
with the schedule set forth in that
section. Section 606 provides for
acceleration of the schedule in section
605 based on a determination by EPA
regarding current scientific information
or the availability of substitutes, or to
conform to any acceleration under the
Montreal Protocol. EPA has previously
accelerated the section 605 schedule
through a rulemaking published
December 10, 1993 (58 FR 65018).
Though this action, EPA is further
accelerating the section 605 HCFC
production and consumption phaseouts.
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
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.’’
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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. EPA believes that in this
instance, all three criteria have been
met.
The first criterion allows the
Administrator, based on an assessment
of credible current scientific
information, to determine that a more
stringent schedule may be necessary to
protect human health. The recent
scientific findings by the Montreal
Protocol’s Science Assessment Panel,
Science Assessment of Ozone Depletion:
2006, available in the docket for this
rulemaking, were initially presented to
the Parties to the Montreal Protocol in
October 2006 at the 18th Meeting of the
Parties in New Delhi, India. The
Assessment was published in March
2007, and hard copies were available to
the Parties in advance of the 26th OpenEnded Working Group Meeting held in
June 2007 in Nairobi, Kenya. The
assessment report shows that
notwithstanding the evidence of a
healing of the ozone layer, there
continue to be human health and
environmental effects associated with
ozone depletion and that recovery
continues to rely on a successful total
global phaseout of ODSs. The report
includes scenarios where additional
actions taken by the Parties would result
in a faster recovery. While these specific
scenarios (including complete phaseout
by the end of that calendar year) were
not all necessarily deemed to be
practical, they demonstrated to the
Parties what could be achieved with
additional actions and contributed in
part to the willingness of many Parties,
including the United States, to consider
the adjustments to the Montreal
Protocol’s HCFC phaseout schedule that
were successfully negotiated in
September 2007. EPA published a
notice of data availability (72 FR 35230)
concerning the potential changes in
HCFC consumption from proposed
adjustments to the Montreal Protocol
submitted by the United States for
consideration at the 19th Meeting of the
Parties held in Montreal September
2007. The data made available through
that notice were specific to the United
States’ proposal but had general
applicability to the other five proposals
submitted by various Parties to the
Protocol and to what was ultimately
agreed to by the Parties at the 19th
Meeting.
Reductions in stratospheric ozone
levels lead to higher levels of ultraviolet
radiation reaching the Earth’s surface,
and a higher risk of negative health
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effects. According to the American
Cancer Society, one in five Americans
will develop skin cancer in their
lifetime, and one American dies every
hour from this disease. While medical
research continues to improve the
understanding of the causes and effects
of skin cancer, many health and
education groups are working to reduce
the incidence of this disease. EPA
believes the recent scientific findings on
stratospheric ozone depletion, together
with the well-established relationship
between ozone depletion and increased
risk of human health effects, support a
determination that a more stringent
HCFC phaseout schedule may be
necessary to protect against such effects.
The second criterion allows the
Administrator to determine a more
stringent schedule is practicable based
on the availability of substitutes for
ODS, taking into account technological
achievability, safety, and other relevant
factors. Since the establishment of the
domestic chemical-by-chemical
phaseout in the United States, advances
by industry have resulted in the
availability of substitutes for a large
variety of end-use applications. Under
section 612 of the CAA, EPA’s
Significant New Alternatives Policy
(SNAP) program evaluates and lists
alternatives for ODSs that reduce overall
risk to human health and the
environment and are currently or
potentially available. Alternatives
include chemical replacements, product
substitutes, and alternative
technologies. The SNAP program has
reviewed approximately 450
combinations of alternatives and end
uses to date. EPA makes information
available concerning potential
alternatives for various end-use
applications. Suitable alternatives—in
many cases, multiple suitable
alternatives—are available for all enduse applications for the HCFCs
considered in this action. The SNAP
program has reviewed substitutes for the
following industrial sectors:
• Refrigeration & Air Conditioning.
• Foam Blowing Agents.
• Cleaning Solvents.
• Fire Suppression and Explosion
Protection.
• Aerosols.
• Sterilants.
• Tobacco Expansion.
• Adhesives, Coatings & Inks.
HCFCs have been used in almost all
of these industrial sectors. For example,
within the air conditioning and
refrigeration industrial sector, end uses
where HCFCs have been used include
chillers, industrial process refrigeration
systems, ice skating rinks, cold storage
warehouses, refrigerated transport, retail
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food refrigeration, household
appliances, and residential and light
commercial air conditioning and heat
pumps. The SNAP program lists
substitutes for each of the end uses. (For
a complete list of substitutes the reader
is directed to: https://www.epa.gov/
ozone/snap/lists/.) EPA
believes that given the availability of
substitutes, a more stringent HCFC
phaseout schedule now is practicable.
The last criterion is that the Montreal
Protocol be modified to include a
schedule to control or reduce
production, consumption, or use of any
substance more rapidly than section 605
would dictate. The United States
submitted a proposal to adjust the
Montreal Protocol in March 2007 to
accelerate the phaseout of HCFCs. This
was one of six proposals considered by
the Parties at their 19th Meeting. Due to
the efforts of the United States and
others, the Parties agreed to adjustments
that result in a more aggressive phaseout
schedule for both developed and
developing countries. Therefore, this
third criterion has been met. Through
this action, EPA is proposing to
incorporate a schedule that reflects the
2007 Montreal Adjustment in its
regulations. In order to meet the 2010
stepdown, EPA is proposing to allocate
HCFC allowances for the years 2010
through 2014 at a level that will ensure
the aggregate HCFC production and
consumption will not exceed 25 percent
of the U.S. baselines.
While section 606 is sufficient
authority for this acceleration of the
section 605 phaseout schedule, EPA
also notes that section 614(b) of the
Clean Air Act provides that in the case
of a conflict between the Act and the
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
Protocol.
In addition to implementing the 2007
Montreal Adjustment, today’s proposed
rule would also address provisions in
section 605 of the Clean Air Act that
relate to use and introduction intro
interstate commerce of class II
substances. In today’s action, EPA is
proposing to complete its
implementation (begun in 1993) of the
section 605 provisions on use of class II
substances. EPA is also proposing
regulatory language to reflect the section
605 provisions on introduction into
interstate commerce of class II
substances. EPA previously addressed
the provisions concerning use of class II
substances in a 1993 rulemaking that
accelerated the phaseout schedule for
HCFC–22 and HCFC–142b (58 FR
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78685
15014, 58 FR 65018). The intent of the
1993 rulemaking was to accelerate not
only the production and consumption
schedule, but also the use restrictions
for those two substances. In the March
18, 1993 notice of proposed rulemaking,
EPA stated that the effect of this
acceleration was ‘‘to prohibit the use of
the chemicals (virgin material only) for
any use except as a feedstock or as a
refrigerant in existing equipment as of
January 1, 2010’’ (58 FR 15028). EPA
noted in the December 10, 1993 notice
of final rulemaking that ‘‘HCFC
restrictions and the approach included
in today’s final rule have not changed
from those proposed by the Agency in
March’’ (58 FR 65028). The regulatory
prohibitions included with that notice,
however, did not control use directly,
but instead banned production and
import for most uses. In today’s action,
EPA is proposing to add the direct use
prohibitions contemplated in the 1993
rule as well as the corresponding
prohibitions on introduction into
interstate commerce. EPA is also
clarifying its interpretation of section
605(a).
III. This Proposal
EPA is proposing to adjust existing
regulations to address the next major
milestone in the HCFC phaseout. As a
Party to the Montreal Protocol, and
having ratified the Montreal Protocol
and all of its amendments, the United
States is required to decrease its amount
of HCFC consumption and production
to 25 percent of the U.S. baseline by
2010. Our domestic chemical-bychemical approach results in differing
schedules for the phaseout of individual
HCFC compounds. EPA believes that
the chemical-by-chemical HCFC
allocation of allowances proposed in
this notice of proposed rulemaking
(NPRM) will ensure that the United
States continues to maintain an overall
HCFC production and consumption
level that is below the 2010 cap
specified by the September 2007
Montreal Adjustment, while at the same
time ensuring that servicing needs
consistent with Section 605(a) of the
Clean Air Act and EPA’s implementing
regulations continue to be met. Thus the
aggregate allowances for all U.S. HCFC
consumption in the years 2010–2014
will not exceed 3,810 ODP-weighted
metric tons (25 percent of the aggregate
U.S. consumption baseline) annually
and the aggregate allowances for all U.S.
HCFC production in the years 2010–
2014 will not exceed 3,884.25 ODPweighted metric tons (25 percent of the
aggregate U.S. production baseline)
annually.
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To meet the 2010 cap for the 2010–
2014 control periods, EPA is proposing
to continue its past practice of
apportioning company-specific
production and consumption baselines
for individual HCFCs, and granting a
certain percent of that baseline as
necessary to achieve compliance with
the cap. For HCFC–141b, HCFC–22, and
HCFC–142b, EPA is proposing to
apportion company-specific baselines in
amounts that are equivalent to those
currently published at § 82.17 (for
production) and § 82.19 (for
consumption), adjusted as necessary to
reflect permanent transfers of baseline
allowances and changes to the names of
entities identified in the tables at § 82.17
and § 82.19. Companies are currently
granted, in § 82.16, 0 percent of baseline
for HCFC–141b and 100 percent of
baseline for HCFC–22 and HCFC–142b.
For 2010–2014, given the previous
phaseout of HCFC–141b, EPA will
continue to allocate zero percent for
HCFC–141b, continuing to allow only
limited amounts of production via an
EPA petition process.5 EPA is proposing
to allocate less than 100 percent of
baseline for HCFC–22 and HCFC–142b
to meet our obligations under the
Montreal Protocol and reflecting the use
restrictions under section 605(a) that are
discussed later in this proposal while
providing for servicing needs consistent
with those restrictions.
EPA is proposing a similar approach
for HCFC–123, HCFC–124, HCFC–
225ca, and HCFC–225cb, which
currently do not have baselines. EPA is
proposing to apportion companyspecific baselines for these HCFCs based
on production and import data available
to the Agency. For control periods
2010–2014, EPA is proposing to grant
125 percent of baseline for these HCFCs.
The allocations described above for
HCFC–22, HCFC–142b, HCFC–123,
HCFC–124, HCFC–225ca, and HCFC–
225cb reflect EPA’s analysis of market
data for these chemicals. The proposed
allocations were developed to allow the
need for virgin material to be met and
to avoid shortages during the affected
control periods, as well as to
accommodate some market growth for
HCFCs–123, –124, –225ca, and –225cb,
for which baselines were not developed
in the 2003 allocation rule. The total
proposed allocation of HCFC allowances
to meet the U.S. need for virgin material
is less than the 3,810 ODP-ton cap. The
differential between the cap and the
total proposed allocation will have the
effect of accommodating minor
5 EPA is not proposing any changes and thus is
not seeking comment with regard to the HCFC–141b
petition process for the 2010–2014 control periods.
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adjustments in the market, particularly
to allow potential market growth for
HCFCs that have not been produced or
imported since 2003 (and which are
therefore not reflected here). In
summary, of the 3,810 ODP tons of
consumption and 3,884.25 ODP tons of
production allowable for the 2010–2014
control periods as established by the
Montreal Protocol, EPA is proposing to
allocate allowances, in aggregate, for
2,920 ODP tons of consumption and
2,646 ODP tons of production.
These proposed allocations represent
77 percent of the consumption cap and
68 percent of the production cap
established by the Montreal Protocol for
2010. EPA seeks comment on whether
the proposed allocations, together with
the amounts assumed to be available
from reclaimed refrigerant, will suffice
to meet HCFC needs for the existing
uses (primarily refrigerant servicing)
that will still be permitted in 2010, as
well as potential adjustments in the
HCFC market. Please provide
information and documentation on
newly emerging uses of HCFCs and
other uses of HCFCs, if any, that are not
accounted for by EPA currently. EPA is
especially interested in information
pertaining to the years 2010 through
2014.
EPA is proposing two other changes
in this proposed rule. First, to reflect the
September 2007 Montreal Adjustments,
EPA is proposing to adjust the amount
of Article 5 allowances for control
periods 2010–2019. Second, EPA is
completing its implementation of the
provisions in section 605 of the Clean
Air Act that relate to use and
introduction into interstate commerce of
class II substances.
EPA is not proposing changes to other
provisions of 40 CFR part 82 subpart A,
such as the recordkeeping and reporting
obligations, the essential use and critical
use provisions, and the HCFC–141b
petition process. EPA is only seeking
comments on the portions of 40 CFR
part 82 subpart A that are specifically
addressed by this proposal.
A. How Does EPA Propose to Issue
Production and Consumption
Allowances for 2010–2014?
In the United States, an allowance is
the unit of measure that controls
production and consumption of ozonedepleting substances. An allowance
represents the privilege granted to a
company to produce or import one
kilogram (not ODP-weighted) of the
specific substance. EPA establishes
company-by-company baselines (also
known as ‘‘baseline allowances’’) and
allocates calendar-year allowances equal
to a percentage of the baseline for
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specified control periods. EPA has
allocated two types of calendar-year
allowances—production allowances and
consumption allowances—for HCFC–22
and HCFC–142b. ‘‘Production
allowance’’ and ‘‘consumption
allowance’’ are defined at 40 CFR 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 trade allowances
for one type of HCFC for allowances of
another type of HCFC, with transactions
weighted according to the ozone
depletion potential of the chemicals
involved. Pursuant to section 607 of the
Clean Air Act, EPA applies an offset to
each HCFC trade by deducting 0.1
percent from the transferor’s allowance
balance. The offset is viewed as a
benefit to 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).
Under current regulations at 40 CFR
82.15(a) and (b), HCFC–22 and HCFC–
142b may not be produced or imported
in excess of the calendar-year
allowances held by the producer or
importer. EPA has not yet allocated any
calendar-year allowances for HCFC–
142b or HCFC–22 to cover the 2010
control period and beyond. Absent a
grant of calendar-year allowances for
these HCFCs, § 82.15 would prohibit
their production and import after
December 31, 2009. EPA intends to
avoid that result by issuing a final rule
in advance of that date that will allocate
calendar-year allowances for 2010–
2014.
1. What Actions Did EPA Take in the
2003 Allocation Rule?
In the January 21, 2003, allocation
rule, EPA established baselines for
HCFC–141b, HCFC–22, and HCFC–
142b. Section 601(2) states that EPA
may select ‘‘a representative calendar
year’’ to serve as the baseline for HCFCs.
In the 2003 allocation rule, however,
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EPA concluded that because the entities
eligible for allowances had differing
production and import histories, no one
year was representative for all
companies. Therefore, in the 2003
allocation rule 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.
EPA assigned individual production
baseline years in the same manner. EPA
did not consider years after 1997 to
avoid creating an uneven playing field
that would skew allocations to those
companies with ample resources and
good access to information regarding the
impending phaseout. EPA is not
proposing to revisit decisions made in
the 2003 allocation rule, such as the
Agency’s discretion to consider data
from multiple years in establishing a
baseline.
The 2003 allocation 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, with the limited
exception described above, by granting
0 percent of that chemical’s baseline for
production and consumption in the
table at § 82.16. The rule granted 100
percent of baseline for production and
consumption of HCFC–22 and HCFC–
142b. 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 baseline.
Because EPA has allocated the same
amount of allowances every year from
2004 to 2009—with minor changes
reflecting permanent trades of baseline
allowances—and because EPA tracks
the production and consumption of all
HCFCs (including those for which
baselines are not allocated), the Agency
can ascertain that the U.S. will remain
comfortably below the cap through
2009. The January 2003 allocation 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 exact
amount of allowances that would be
needed for HCFC–22 and HCFC–142b,
bearing in mind that other HCFCs
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would also contribute to total HCFC
consumption. EPA stated that it would
likely achieve the 2010 reduction step
by applying a percentage reduction to
the HCFC–22 and HCFC–142b baseline
allowances. EPA has monitored the
market to ascertain servicing needs and
market adjustments in the use of HCFCs,
including HCFCs for which EPA did not
establish baselines in the 2003
allocation rule.
2. How Will EPA Allocate 2010–2014
Allowances for HCFC–22 and HCFC–
142b?
This proposal identifies five primary
options for allocating HCFC–22 and
HCFC–142b allowances for the control
periods 2010–2014: (1) Allocating a
percentage of the baseline allowances
(§§ 82.17 and 82.19) for each HCFC
respectively with or without
considering any permanent baseline
transfers and/or inter-pollutant transfers
that resulted in a different amount of
production or consumption for a
specific HCFC; (2) allocating allowances
based on evaluation of the most recent
three years of production, import, and/
or export data as reported to EPA; (3)
allocating allowances based on
evaluation of past sales of HCFCs by
allowance holders by considering how
the HCFCs were ultimately used (e.g.,
servicing refrigeration or airconditioning, original manufacture of
refrigeration or air-conditioning
equipment, foam blowing); (4) allocating
allowances based on aggregated ODP
tons; or (5) allocating a total amount of
allowances and allowing for purchase
by establishing an auction system.
These options are described in more
detail in section III.A.9 of this preamble.
Each of these five methods offers
advantages and disadvantages for
potential allowance holders which vary
according to whether a particular entity
is predominantly a producer or
importer; whether it currently sells
HCFC–22 and HCFC–142b to original
equipment manufacturers, wholesalers,
retailers, or companies that service
appliances; whether the portion of its
business that is ODS-based is expanding
or contracting as the next major
milestone in the phaseout approaches;
its liquidity; whether it holds both
HCFC–142b and HCFC–22 allowances
and/or engages in inter-pollutant
transfers; and whether it sold HCFCs for
applications that do not lend themselves
to servicing. Without regard to the
practices of individual entities, each of
the potential allocation schemes also
offers advantages and disadvantages
associated with the ease of
implementation and other
administrative burdens. EPA has placed
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78687
in the docket to this NPRM a
memorandum titled ‘‘Draft Regulatory
Options for Allocating HCFC
Allowances after 2009’’ that explores
the advantages and disadvantages of the
various options. In addition to the
memorandum, EPA has also placed in
the docket written correspondence by
entities that also discusses various
options for allocating HCFC allowances.
EPA provided notice of the leading
option for implementing the 2010
milestone in the preamble to the 2003
allocation rule by indicating that EPA
‘‘intends to achieve this reduction step
through notice and comment prior to
2010 and will likely implement the
reduction by simply listing a percent of
baseline allowances to be granted in
§ 82.16 for the years after 2009’’ (68 FR
2823). The Agency said that it would
allocate allowances for HCFC–22 and
HCFC–142b at less than 100 percent of
the respective baselines during the
control periods 2010–2014. EPA
continues to believe that this option is
the most appropriate, but seeks
comment on other options. This
approach offers a transparent design and
provides stability in that it uses a wellvetted baseline. EPA believes this
option also is the least burdensome
because it would not require additional
one-time or periodic reporting
obligations that may be necessary if EPA
were to adopt a different option.
Producers and importers have adapted
to the current HCFC allocation method
and aligned their business activities
around the baselines set forth in the
2003 allocation rule. Currently, EPA
manages a tracking system and issues
calendar-year allowances per control
period to specific entities listed in
§ 82.17 and § 82.19. An option that
utilizes this system would limit
administrative burdens for the Agency
and allowance holders.
In the 2003 allocation rule, EPA did
not forecast the amount of reduction for
HCFC–22 and HCFC–142b that would
be needed to ensure that the United
States stayed sufficiently below the
2010 stepwise reduction, which at the
time was a reduction of 65 percent from
the Montreal Protocol baseline. EPA did
not determine whether it would reduce
the allocations for the two substances by
the same percentage or by different
percentages. Several factors affect
determination of the appropriate
percentage of the HCFC–22 and HCFC–
142b production and consumption
baselines to allocate for 2010–2014.
Factors include the percentage of the
aggregate U.S. production and
consumption caps that other HCFCs
comprise as well as provisions in the
Clean Air Act and implementing
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regulations that include use restrictions
(discussed in section III.C of this
NPRM).
EPA uses information from quarterly,
annual, and other periodic reporting
requirements to monitor consumption,
production, imports, and exports of all
HCFCs. EPA uses this information to
ensure companies’ compliance with
regulatory requirements and to develop
reports that are requested by the Parties
to the Montreal Protocol, including
reports ascertaining U.S. compliance
with the phaseout caps. The information
enables EPA to monitor production and
consumption for all HCFCs, including
HCFCs for which baselines have not yet
been established and for which
allowances have not yet been allocated.
Although EPA’s July 20, 2001,
proposed HCFC allocation rulemaking
would have allocated production and
consumption allowances for all HCFCs,
the January 2003 final rule apportioned
company-specific baselines, and
allocated a specific percentage of
baseline allowances for the 2003–2009
control periods, only for HCFC–141b,
HCFC–22, and HCFC–142b. EPA
applied a ‘‘worst-first’’ approach to
these HCFCs since they are the most
damaging to the stratospheric ozone
layer. The 2003 final rule noted that the
HCFC market was continuing to evolve.
At that time, the market for HCFCs with
lower ODPs did not reflect rapid
expansion and thus it was not necessary
to establish specific baselines by
chemical and issue allowances to ensure
that the United States remained below
its cap. Later in this proposal, EPA
further discusses establishing and
apportioning baselines as well as
allocating calendar-year allowances for
these lower-ODP HCFCs for the control
periods 2010–2014.
3. How Should EPA Consider Servicing
Needs for Existing Equipment?
EPA is proposing to use projected
servicing needs in its determination of
the amounts of HCFC–22 and HCFC–
142b allowances to be allocated for the
2010–2014 control periods. EPA is
focusing on servicing needs because
under section 605(a) of the Clean Air
Act and EPA’s implementing
regulations, nearly all other uses of
these two HCFCs will be banned
effective January 1, 2010. EPA has
previously issued a draft analysis of
servicing demand for the HCFC
appliances in the U.S. refrigeration and
air-conditioning sector projected to be
in service from 2010–2019. The report is
titled The U.S. Phaseout of HCFCs:
Projected Servicing Needs in the U.S.
Air-Conditioning and Refrigeration
Sector (the ‘‘Servicing Tail’’ report). On
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November 4, 2005, EPA published a
notice of data availability (70 FR 67172)
making a draft of the report available for
public review and comment. On
September 29, 2006, EPA held a
stakeholder meeting presenting the
findings of a revision to the Servicing
Tail report along with other important
information regarding the next major
milestones in the HCFC phaseout. EPA
solicited comments on the findings
presented at the meeting. Some
stakeholders, including representatives
of manufacturers, chemical producers,
importers, reclaimers, industry
associations, and environmental
organizations, commented on the
projected amount of HCFCs needed to
service this installed base of equipment
and on the amounts expected to be
available from reclamation.
EPA focused the analysis on airconditioning and refrigeration
appliances because such equipment will
represent 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. EPA also focused
the analysis on HCFC–22 because
HCFC–22 is the predominant HCFC in
the installed base of air-conditioning
and refrigerant equipment for which
servicing in the U.S. will likely
continue. The findings in the Servicing
Tail report have helped to shape EPA’s
views regarding the allocation for the
control periods 2010–2014.
The majority of HCFC–22 equipment
that is projected to be in use from 2010
onward will be air-conditioning
applications, including window units,
packaged terminal units, residential and
commercial unitary air-conditioning,
chillers, dehumidifiers, water and
ground source heat pumps, and nonlight duty mobile air-conditioning in
buses and trains. Approximately 147.5
million units of all such types of HCFC–
22 air-conditioning equipment will be
in use in 2010, decreasing from 2010
levels by about 41 percent by 2015 and
76 percent by 2020. In 2010,
approximately 2.2 million units of
HCFC–22 refrigeration equipment will
be in use, including retail food,
industrial process refrigeration, and
transport refrigeration equipment (but
not including cold storage warehouses).
The installed base of HCFC–22
refrigeration equipment is projected to
decrease from 2010 levels by about 29
percent by 2015 and 51 percent by 2020.
EPA developed these estimates using its
Vintaging Model, a tool for estimating
the annual chemical emissions from
industrial sectors that have historically
used ozone-depleting substances in
their products. Additional information
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on the Vintaging Model is available in
the docket for this rulemaking.
As a result of the September 2007
Montreal Adjustment, in which the
Parties agreed to adjust the stepwise
reduction in 2010 from 65 percent of
baseline to 75 percent of baseline for
non-Article 5 Parties, and recognizing
the overall advances by industry in
transitioning to non-ODS substitutes,
EPA has prepared a draft revised
Servicing Tail report to: (1) Reflect the
75 percent reduction in 2010; (2)
consider more recent production and
consumption data in the United States;
and (3) consider more recent trends in
the air-conditioning and refrigeration
sectors. This revised draft report is
available in the docket for this
rulemaking. EPA is accepting comments
on the analysis and the draft findings
until February 23, 2009 or March 9,
2009 if a hearing regarding this
rulemaking is held.
The Servicing Tail report utilizes
production, import, and export data
reported to the Agency on a quarterly,
annual, and transactional basis, as
required by § 82.24. EPA’s analysis of
the reported data confirms that the
United States is satisfying its obligations
as it phases out ODSs and enables EPA
to consider trends in the HCFC markets
on a chemical-by-chemical basis. EPA
also uses this information to submit an
annual report to the Ozone Secretariat
as requested by the Parties to the
Montreal Protocol.
Using the reported data, the draft
revised Servicing Tail report, and the
comments provided at the September
2006 stakeholder meeting and submitted
in subsequent correspondence (available
in the docket), EPA believes it has
sufficient information to propose
through this action to allocate a
percentage of baseline allowances for
HCFC–22 and for HCFC–142b for
production and consumption for the
control periods 2010–2014 that will
address servicing needs. The specific
percentage of baseline for each of the
affected compounds is discussed below.
EPA requests comments regarding
whether it should consider other
sources of information in addition to the
required reports, the Servicing Tail
report, and stakeholder comments. In
particular, EPA is interested in whether
these sources provide sufficient
information to allow EPA to reasonably
estimate servicing needs for 2010–2014,
especially for HCFC–22, which accounts
for the majority of the market.
4. How Will the Allocated Allowances
Appear in the Regulations?
EPA is proposing to revise two types
of tables in 40 CFR part 82 that together
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specify the production and
consumption allowances available to
allowance holders during specified
control periods. Tables at § 82.17 and
§ 82.19 apportion baseline production
and consumption amounts (also referred
to as baseline production allowances
and baseline consumption allowances),
respectively, to individual companies
for individual HCFCs. Complementing
these tables, the table at § 82.16 lists the
percentage of baseline allocated to
allowance holders for specific control
periods. EPA is proposing to retain this
framework of complementary tables,
revising them to reflect adjustments to
baselines, and to grant percentages of
baselines in a manner that achieves the
2010 phasedown goal.
Currently the table at § 82.16 allocates
zero percent of baseline to HCFC–141b
and 100 percent of baseline to HCFC–22
and HCFC–142b (combined in a single
column) for each control period
spanning 2003–2009. EPA is proposing
to amend the table by including control
periods 2010–2014, by continuing to
allocate zero percent to HCFC–141b,
and by allocating specified percentages
(in separate columns) to HCFC–22,
HCFC–142b, and—as will be discussed
later—other HCFCs.
The proposed percentages for HCFC–
22 and HCFC–142b differ because EPA
projects that the needs will differ for
servicing air-conditioning and
refrigeration appliances during the
2010–2014 control periods. EPA’s
analysis shows that there will be a
significantly greater need for HCFC–22
than for HCFC–142b during the control
periods 2010–2014. Based on the
Servicing Tail report and reporting
information already required by EPA
(which includes inter-pollutant
transfers), the needs for individual
HCFCs are not uniform.
EPA believes that allocating the same
percentage of baseline for HCFC–22 and
HCFC–142b would result in too few
allowances for HCFC–22 and too many
allowances for HCFC–142b.6 While
inter-pollutant transfers in accordance
with § 82.23(b) could continue to be
used as a means to trade allowances for
one HCFC for another, EPA is not
planning to rely on such transfers as a
mechanism for large-scale corrections.
Instead, EPA anticipates that the
continued availability of inter-pollutant
transfers will permit the market to selfcorrect for unforeseen changes in
demand and allow individuals to
consider a range of options for their
6 EPA estimates that to stay below the aggregate
cap while reducing HCFC–22 and HCFC–142b by
equal percentages, the resulting HCFC–22
allowances would equal less than two-thirds of the
projected demand for HCFC–22.
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allowances. EPA seeks to avoid
unnecessary disruptions in the
marketplace. EPA’s goal is to promote a
smooth transition for industry.
EPA requests comments on allocating
different percentages of baseline
production allowances and baseline
consumption allowances for HCFC–22
and HCFC–142b.
5. What Other Methods Could Be Used
to Determine the Allocation for HCFC–
22 and HCFC–142b Allowances?
EPA is proposing 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.
However, EPA can envision other
methods for determining how many
allowances to allocate for the control
periods 2010–2014 for these two
compounds, including allocating the
maximum amount that ensures
compliance under the Montreal Protocol
aggregate 2010 cap without room for
other HCFCs. EPA notes above that
HCFCs other than HCFC–22 and HCFC–
142b are likely to be needed during the
control periods 2010–2014. Thus EPA
favors an approach that includes other
HCFCs, recognizing that for such HCFCs
baselines must be established and
apportioned for each substance, and a
percentage of the baseline must be
allocated for these control periods. EPA
believes it would not be appropriate to
allocate the full 3,810 ODP-weighted
metric tons of consumption and
3,884.25 ODP-weighted metric tons of
production solely to HCFC–22 and
HCFC–142b, given the projected needs
for other HCFCs as discussed in section
III.B.11 of this preamble.
Approaches that do not consider
servicing needs could result in shortages
of HCFC–22. EPA considered, but is not
proposing, allocating a percentage of the
2010 aggregate HCFC consumption and
production caps for HCFC–22 and
HCFC–142b respectively equal to the
same overall percentage of the aggregate
HCFC consumption and production
caps allocated for each substance in the
2003 allocation rule. Under this
approach, EPA would start with the
percentage of the total allowable HCFC
consumption and production level
attributable to each HCFC in the 2003
rule. For example, beginning in 2004,
the total allowable HCFC consumption
level was 9,906 ODP-weighted metric
tons. Using the consumption data for
each company’s highest ODP-weighted
consumption year, EPA allocated
HCFC–22 allowances equal to 66
percent of 9,906 ODP tons and HCFC–
142b allowances equal to 13 percent of
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9,906 ODP tons. We could apply the
same percentages to the total allowable
HCFC consumption level for 2010–2014
of 3,810 ODP-weighted metric tons. This
would provide congruence for the
overall ‘‘pie.’’ EPA is concerned,
however, that such an approach would
provide significantly fewer HCFC–22
allowances in 2010 than would be
needed for servicing. Sixty-six percent
of the aggregate HCFC cap for the
control periods 2010–2014 equals 2,515
ODP-weighted metric tons, which is
approximately equal to 46,000 metric
tons of HCFC–22. The Servicing Tail
report, however, estimates that
approximately 62,500 metric tons of
HCFC–22 will be needed for servicing in
2010. EPA is concerned that if large
quantities of recycled or reclaimed 7
HCFC–22 are not available, the need to
make up the almost 20,000-metric-ton
shortfall could trigger illegal activities
such as imports of HCFC–22 by those
that do not hold consumption
allowances. As noted elsewhere in this
NPRM, EPA does not believe it should
rely on inter-pollutant transfers to
secure such a significant amount of
HCFC–22 allowances.
While EPA regulations aim at
maximizing refrigerant reuse, EPA
believes that reclamation rates in 2010–
2014 would not be sufficient to avert a
shortfall if EPA were to issue 46,000
metric tons of consumption allowances
to HCFC–22 using this option. This
shortfall would equal approximately 30
percent of the total projected servicing
need for 2010–2014. As explained in the
next section, amounts reported to EPA
of reclaimed refrigerant coupled with
estimates for available recycled
refrigerants indicate that currently less
than 30 percent of the servicing need
can be met through refrigerant recovery
and reuse during these control periods.
Thus, EPA has rejected this method as
a basis for deciding the relative amounts
7 EPA has defined Reclaim, Recover and Recycle
at § 82.152 as follows: (1) Reclaim refrigerant means
to reprocess refrigerant to all of the specifications
in appendix A to 40 CFR part 82, subpart F (based
on ARI Standard 700–1995, Specification for
Fluorocarbons and other Refrigerants) that are
applicable to that refrigerant and to verify that the
refrigerant meets these specifications using the
analytical methodology prescribed in section 5 of
appendix A of 40 CFR part 82, subpart F; (2) recover
refrigerant means to remove refrigerant in any
condition from an appliance and to store it in a
external container without necessarily testing or
reprocessing it in any way; (3) recycle refrigerant
means to extract refrigerant from an appliance and
clean refrigerant for reuse without meeting all of the
requirements for reclamation. In general, recycled
refrigerant is refrigerant that is cleaned using oil
separation and singe or multiple passes through
devices, such as replaceable core filter-driers,
which reduce moisture, acidity, and particulate
matter. These procedures are usually implemented
at the field job site.
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of HCFC–22 and HCFC–142b
allowances to issue for the 2010–2014
control periods. A memorandum to the
docket entitled ‘‘Summary: EPA
Analysis of U.S. Reclamation Practices
and Trends’’ provides additional
information on reclamation practices
underlying the assumptions in EPA’s
analysis.
EPA’s primary objective is to ensure
compliance with the obligation under
the Montreal Protocol to reduce the
ODP-weighted ‘‘basket’’ of HCFCs to 75
percent below the baseline for
production and consumption beginning
January 1, 2010. Various options, alone
or in combination, could be used to
meet this objective. EPA believes,
however, that the proposed option
provides the best assurance that
allocations will be available to meet the
projected needs for all HCFCs during
the 2010–2014 control periods.
6. How Important Is HCFC–22 in
Determining the Allocation of
Allowances?
HCFC–22 is the HCFC most widely
produced and used in applications for
which servicing of existing equipment
will occur during 2010–2019. The
Servicing Tail analysis focused on
HCFC–22, which represents a majority
of the market, but also includes
information on other refrigerants and
components of blends including HCFC–
142b and HCFC–123. The report
included in the docket focuses on two
major equipment types: refrigeration
and air conditioning.
Refrigeration equipment can be
broken down into four categories: (1)
Domestic refrigeration, (2) refrigerated
transport, (3) industrial process
refrigeration (IPR), and (4) commercial
refrigeration. Domestic refrigeration
includes household refrigerators,
household freezers, combination
refrigerator/freezer units, and water
coolers. With the exception of certain
older household freezers that use
HCFC–22, this category typically does
not use HCFCs or blends containing
HCFCs. Refrigerated transport includes
refrigeration used in equipment that
moves products from one place to
another and includes refrigerated ship
holds, truck trailers (i.e., reefer trucks),
railway freight cars, and other shipping
containers. Industrial process
refrigeration systems are complex,
customized systems used to cool
process streams in the chemical, food
processing, pharmaceutical,
petrochemical, and manufacturing
industries. This sector also includes
industrial ice machines, equipment
used directly in the generation of
electricity, and ice rinks. Commercial
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refrigeration can be further broken down
into three end-uses: cold storage
warehouses, retail food systems, and ice
makers.
EPA estimates that HCFC–22 use in
air-conditioning and refrigeration
equipment was approximately 115,000
metric tons in 2006. Approximately 66
percent—about 76,000 metric tons—was
for servicing existing equipment, with
the percentage higher for the
refrigeration industry than the airconditioning industry. The majority of
HCFC–22 consumption for servicing is
currently attributed to residential and
small commercial unitary equipment
and retail food refrigeration equipment.
The projected servicing need for
HCFC–22 in 2010 is approximately
62,500 MT (3,438 ODP-weighted metric
tons) or approximately 90 percent of the
consumption cap for all HCFCs in 2010,
which is 3,810 ODP-weighted metric
tons. Although EPA estimates that the
servicing need for HCFC–22 will
decrease each year beginning in 2010,
EPA is not convinced that there is
enough room under the aggregate HCFC
cap to consider any scenario where the
allocation of allowances for HCFC–22
production or consumption is
substantially higher than the projected
servicing need, given the need to
allocate allowances for other HCFCs as
discussed elsewhere in this NPRM.
In the 2003 allocation rule, EPA
issued baseline consumption
allowances for HCFC–22 equaling
119,384,852 kilograms (119,385 metric
tons, or 6,566 ODP-weighted metric
tons) and allocated 100 percent of the
baseline for the 2003–2009 control
periods. The Montreal Protocol cap for
all U.S. HCFC consumption beginning
in 2004 was 9,906 ODP-weighted metric
tons. The baseline allowances for
HCFC–22 consumption represented
approximately 66 percent of the
Montreal Protocol HCFC consumption
cap for the United States.
In the 2003 allocation rule EPA issued
baseline production allowances for
HCFC–22 equaling 110,619,359
kilograms (110,619 metric tons, or 6,084
ODP-weighted metric tons) and
allocated 100 percent of the baseline for
the 2003–2009 control periods. The
Montreal Protocol cap for all U.S. HCFC
production beginning in 2004 was
10,999 ODP-weighted metric tons. The
baseline allowances for HCFC–22
production represented approximately
70 percent of the Montreal Protocol
HCFC production cap for the United
States.
In the 2003 allocation rule EPA issued
baseline consumption allowances for
HCFC–142b equaling 21,088,677
kilograms (21,089 metric tons, or 1,371
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ODP-weighted metric tons) and
allocated 100 percent of the baseline for
the 2003–2009 control periods. This
represented approximately 14 percent of
the Montreal Protocol HCFC
consumption cap of 9,906 ODPweighted metric tons for the United
States.
In the 2003 allocation rule EPA issued
baseline production allowances for
HCFC–142b equaling 25,090,394
kilograms (25,090 metric tons, or 1,631
ODP-weighted metric tons) and
allocated 100 percent of the baseline for
the 2003–2009 control periods. This
represented approximately 15 percent of
the 10,999 ODP-weighted metric tons
allowed for the United States under the
Montreal Protocol HCFC cap.
In the 2003 allocation rule EPA issued
baseline consumption and production
allowances for HCFC–141b, and under
its ‘‘worst first’’ chemical-specific
approach allocated 0 percent of baseline
for consumption and production—
eliminating, with certain narrow
exemptions, the production and import
of HCFC–141b. EPA projects that a
minimal amount of HCFC–141b will
continue to be needed for exempted
HCFC–141b production until 2015.
Although EPA does not intend to
allocate HCFC–141b production or
consumption allowances, EPA must
account for continued consumption and
production of minimal exempted
amounts of HCFC–141b to ensure
compliance with the 2010 caps.
In addition, EPA must ensure that
production and consumption of HCFCs
for which baselines were not established
in the 2003 allocation rule does not
result in an aggregate allocation
exceeding the HCFC production or
HCFC consumption caps established by
the Montreal Protocol.
Air-conditioning and refrigeration
equipment commonly requires
servicing, which may include the need
to add refrigerant to account for
refrigerant losses that occur over time.
The limited amount of production and
import of HCFC–22 and HCFC–142b
beginning January 1, 2010, will be
allowed only for servicing equipment
manufactured prior to January 1, 2010.
Later in this proposal, EPA will
consider what is meant by
‘‘manufactured.’’
The Agency recognizes that servicing
needs can be met with a combination of
newly manufactured HCFCs (virgin
HCFCs) and HCFCs that have been
recovered and either recycled or
reclaimed. Therefore, EPA does not
anticipate that the entire projected
HCFC–22 servicing need (3,438 ODP
tons) will need to be produced or
imported to meet the anticipated
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demand. A percentage of that servicing
need will be met by recovering used
HCFC–22 from existing equipment. The
‘‘servicing tail’’ report provides analysis
of various scenarios regarding
reclamation. In addition, EPA’s memo to
the docket ‘‘Summary: EPA Analysis of
U.S. Reclamation Practices and Trends’’
provides background on the reclamation
industry, which includes information
concerning capacity to reclaim greater
amounts of refrigerants, and projects
that more than 20 percent of the
servicing need can be met by recovering
used HCFC–22 from existing equipment.
Recycled and reclaimed HCFCs offset
the need for newly-manufactured
HCFCs and after the terminal phaseout,
as with the CFC phaseout, will become
the sole source of HCFCs for servicing
existing equipment. EPA regulations at
40 CFR part 82 Subpart F manage the
recovery, recycling, reclamation, and
reuse of HCFCs under section 608 of the
CAAA. Under those regulations, HCFCs
may not be vented and must be
recovered and are then generally either
recycled, reclaimed, or in some cases
destroyed. Therefore, it is reasonable to
assume that some amount of used
HCFCs will be available to meet
servicing needs. In accordance with the
chemical-by-chemical phaseout regime
adopted by the United States, after 2020
only recycled, reclaimed, and stockpiled
HCFC–22 and HCFC–142b will be
available to service appliances that
require those substances. EPA’s existing
regulations at § 82.16 terminate HCFC–
22 and HCFC–142b production and
consumption at the end of 2019, and
EPA is not proposing to modify that
provision. The very small amount of
additional production and consumption
of HCFCs allowed under Article 2F of
the Montreal Protocol between 2020 and
2030 for servicing existing appliances
(0.5 percent of baseline) will only be
permitted for HCFCs other than HCFC–
141b, HCFC–22, and HCFC–142b, per
§ 82.16(e), and restricted to servicing
only air-conditioning and refrigeration
equipment manufactured prior to
January 1, 2020 per § 82.16(d).
Given its previous experience with
the Class I phaseout, EPA believes that
over time a larger percentage of
recovered HCFCs will be available for
reuse. For example, after the 1996 CFC
phaseout, motor vehicles with CFC–12
air-conditioning systems continued to
be serviced with used CFC–12. In fact,
even today recovered CFC refrigerants
are still in use for servicing a range of
older equipment.
The Servicing Tail report used EPA’s
Vintaging Model to determine the
quantities of HCFC–22 from existing
(recycled or reclaimed) sources that can
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meet post-2010 servicing needs with the
remaining quantities required through
virgin manufacture (expending
allowances). For a given year, the
Vintaging Model assumes that a certain
percentage of refrigerants, which varies
by end-use, is recovered from discarded
equipment. The model aggregates the
quantities recovered but does not
distinguish the ‘‘pool’’ of refrigerant
between quantities that are reclaimed
versus those that are recycled. EPA’s
Vintaging Model was the primary tool
used to launch the analysis and form the
basis for quantitative estimates of
projected HCFC consumption. The
Vintaging Model estimates the annual
chemical emissions from industry
sectors that have historically used ODS,
including air conditioning, refrigeration,
foams, solvents, aerosols, and fire
protection. Within these industry
sectors, there are over 50 independently
modeled end-uses. The model uses
information on the market size and
growth for each of the end-uses, as well
as a history and projections of the
market transition from ODS to
alternatives. As ODS are phased out, a
percentage of the market share
originally filled by the ODS is allocated
to each of its substitutes. The model
tracks emissions of annual ‘‘vintages’’ of
new equipment that enter into operation
by incorporating information on
estimates of the quantity of equipment
or products sold, serviced, and retired
or converted each year, and the quantity
of the compound required to
manufacture, charge, and/or maintain
the equipment. EPA’s Vintaging Model
makes use of this market information to
build an annual inventory of in-use
stocks of equipment and the ODS
refrigerant and non-ODS substitutes in
each of the end-uses.
For purposes of analysis, the
Servicing Tail report considers
scenarios for HCFC–22 and HCFC–142b
where differing amounts of servicing
needs were met by recycled and
reclaimed refrigerants. For example, the
report examines scenarios in which 10
percent, 15 percent, 20 percent, 25
percent, 50 percent, and 75 percent of
the total amount of HCFC–22 in retired
or converted equipment is recovered.
These analyses depict the potential
ratios of new and recovered HCFCs that
could be available during the years
2010–2019 to meet the overall servicing
needs recognizing that the higher
recovery rates are less likely for the
earlier control periods.
EPA has anecdotal and reported
information concerning recovery rates
for refrigerants. Commenters at the
September 2006 stakeholder meeting
indicated that approximately 10 percent
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of HCFC–22 in current use was
recovered and either reclaimed or
recycled. Data reported to EPA
consistent with 40 CFR Part 82 Subpart
F shows that approximately 3716 metric
tons (204 ODP tons) of HCFC–22 was
reclaimed in 2007. EPA does not track
recycled refrigerants, since recycled
refrigerant (unlike reclaimed refrigerant)
typically is charged back into
equipment with the same ownership
rather than re-entering the market.
Readers interested in additional
information concerning recovery and
recycling should review the Servicing
Tail report. Given the regulatory
requirements for recycling and
reclamation (at 40 CFR part 82 subpart
F), experience with the CFC phaseout,
and industry practices, EPA estimates
that during the period 2010–2014, an
amount greater than 20 percent of the
total servicing need for HCFC–22 can be
met with HCFC–22 that has been
recovered and either recycled or
reclaimed. Since EPA is not banning the
use of HCFC–22 equipment, recovered
and reclaimed HCFC–22 will become a
more valuable commodity as the U.S.
approaches the January 1, 2015,
stepdown. The demand for HCFC–22 to
service existing equipment should
provide an economic incentive for an
increase in the quantities of used
HCFC–22 available for reclamation. As
an indicator, EPA notes that several
reclamation companies have recently
started offering financial payments for
used HCFC–22. The docket for this
NPRM provides further information
regarding EPA’s assumptions regarding
the availability of recycled or reclaimed
HCFC–22 to meet servicing needs.
EPA has considered, but is proposing
to reject, using an increasing number to
represent the contribution of recycled
and reclaimed refrigerant for each of the
control periods from 2010–2014 and
thus simultaneously reducing the
amount of allowances needed for
HCFC–22. EPA believes for these
control periods, maintaining a constant
number of allowances would reduce the
overall burden for the allowance holders
and would ease business practices. EPA
notes that recovery rates could fluctuate
yearly and thus holding steady for
control periods 2010–2014 is an
appropriate approach. In addition, the
step downs in the expected recycling
and reclamation rates then more closely
reflect the international commitments in
Decision XIX/6. EPA expects that for the
2015–2019 control periods, the percent
of servicing need met by recovered
refrigerants will increase and, as noted
above, beginning in 2020 all servicing
needs for HCFC–22 will be met with
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recovered refrigerants. EPA will address
the percent of servicing need to be met
by recovered refrigerants in 2015–2019
in a subsequent rulemaking to reflect
the 2015 stepdown required by Article
2F:
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 1 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 the controlled
substances in Group 1 of Annex C does not
exceed zero. However, * * * each Party may
exceed that limit on consumption by up to
zero point five percent 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.
EPA believes that meeting demand after
2010 will require the reuse of HCFC–22,
and is particularly concerned with
ensuring that demand is met during the
first years of the 2010–2014 control
periods when a large number of
appliances using HCFC–22 will still be
suitable for use. EPA notes that a
smooth transition for stakeholders—
including continued availability of
needed material for approved uses—has
historically been an essential aspect of
the U.S.’s success in implementing the
Montreal Protocol and Clean Air Act
requirements. For purposes of the 2010–
2014 control periods, EPA is proposing
to use a number in the range of 15—25
percent to represent the contribution of
recovered refrigerant to the total
servicing need. EPA requests comments
on the amount of the total servicing
need for HCFC–22 that can be met with
recovered refrigerants, which is between
15 and 25 percent of total estimated
servicing need.
7. HCFC–22 Allowances for 2010–2014
EPA is proposing to allocate HCFC–22
consumption allowances to meet 80
percent of the servicing need, assuming
that the remaining 20 percent will be
met by recovered HCFC–22 that is either
recycled or reclaimed. This translates
into approximately 50,000 metric tons
(2,750 ODP-weighted metric tons), or
approximately 72 percent of the total
HCFC consumption cap for each of the
control periods from 2010 through 2014.
As it did in the 2003 allocation rule,
EPA is proposing to allocate production
allowances among different chemicals
using the same percentage breakdown as
for consumption allowances. This
would allocate 45,498 metric tons (2,502
ODP tons) of the 3,884.25-ODP-ton
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production cap to HCFC–22 production.
This is consistent with section 605(c) of
the Clean Air Act, which states that EPA
shall promulgate a phaseout schedule
for HCFC consumption that is the same
as that applicable to HCFC production.
EPA recognizes that there is a difference
between the amount of imported and
produced HCFCs and that the degree of
difference may vary over time. However,
EPA does not believe it is necessary to
use two different chemical-by-chemical
percentage breakdowns (i.e., one for
consumption allowances and another
for production allowances) to ensure
compliance with the production and
consumption caps. Therefore, for
simplicity and for consistency with
section 605(c), EPA is proposing to use
the same percentages for production and
consumption allocations—deriving the
percentages based on estimated need for
each individual HCFC.
If more HCFC–22 is recovered,
recycled, and reclaimed than assumed
in this proposed rule, EPA anticipates
that the demand for virgin HCFC–22
will decrease. Thus it is possible that
not all the production and consumption
allowances will be used. It is also
possible that any ‘‘extra’’ HCFC–22
allowances could be converted via interpollutant transfers to meet other HCFC
needs.
EPA requests comments on its
application of a 20 percent rate of
availability of recovered (recycled or
reclaimed) HCFC–22. As discussed
above, EPA estimates that at least 20
percent of the 2010–2014 servicing need
can be met from recycled or reclaimed
material. EPA believes that by the
January 1, 2010, effective date of this
rule, 20 percent of the 2010–2014
servicing needs should be available
from recycled or reclaimed material,
and that the availability of recycled or
reclaimed material would be expected
to increase as the phaseout progresses.
EPA notes that in 2020 all HCFC–22 and
HCFC–142b used to service airconditioning and refrigerant equipment
will need to be recycled or reclaimed, in
light of the nearly-complete phasedown
of production and import of virgin
material that is scheduled to occur by
that date. Additionally, EPA regulations
already prohibit the intentional venting
of refrigerants and require refrigerant
recovery, and the market for recycled
and reclaimed refrigerant is predicted to
grow as the phaseout progresses. EPA is
interested in other data regarding the
actual and projected rates of refrigerant
recycling and reclamation in the U.S., as
well as whether it should consider
allocating allowances for HCFC–22 at
other levels, such as approximately 100
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percent, 90 percent, 80 percent, or 75
percent of the aggregate 2010 cap.
8. HCFC–142b Allowances for 2010–
2014
After subtracting out the proposed 72
percent of the 2010 cap for HCFC–22, 28
percent remains to meet all other HCFC
needs. EPA believes that the remaining
28 percent is more than the projected
HCFC–142b servicing needs, the
amounts of HCFC–141b that EPA
expects to allow based on the petition
process, and all other likely HCFC
consumption for the 2010–2014 control
periods. This is based on a review of
required quarterly, annual, and periodic
reports; the Servicing Tail analysis; and
comments submitted to EPA by
stakeholders in advance of this
proposed rulemaking. As described
below, the amounts allocated for these
substances reflect these assumptions.
As discussed in the Servicing Tail
report described above, the projected
servicing need for HCFC–142b is
extremely low: Approximately 100
metric tons (7 ODP tons). In estimating
the need for 2010–2014, EPA has
considered the amount of HCFC–142b
produced and imported into the United
States as reported to EPA in recent years
under the existing requirements.
Whereas earlier versions of the
Servicing Tail analysis focused on
HCFC–22, the most recent version—
which is included in the docket for this
rulemaking—also projects the demand
for all other HCFCs for which
consumption and production are likely
to occur: HCFC–142b, HCFC–123,
HCFC–124, HCFC–225ca, and HCFC–
225cb. The recovery, recycling, and
reclamation requirements apply to
HCFC–142b as they do to all
refrigerants, but recovery rates for
HCFC–142b are considerably lower than
for HCFC–22, largely because HCFC–
142b is typically used in blended
refrigerants. The limited amount of data
available to EPA indicates that less than
1 percent of HCFC–142b is recycled or
reclaimed. In light of the limited data
available, and the extremely low
estimate of recycling and reclamation,
EPA is proposing to allocate 100 percent
of the projected HCFC–142b servicing
need rather than assuming that a
specified percentage of the need will be
met through the use of recycled or
reclaimed amounts. EPA is proposing to
issue consumption allowances for
HCFC–142b of 100 metric tons (7 ODP
tons). Allocating 72 percent of the
consumption cap to HCFC–22 and less
than 1 percent to HCFC–142b allows up
to 27 percent to be allocated to other
HCFCs.
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EPA is proposing to allocate
production allowances for HCFC–142b
at the same proportion of the production
cap as was used to allocate consumption
allowances as a proportion of the
consumption cap. Thus EPA is
proposing to allocate production
allowances for HCFC–142b at 142
metric tons (9.2 ODP tons).
9. How Does the Aggregate for HCFC–
22 and HCFC–142b Translate to Entityby-Entity?
EPA is proposing to allocate up to a
total of no more than 50,000 metric tons
of HCFC–22 consumption allowances,
45,498 metric tons of HCFC–22
production allowances, 100 metric tons
of HCFC–142b consumption allowances,
and 142 metric tons of HCFC–142b
production allowances. However, EPA
actually allocates allowances to
individual persons (i.e., legal entities).
As discussed in section III.A.2 of this
preamble, EPA’s preferred approach is
to apportion baselines and allocate
allowances on a pro-rata basis to the
entities that received baseline
allowances in the 2003 allocation rule.
Nevertheless, the Agency is taking
comment on other allocation options,
which are discussed below.
Company-specific production and
consumption baselines (also referred to
as ‘‘baseline allowances’’) for HCFC–
141b, HCFC–22, and HCFC–142b are
listed at §§ 82.17 and 82.19(a),
respectively. The percentage of baseline
each entity receives in each control
period from 2003 through 2009 appears
at § 82.16(a). EPA is proposing to amend
§ 82.16(a) to include the 2010–2014
control periods. For the years 2010–
2014, as for the years 2003–2009, EPA’s
preferred approach is to specify the
same percentage of baseline for each
entity. EPA considers allocation of the
same percentage to each entity listed at
§ 82.17 and § 82.19 to be the most
equitable approach. EPA does not
believe that its allocation of baseline
allowances should reflect sales of
controlled substances that would
subsequently occur. EPA believes that
the market for HCFCs that the allowance
holders sell to, will evolve to reflect
these restrictions as it would evolve
other market conditions. This approach
is consistent with EPA’s previous
approach to allocations. However, EPA
does note that there have been and
continue to be restrictions on use of
controlled substances. EPA considered
alternative approaches such as
evaluating sales information for HCFCs
where allowances were expended and
considering the differences between
expended allowances versus allowances
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acquired via inter-pollutant transfers.
EPA has included in the docket to this
rulemaking a memorandum titled Draft
Regulatory Options for Allocating HCFC
Allowances after 2009 as well as
comments submitted by stakeholders
describing alternative approaches that
the Agency may consider.
As previously noted, allowances
allocated for individual control periods
may be thought of as ‘‘calendar-year
allowances’’ to distinguish them from
the apportioned baseline production or
consumption allowances (§ 82.17 and
§ 82.19). For 2010–2014, EPA is
proposing to apportion production and
consumption baselines for HCFC–22
and HCFC–142b to the same entities
that were apportioned HCFC–22 and
HCFC–142b baselines in the 2003
allocation rule. EPA is proposing to
amend that list of entities and their
baselines to reflect changes in the
entities’ names as well as mergers and
acquisitions, but only where EPA has
been notified of changes in writing
before or during the comment period for
this rulemaking, which closes February
23, 2009 or March 9, 2009 if a hearing
is held.
The proposed company-specific
baselines also reflect adjustments
resulting from approved inter-pollutant
and/or inter-company transfers of
baseline allowances (i.e., permanent
rather than calendar-year allowances)
through the process described in
§ 82.23. To be reflected in the final
apportionment of baselines in the final
rule, such transfers must have occurred,
with EPA approval, before or during the
second quarter of the 2008 control
period (i.e., by June 16, 2008). As noted
in the 2003 allocation rulemaking, EPA
is sensitive to the need to avoid creating
an ‘‘uneven playing field’’ that could
potentially skew allocations to entities
with ample resources and good access to
information. EPA held a public meeting
on June 16, 2008. As it did in the 2003
allocation rulemaking when
determining which years to use for
establishing a baseline, EPA is using the
date of the public meeting as a cutoff
date for inter-pollutant and intercompany transfers of permanent
baseline allowances that would be
reflected in the revised tables shown in
this NPRM. EPA believes that since
allowance transfers affect the pool of
allowances for each controlled
substance and thus the amounts
apportioned company-by-company, a
cutoff date in advance of the issuance of
the NPRM is necessary and thus
selected a date based on availability and
access to information.
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78693
EPA recognizes that in some cases
entities are no longer actively involved
in HCFC production, import, and/or
export activities. EPA is seeking
comment on whether it should retain
the baselines for such entities (the
preferred approach) or whether it
should retire, auction, or redistribute
the baselines among the active entities.
EPA has placed in the docket to this
proposed rule a memorandum that
considers and evaluates each of these
options, discussing both the advantages
and disadvantages, titled Draft
Regulatory Options for Adjusting the
HCFC Baseline for Allowance
Allocations. For example, apportioning
a baseline to an entity that is no longer
active means that its allowances might
not be expended, resulting in a net
environmental benefit. Allocating
allowances via an auction may allow for
new entrants to purchase allowances or
for allowances to be purchased and
intentionally retired. However, EPA
currently does not use an auction for
allocating allowances and anticipates
that designing and deploying an auction
system could cause administrative
delays. An auction system could impose
costs on new participants, which would
be borne by non-participants who
received allowances for the 2003–2009
control periods without charge. EPA
notes, however, that under the current
allowance system for new entrants to
acquire allowances, allowances must be
transferred from an existing allowance
holder and that when such a transfer
occurs, costs are likely to arise from the
purchase price and any transaction
costs. Allocating allowances to entities
that are no longer active in the field may
provide an option for new entrants and
for entities seeking to purchase and
retire allowances, as the inactive entities
would presumably be willing sellers.
EPA is proposing to retain the baselines
for HCFC–22 and HCFC–142b as
previously apportioned, subject to
updates to reflect name changes and
permanent inter-company and interpollutant transfers.
Consistent with past practice, EPA is
publishing baseline allowance
information in this NPRM, having first
notified the affected companies of its
intention to do so.
Applying the approach described
above, EPA proposes to apportion
production and consumption baselines
for HCFC–141b, HCFC–22, and HCFC–
142b to the following entities in the
following amounts:
Table
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Person
Controlled substance
Allowances
(kg)
Production Allowance Allocation
Arkema .........................................................................................................................
DuPont ..........................................................................................................................
Honeywell .....................................................................................................................
MDA Manufacturing ......................................................................................................
Solvay Solexis ..............................................................................................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–142b ..............................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–142b ..............................................
HCFC–22 ..................................................
HCFC–142b ..............................................
46,692,336
24,647,925
484,369
42,638,049
37,378,252
28,705,200
2,417,534
2,383,835
6,541,764
Consumption Allowance Allocation
ABCO Refrigeration Supply .........................................................................................
Altair Partners ...............................................................................................................
Arkema .........................................................................................................................
Automatic Equipment Sales .........................................................................................
Condor Products ..........................................................................................................
Continental Industrial Group ........................................................................................
Coolgas, Inc .................................................................................................................
Coolgas Investment Property .......................................................................................
Discount Refrigerants ...................................................................................................
Dupont ..........................................................................................................................
Full Circle .....................................................................................................................
H.G. Refrigeration Supply ............................................................................................
Honeywell .....................................................................................................................
ICC Chemical Corp ......................................................................................................
Ineos Fluor Americas ...................................................................................................
Kivlan & Company ........................................................................................................
MDA Manufacturing ......................................................................................................
Mondy Global ...............................................................................................................
National Refrigerants ....................................................................................................
Refricenter of Miami .....................................................................................................
Refricentro ....................................................................................................................
R-Lines .........................................................................................................................
Saez Distributors ..........................................................................................................
Solvay Fluorides ...........................................................................................................
Solvay Solexis ..............................................................................................................
Tulstar Products ...........................................................................................................
EPA requests comments on the
proposed method and calculations for
allocating allowances on an entity-byentity basis for HCFC–22 and HCFC–
142b production and consumption.
10. Baselines for HCFC–123, HCFC–124,
HCFC–225ca, and HCFC–225cb
EPA is proposing to establish and
apportion baselines for other HCFCs
that have been produced or imported in
recent years by using information on
production, import, export, and other
transactions that has been reported to
the Agency under existing regulations.
EPA requires recordkeeping and
reporting for production, import, export,
and trade of all ozone-depleting
substances, including HCFCs for which
baseline allowances have not yet been
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HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–142b ..............................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–141b ..............................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–142b ..............................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–142b ..............................................
HCFC–141b ..............................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–142b ..............................................
HCFC–141b ..............................................
established. The recordkeeping and
reporting requirements implement
section 603 of the Clean Air Act and
ensure that companies are in
compliance with regulatory and Clean
Air Act requirements and that the
United States is able to meet
international obligations. EPA is not
proposing any changes to these
requirements.
EPA reviewed HCFC production,
import, and export data for the years
leading up to the 2003 allocation rule,
and chose to establish baselines and
allocate allowances for the highest-ODP
HCFCs (e.g., a ‘‘worst-first’’ approach) in
a manner that ensured U.S. compliance
with the 2004 cap (35 percent below the
U.S. baseline). Prior to the tightening of
the 2010 HCFC cap at the 19th Meeting
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279,366
302,011
48,637,642
25,405,570
483,827
54,088
74,843
20,315
16,097,869
590,737
375,328
994
38,814,862
9,049
52,797
14,865
40,068
35,392,492
20,749,489
1,315,819
81,225
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
3,940,115
194,536
89,913
of the Parties to the Montreal Protocol
in September 2007, EPA anticipated that
limiting production and consumption of
HCFC–22 and HCFC–142b for the 2010–
2014 control periods would ensure
sufficient room under the then-effective
65 percent reduction cap without the
need to restrict production and
consumption of other HCFCs. Prior to
attending the 19th Meeting of the Parties
where agreement was reached to reduce
the 2010 cap from a 65 percent
reduction to a 75 percent reduction,
EPA conducted analysis which was
shared with stakeholders to ensure that
the U.S. could consider changes to our
obligations that were both meaningful
for ozone layer protection and
achievable, allowing servicing needs to
continue to be met. Considering that the
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September 2007 Montreal Adjustment
provides for adjustment of the cap from
a 65 percent to a 75 percent reduction,
EPA is proposing additional precautions
to ensure that the more stringent cap
will not be exceeded. These precautions
include establishing and apportioning
baselines for the 2010–2014 control
periods for other HCFCs that were
produced or imported during the 2003–
2007 control periods.
EPA is proposing to apportion
baselines for the other HCFCs by
amending §§ 82.17 and 82.19 to include
company-specific production and
consumption baselines for HCFC–123,
HCFC–124, HCFC–225ca, and HCFC–
225cb. EPA data indicate that those four
HCFCs were produced, imported, or
exported during the 2003–2007 control
periods.
In the 2003 allocation rule, EPA did
not issue allowances for all HCFCs,
noting in part ‘‘that the continuously
developing HCFC market would be
hampered by such distribution’’ and
that the market proportions at that time
‘‘of these lower-ODP HCFCs do not
reflect the rapidly expanding market
and that distributing allowances for
these HCFCs at [that] time would
unnecessarily restrict their supply and
impede transition to less ozonedepleting substances’’ (68 FR 2823).
Considering the recent adjustments to
the Montreal Protocol and the evolution
in the HCFC market, EPA believes it is
now appropriate to establish a baseline
and apportion baseline allowances for
HCFC–123, HCFC–124, HCFC–225ca,
and HCFC–225cb.
All HCFCs are covered under the
Montreal Protocol stepwise reductions,
and EPA must consider all HCFC
production and import in ensuring that
the United States continues to meet its
international obligations. The four
HCFCs identified in this proposal are
the only remaining HCFCs commonly
used in the United States that do not
currently have established baselines.
EPA does not expect that establishing
baseline allowances for these four
HCFCs would trigger additional
recordkeeping or reporting obligations,
since companies that produce, import,
or export any HCFC already report
production and consumption data to
EPA. The impacts stem from the years
chosen for establishing a baseline, the
apportionment of the baseline among
companies, and the percentage of
baseline allocated for the control years
2010–2014. EPA discusses these issues
more specifically below.
EPA recognizes that many different
methods and data sources can be used
to establish baseline allowances. EPA
believes that the best data to use for this
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purpose are the data reported to the
Agency under § 82.24. Entities that have
not reported data would not be included
in the baseline calculations and would
not receive baseline allowances. If
necessary, EPA could augment the data
for completeness or to verify accuracy
by issuing requests for information
under section 114 of the CAA. EPA
seeks comment on its proposal to use
data reported under § 82.24 as the basis
for identifying the entities to which
allowances should be allocated.
In the 2003 allocation rule, EPA
calculated each entity’s HCFC–141b,
HCFC–22, and HCFC–142b baseline
from that entity’s highest reported
consumption and production from the
years 1994–1997. EPA chose that
particular range of years because
beginning in 1998, some entities were
aware of the impending rulemaking and
could have increased production or
import in an effort to secure higher
baseline allowances. EPA stated in the
2003 allocation rulemaking that ‘‘by not
selecting a year after 1997 it will avoid
creating an uneven playing field that
skews allocations to those companies
with ample resources and good access to
information’’ (68 FR 2832). EPA is
proposing to follow a similar approach
for these four HCFCs by considering the
highest reported data from a range of
years rather than selecting a single
baseline year. EPA is proposing to use
the data reported for the 2005–2007
control periods to calculate baselines for
the four additional HCFCs, based on an
entity’s highest reported consumption
and production for the 2005–2007
control periods. By using past years,
EPA avoids any ramp-up in the level of
production and consumption resulting
from a desire to maximize individual
baselines in anticipation of this rule
going into effect. By using recent data,
EPA ensures the baseline reflects the
current market as closely as possible,
and issues raised when EPA decided to
postpone allocating baseline allowances
for these HCFCs in 2003.
EPA requests comment on the need to
establish baselines for these four
additional HCFCs at this time. In
particular, EPA is interested in
comments concerning whether
establishing and apportioning a baseline
for these four HCFCs, and allocating a
percentage of that baseline for the 2010–
2014 control periods, is necessary to
ensure that the United States does not
exceed the 25 percent HCFC cap under
the 2007 Montreal Adjustment. EPA
requests comments on the
appropriateness of using each
company’s highest reported
consumption and production for 2005–
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78695
2007 rather than the lowest or an
average.
11. What Percentage of the Baseline Will
EPA Allocate for HCFC–123, HCFC–124,
HCFC–225ca, and HCFC–225cb for the
Control Periods 2010–2014?
EPA is proposing to establish baseline
production and consumption
allowances for HCFC–123, HCFC–124,
HCFC–225ca, and HCFC–225cb, and to
allocate 125 percent of these baselines
for the 2010–2014 control periods. By
establishing these baseline production
and consumption allowances, EPA
would be creating a mechanism for
limiting growth in production and
consumption for these HCFCs during
those control periods. Regardless of any
action by EPA, given the 605(a) selfeffectuating provisions, further growth
for these HCFCs will be constrained in
2015 by the provisions on use. For
example, given the characteristics of
HCFC–225ca and HCFC–225cb, they are
generally used as solvents. As of January
1, 2015 that application will be
restricted. Thus any growth in the use
of these HCFCs will be balanced to some
extent by the self-effectuating
provisions. Thus EPA is recognizing
that other limiting factors, such as
section 605(a) of the CAA, will
considerably affect how these HCFCs
can be used in subsequent control
periods. While it is appropriate and
necessary for EPA to allocate less than
100 percent of the baseline allowances
for HCFC–22 and HCFC–142b, given the
use restrictions that apply beginning
January 1, 2010, these four low-ODP
HCFCs are not subject to domestic use
restrictions until a later date. For
example, while newly manufactured
HCFC–22 cannot be produced or
imported for charging into new airconditioning and refrigeration
appliances as of January 1, 2010 (40 CFR
82.16(c)), HCFC–123 can be produced or
imported for new appliances until 2020
(40 CFR 82.16(d)). Therefore, EPA
believes that it is not appropriate to
allocate less than 100 percent of
baseline for these compounds in this
action. EPA has included information
and analysis on these HCFCs in Chapter
3 of the Servicing Tail analysis, which
is in the docket for this rulemaking.
After reviewing trends in the
production, import, export, and trade
data submitted to EPA since 2003, EPA
believes that allocating 100 percent of
the baseline should be sufficient to meet
current demand. The Servicing Tail
analysis available in the docket provides
additional information concerning
trends based on the Vintaging Model
and additional information provided by
stakeholders. However, EPA has heard
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from stakeholders that some amount of
market expansion for these low-ODP
HCFCs is possible during the 2010–2014
control periods. Given the low ODPs for
these HCFCs, EPA believes that if it
were to allocate 125 percent of the
baseline for 2010–2014, the United
States could still meet the overall HCFC
cap of 75 percent below the baseline
during these control periods. EPA
believes that any continued growth for
these HCFCs will be considerably
affected by section 605(a) as of January
1, 2015.
Through this action, EPA is proposing
to allocate allowances equaling 125
percent of the baseline for HCFC–123,
HCFC–124, HCFC–225ca, and HCFC–
225cb for the 2010–2014 control
periods. If rapid growth were to occur,
creating the need for additional amounts
of these HCFCs, EPA believes that interpollutant transfers could be used to
make adjustments. If the full amount of
allowances is not needed, then some
allowances may go unused. In
accordance with the next stepdown
under the Montreal Protocol, EPA will
issue a rule prior to the 2015 HCFC
milestone to limit aggregate production
and consumption of all HCFCs to no
more than 10 percent of the U.S.
baselines for production and
consumption. At that time, EPA plans to
consider the appropriate level of
allowances for 2015 and beyond based
on market demand and the section
605(a) restrictions on introduction into
interstate commerce and use discussed
elsewhere in this NPRM. Examples of
uses that will be limited by section
605(a) beginning in 2015 are solvent
uses and fire suppression. EPA
anticipates other changes as well. For
example, EPA’s proposed allowance
level for HCFC–123, HCFC–124, HCFC–
225ca, and HCFC–225cb does not
assume a specified level of recycling
and reclamation. For HCFCs used in
non-refrigeration applications, such as
those used as solvents (i.e., HCFC–225ca
and HCFC–225cb), the section 608 ‘‘no
venting’’ prohibition is not applicable.
HCFC–123 is used in chillers that in
some cases are replacing CFC chillers.
Given that in many cases these
appliances will last a long time, it will
be some time before significant amounts
of HCFC–123 are recovered and
recycled or reclaimed. In future
rulemakings, however, EPA may
estimate the amount of the total need for
HCFC–123 that can be met through
recycling and reclamation. As the
HCFC–123 market matures, the
refrigerant recovery, recycling, and
reclamation requirements in 40 CFR
part 82 subpart F, will result in a greater
amount of reusable HCFC–123.
Recognizing that the HCFC market will
continue to evolve, subject to the
constraints in section 605(a), EPA is
proposing to establish and apportion
baseline allowances and provide
calendar-year allowances for the control
periods 2010–2014 for these HCFCs.
EPA has established company
baselines for these four low-ODP HCFCs
by choosing each company’s highest
production and consumption years from
2005, 2006, and 2007. This is the same
approach EPA used to establish the
company baselines for HCFC–141b,
HCFC–22, and HCFC–142b in the 2003
allocation rule.
Data show that 125 percent of the
highest year’s consumption of HCFC–
123, HCFC–124, HCFC–225ca, and
HCFC–225cb for all the companies
combined equals 163 ODP-weighted
metric tons, which is slightly more than
4 percent of the total HCFC
consumption cap of 3,810 ODP tons.
EPA data also show that 125 percent
of the highest year’s production of
HCFC–123, HCFC–124, HCFC–225ca,
and HCFC–225cb for all the companies
combined equals 135 ODP-weighted
metric tons, which is slightly more than
3 percent of the total HCFC production
cap of 3,884.25 ODP tons.
EPA proposes to allocate production
allowances to the following entities for
the following amounts:
Person
Controlled substance
AGC Chemicals Americas ............................................................................................
HCFC–225ca ............................................
HCFC–225cb ............................................
HCFC–124 ................................................
HCFC–124 ................................................
DuPont ..........................................................................................................................
Honeywell .....................................................................................................................
EPA also proposes to allocate
consumption allowances to the
Controlled substance
AGC Chemicals Americas ............................................................................................
HCFC–225ca ............................................
HCFC–225cb ............................................
HCFC–124 ................................................
HCFC–124 ................................................
HCFC–123 ................................................
HCFC–123 ................................................
HCFC–124 ................................................
HCFC–124 ................................................
HCFC–124 ................................................
HCFC–123 ................................................
HCFC–124 ................................................
HCFC–123 ................................................
HCFC–124 ................................................
Arkema .........................................................................................................................
Condor Products ..........................................................................................................
Coolgas, Inc .................................................................................................................
Dupont ..........................................................................................................................
Honeywell .....................................................................................................................
ICOR .............................................................................................................................
National Refrigerants ....................................................................................................
Tulstar Products ...........................................................................................................
EPA is proposing to allocate 125
percent of each company’s baseline for
these low-ODP HCFCs for the 2010–
2014 control periods. These allocations
15:42 Dec 22, 2008
266,608
373,952
2,269,210
1,804,121
following entities for the following
amounts:
Person
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Allowances
(kg.)
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would appear as additions to the table
at § 82.16. EPA requests comments on
its proposal to grant 125 percent of
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Allowances
(kg.)
285,328
286,832
3,719
3,746
20,000
2,933,906
743,312
1,284,265
81,220
72,600
50,380
34,800
229,582
baseline to companies for these HCFCs
for the 2010–2014 control periods.
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12. What About Other HCFCs?
In addition to HCFC–141b, HCFC–22,
and HCFC–142b, as well as newly
addressed HCFC–123, HCFC–124,
HCFC–225ca, and HCFC–225cb, EPA
recognizes that the list of HCFCs in
appendix B to subpart A includes
additional substances. EPA’s proposed
allocations, based on projected 2010–
2014 need, have the effect of reserving
some room under the 2010 aggregate
HCFC cap for any HCFCs not
specifically included in §§ 82.16, 82.18,
and 82.19. Given the 4 percent of the
3,810 consumption cap EPA is
proposing to allocate for the newly
addressed HCFCs (–123, –124, –225ca
and –225cb), room under the 2010
production and consumption caps still
remains. EPA notes that some niche
applications in the U.S. use other
HCFCs, such as HCFC–21. However,
EPA is not aware of additional need for
production or import of these
substances at this time. Also, some
amount of HCFC–141b will likely
continue to be produced or imported via
the petition process during the 2010–
2014 control periods. EPA believes it is
appropriate to reserve some room in
case circumstances were to change and
users of another HCFC were to seek to
acquire an amount either by production
or by import. EPA notes that the
producer or importer would be required
to report to EPA consistent with the
existing recordkeeping and reporting
requirements. If necessary, EPA could
subsequently propose amending the
regulations to set and apportion
baselines and issue allowances for these
HCFCs. EPA requests comments on its
proposed approach of allocating
baseline allowances for HCFC–141b,
HCFC–22, HCFC–142b, HCFC–123,
HCFC–124, HCFC–225ca, and HCFC–
225cb based on the projected need for
virgin material in the U.S., which would
have the effect of not allocating
allowances for the remaining amount
under the 3,810 ODP-ton cap.
B. Does the Article 5 Allowance
Provision Change Given the
Adjustments to the Montreal Protocol?
Under the Montreal Protocol,
industrialized countries and developing
countries have different schedules for
phasing out ODS production and
consumption. Developing countries
operating under Article 5, paragraph 1
of the Montreal Protocol in most cases
have additional time in which to phase
out ODSs. Recognizing that it would be
inadvisable for developing countries to
spend their scarce resources to build
new ODS manufacturing facilities to
meet basic domestic needs for chemicals
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they would ultimately phase out, the
Parties to the Montreal Protocol decided
to permit a small amount of production
in industrialized countries, in addition
to the amounts otherwise permitted for
such countries under the relevant
phaseout schedules, for export to meet
the basic domestic needs of developing
countries. As discussed above, at the
19th Meeting of the Parties (MOP) to the
Montreal Protocol held in September
2007, the Parties agreed to a revised
phaseout schedule for both Article 5
and non-Article 5 Parties. Included with
the changes to the phaseout schedule
were changes to the amount of
production in industrialized countries
that would be permitted to meet the
basic domestic needs of Article 5
Parties. These changes were in keeping
with the more stringent phaseout
schedule for developing countries.
Previously, the Montreal Protocol had
allowed non-Article 5 countries to
produce at 15 percent of their baseline
levels for export to Article 5 countries
from 2016, the year in which Article 5
countries were required to freeze
consumption, through the terminal
phaseout in 2040. At the 19th MOP the
Parties agreed that to satisfy basic
domestic needs of Article 5 countries,
non-Article 5 Parties would be allowed
to produce up to 10 percent of baseline
levels until 2020. For the period after
2020, the Parties agreed to consider
further reduction of the production for
basic domestic needs no later than 2015
(UNEP/Ozl.Pro.19/7 Decision XIX/6:
Adjustments to the Montreal Protocol
with regard to Annex C, Group I,
substances (hydrochlorofluorocarbons)).
Section 605(d)(2) of the Clean Air Act
states that notwithstanding the
restrictions on production, use, and
introduction into interstate commerce
set forth in paragraphs (a) and (b) of that
section, EPA ‘‘may authorize the
production of limited quantities of a
class II substance in excess of the
quantities otherwise permitted under
such provisions solely for export to and
use in developing countries that are
Parties to the Montreal Protocol, as
determined by the Administrator’’ (42
U.S.C. 7671d(d)(2)). EPA’s
implementing regulation at 40 CFR
§ 82.18(a) provides for allocation of
‘‘Article 5 allowances’’ for production of
specified ODSs solely for export to
Article 5 Parties to meet those countries’
basic domestic needs. The ‘‘Article 5’’
Parties are listed at 40 CFR part 82,
subpart A, appendix E. Currently under
§ 82.18(a) an entity that is apportioned
baseline HCFC production allowances
receives an amount of Article 5
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allowances equal to 15 percent of that
production baseline.
EPA is proposing to amend § 82.18(a)
to reflect the adjustment to the Montreal
Protocol at the 19th MOP and to ensure
that the United States does not permit
a level of production to meet basic
domestic needs in Article 5 Parties that
exceeds the level specified in the
adjustments. EPA is taking this action in
accordance with section 606(a)(3) of the
Clean Air Act. EPA is also proposing
minor changes to 82.15(c) to clarify that
HCFCs produced with Article 5
allowances may be introduced into
interstate commerce if destined for
export.
Section 82.18(a)(1) currently states
that a person apportioned baseline
production allowances for specified
HCFCs is also apportioned Article 5
allowances for the specified HCFCs
equal to the following percentages of
that person’s baseline: For control
periods through 2014, 15 percent; for
control periods from 2015 through 2029,
10 percent; and for control periods from
2020 through 2039, 15 percent. While
the Montreal Protocol previously
permitted production for the basic
domestic needs of Article 5 countries
equal to 15 percent of the U.S.
production baseline for each control
period until 2040, section 605(d)(2)(B)
of the Clean Air Act requires that for the
period between 2015 and 2030 the
production for Article 5 countries be
limited to 10 percent of baseline. Thus
EPA regulations at § 82.18(a) currently
restrict Article 5 allowances to 10
percent of production baseline from
January 1, 2015, through December 31,
2029, but otherwise allow the full 15
percent previously permitted by the
Protocol.
EPA is proposing to amend § 82.18(a)
to allocate Article 5 allowances for the
HCFCs covered by this rulemaking, for
the period 2010–2019, consistent with
the recent changes to the Montreal
Protocol. Prior to 2015, exports to
Article 5 Parties of HCFC–123, HCFC–
124, HCFC–225ca, or HCFC–225cb
would not require expending Article 5
allowances.
Given that Article 2F of the Montreal
Protocol, as adjusted in September 2007,
does not provide for additional HCFC
production to meet the basic domestic
needs of Article 5 Parties past 2019,
EPA is proposing to sunset the Article
5 allowance provision for all HCFCs at
the end of 2019 in the absence of further
adjustments to the Protocol. Decision
XIX/6 paragraph 14 states ‘‘In order to
satisfy basic domestic needs [the
Parties] agree to allow for up to 10% of
baseline until 2020, and for the period
after that, to consider no later than 2015
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further reductions of production for
basic domestic needs.’’ If the Parties
were to adjust the basic domestic needs
provisions of the Protocol to permit
continued production for such needs
past 2019, EPA would evaluate that
adjustment and consider issuing a
proposed regulation to extend the
availability of Article 5 allowances for
basic domestic needs to the extent
consistent with the Clean Air Act. Any
such proposed regulations would
include production levels and schedules
that were at least as stringent as those
specified in the Montreal Protocol, as
adjusted.
EPA requests comments on its
proposed revisions to § 82.18(a).
C. How Does EPA Interpret ‘‘Introduce
Into Interstate Commerce or Use’’?
Section 605(a) is titled ‘‘Restriction of
use of class II substances’’ and reads:
‘‘Effective January 1, 2015, it shall be
unlawful for any person to introduce
into interstate commerce or use any
Class II substance unless such
substance—
(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.
As used in this subsection, the term
‘refrigerant’ means any class II
substance used for heat transfer in a
refrigerating system.’’
Section 605(a) is self-effectuating,
banning the introduction into interstate
commerce and use of HCFCs by its own
terms. In section 605(c), however,
Congress directed EPA to promulgate
regulations restricting the use of class II
substances in accordance with section
605. In today’s action, EPA is proposing
to complete its implementation of the
section 605 provisions on use of class II
substances. EPA is also proposing
regulatory language to reflect the section
605 provisions on introduction into
interstate commerce of class II
substances.
As discussed earlier in this notice, the
provisions governing HCFC–22 and
HCFC–142b promulgated as part of the
1993 phaseout rule were intended ‘‘to
prohibit the use of the chemicals (virgin
material only) for any use except as a
feedstock or as a refrigerant in existing
equipment as of January 1, 2010’’ (58 FR
15028). As promulgated, however, the
regulatory prohibitions did not control
use directly, but instead banned
production and import for most uses.
EPA is proposing to add the direct use
prohibitions contemplated in the 1993
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phaseout rule as well as the
corresponding prohibitions on
introduction into interstate commerce
contained in section 605(a). Consistent
with the schedule adopted in the 1993
phaseout rule, the section 605(a) use
and interstate commerce restrictions
would apply to HCFC–22 and HCFC–
142b beginning in 2010 and to all other
HCFCs beginning in 2015.8 The
restrictions on production and import,
both in general and for particular uses,
that were promulgated in 1993 are at 40
CFR 82.16(b)–(g). EPA is not proposing
to change these provisions in this
action. However, EPA is further
implementing section 605(a) by
proposing direct restrictions on use and
introduction into interstate commerce to
be codified at § 82.15 and by clarifying
its interpretation of the statutory
requirements.
Since the promulgation of the 2003
allocation rule, EPA has received
questions from stakeholders regarding
the Agency’s interpretations of section
605(a). Based on these questions, EPA
has decided to include in this proposed
rule a discussion of how it interprets
that section, particularly the terms
‘‘introduction into interstate commerce’’
and ‘‘use.’’ EPA is proposing to
promulgate a definition of interstate
commerce to facilitate the
implementation of section 605(a).
Section 605(a) includes the phrase
‘‘introduction into interstate
commerce.’’ Section 611 (Labeling)
contains a similar phrase, noting that
certain products shall not be
‘‘introduced into interstate commerce’’
unless the product bears a clearly
legible and conspicuous warning label.
EPA’s definition of interstate commerce
for section 611 purposes appears at 40
CFR 82.104(n):
Interstate Commerce means the
distribution or transportation of any product
between one state, territory, possession or the
District of Columbia, and another state,
territory, possession or the District of
Columbia, or the sale, use or manufacture of
any product in more than one state, territory,
possession or District of Columbia. The entry
points for which a product is introduced into
interstate commerce are the release of a
product from the facility in which the
product was manufactured, the entry into a
warehouse from which the domestic
manufacturer releases the product for sale or
distribution, and at the site of United States
customs clearance.
8 The petition process for HCFC–141b exemption
allowances at 82.16(h) would sunset in 2015, since
HCFC–141b is not used as a refrigerant and thus
does not meet the criteria established by 605(a) for
an exception from the statutory ban on use. EPA
intends to revise § 82.16(h) when it addresses the
control periods 2015–2019.
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After considering this regulatory
definition, and noting the similarities in
the statutory language, EPA proposes to
amend § 82.3 to include a definition of
‘‘interstate commerce’’ that is identical
to the definition at § 82.104(n), except
that the phrase ‘‘controlled substance’’
would appear where the § 82.104(n)
definition uses the term ‘‘product.’’ This
is because section 605(a) addresses
substances rather than products. Adding
a definition of interstate commerce to
§ 82.3 will clarify the applicability of
the section 605(a) provisions. Choosing
a definition that is already wellestablished in the labeling program will
minimize stakeholder confusion. EPA
requests comments on adding this
definition of interstate commerce to
subpart A.
EPA notes that under this definition,
‘‘introduction into interstate commerce’’
would include release of HCFCs by the
domestic manufacturer for distribution
and transport prior to export. The
section 605(a) ban thus has relevance to
the export of HCFCs—limiting exports
to HCFCs that are ‘‘used, recovered, and
recycled’’ (section 605(a)(1)); HCFCs
that are destined for transformation
(section 605(a)(2)); HCFCs that will be
used as a refrigerant in appliances
manufactured before the date specified
in the regulations (section 605(a)(3));
and HCFCs that will be exported to
Article 5 Parties (section 605(d)(2)). As
a result, HCFC exports to non-Article 5
Parties would be limited as of January
1, 2010, or January 1, 2015, depending
on the specific HCFC.
In addition to banning ‘‘introduction
into interstate commerce’’ of HCFCs,
section 605(a) also bans ‘‘use,’’ subject
to three statutory exceptions that inform
EPA’s understanding of the term ‘‘use.’’
While these exceptions apply to the
‘‘interstate commerce’’ ban as well as
the ‘‘use’’ ban, the discussion below
focuses on the ‘‘use’’ aspects of the
exceptions. EPA is proposing to
interpret the ‘‘use’’ ban as applying to
the use of HCFCs in manufacturing and
servicing HCFC products.
The first exception, which appears at
section 605(a)(1), applies to class II
substances that have been ‘‘used,
recovered, and recycled.’’ This
exception confirms EPA’s
understanding of the use ban as limited
to the manufacture and servicing of
HCFC products. If the ban applied to
use of HCFCs by a consumer, such
‘‘use’’ might include the continued
operation of an appliance (e.g., a
residential air conditioner) where an
HCFC acts as the refrigerant. Under this
broad definition of ‘‘use,’’ there would
be an incentive for consumers to hire
servicing technicians to recover the
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HCFCs from appliances already in their
homes and businesses, to recycle the
HCFCs for reuse, and to charge the
HCFCs back into the same appliances.
These steps should not be necessary for
continued operation of installed
equipment. However, by taking these
steps, consumers could avail themselves
of the exception for ‘‘used, recovered,
and recycled’’ substances at section
605(a)(1). There would be no
environmental benefit to following such
a procedure. There could even be an
environmental detriment, given the
potential for losses of refrigerant during
the recovery and recycling process. EPA
does not believe that Congress intended
such a result. Moreover, EPA believes
that Congress intended to permit the
continued use of previously
manufactured appliances, as indicated
by the third exception to the use ban
(section 605(a)(3)). Thus, EPA is not
proposing an interpretation that would
result in shortening the useful lifetime
of appliances that were manufactured
prior to the effective date of the use
restriction. EPA concludes that the
section 605(a) ‘‘use’’ ban does not apply
to a consumer’s operation of equipment
that contains HCFCs. Rather, it applies
to use during manufacture and servicing
of equipment. EPA believes that
Congress meant for the section 605(a)(1)
exception to allow the use of ‘‘used,
recovered, and recycled’’ HCFCs in
appropriate instances by servicing
technicians, reclaimers, and appliance
manufacturers.
Section 605(a)(2) refers to HCFCs that
are ‘‘used and entirely consumed
(except for trace quantities) in the
production of other chemicals.’’ Similar
language appears as an exception to the
definition of ‘‘production’’ at section
601(11). This type of use is referred to
in EPA’s regulations as
‘‘transformation’’ (see the definition of
‘‘transform’’ at 40 CFR 82.3). The
current phaseout schedule for HCFC
production and consumption already
includes a transformation exception
within § 82.16. EPA intends to
implement the transformation exception
in section 605(a)(2) consistent with the
transformation exception to the HCFC
production phaseout.
Section 605(a)(3) provides an
exception for HCFCs that are ‘‘used as
a refrigerant in appliances manufactured
prior to January 1, 2020.’’ EPA reads this
exception as allowing appliances
manufactured before the specified date
to be serviced with virgin HCFCs. This
is consistent with the legislative history
of the exception. The predecessor to
section 605(a)(3) in the Senate bill was
an exception for ‘‘other regulated
substances’’ (such as HCFCs) that are
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‘‘used to maintain and service
household appliances or commercial
refrigeration units manufactured prior to
January 1, 2015.’’ The House
amendment contained identical
language. While the language that
emerged in the Conference Agreement is
less specific, we can infer that this
exception was intended to address, at a
minimum, maintenance and servicing
needs.
As noted above, EPA interprets the
605(a) use ban to cover initial charges as
well as maintenance and servicing. As
written, the section 605(a)(3) exception
would permit some newly
manufactured appliances (i.e., those
manufactured prior to January 1, 2020)
to be charged with virgin HCFCs
following the effective date of the use
ban. In the 1993 phaseout rule,
however, EPA banned production and
import of HCFC–22 and HCFC–142b,
effective January 1, 2010, for use in
appliances manufactured after 2009.
EPA also indicated that it intended to
ban use of virgin HCFC–22 and HCFC–
142b in such appliances. Consistent
with decisions made in the 1993 rule,
EPA is proposing, for HCFC–22 and
HCFC–142b, to apply the section
605(a)(3) exception only to the use of
these HCFCs in appliances
manufactured before 2010. Such use
would consist of servicing and
maintenance of these appliances. EPA
notes that servicing could entail a wide
range of activities including replacing
parts or components. For the low ODPrefrigerants covered by 82.16(d),
however, EPA is proposing to apply the
section 605(a)(3) exception to the use of
HCFCs in equipment manufactured
before January 1, 2020, which would
allow initial charging of equipment for
a limited period as well as servicing and
maintenance uses. For those
refrigerants, 82.16(d) bans production
and import effective January 1, 2015 for
use in appliances manufactured after
2019.
EPA notes that the exception at
section 605(a)(3) limits introduction
into interstate commerce and use to
situations where the HCFC: ‘‘is used as
a refrigerant in appliances manufactured
prior to’’ the specified date. Section 601
defines appliance as ‘‘any device which
contains and uses a class I or class II
substance as a refrigerant and which is
used for household or commercial
purposes, including any air conditioner,
refrigerator, chiller, or freezer.’’ EPA
recognizes many devices meet the
section 601 definition of appliance. For
example, commercial refrigeration
includes the retail food and cold storage
sectors. Industrial process refrigeration
includes customized appliances used in
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the chemical, pharmaceutical,
petrochemical and manufacturing
industries. Other types of appliances
include household refrigerators and
freezers; chillers; water coolers; vending
machines; residential and light
commercial heat pumps; residential
dehumidifiers; unitary systems; and
commercial ice machines. Under the
SNAP program and regulations
promulgated under § 608, EPA has
recognized the differences in these
appliances and in some cases has found
substitute refrigerants acceptable for
some appliances but not others or
established different control thresholds
such as different leak rate requirements.
For the purposes of this action, EPA has
considered the definition of appliance
carefully, particularly evaluating at
what point a device becomes a
manufactured appliance. EPA believes
that the difference in types of
appliances affects the point when
manufacture is complete.
Through this action, EPA is providing
an interpretation of section 605(a) under
which air-conditioning and refrigeration
appliances are ‘‘manufactured’’ when
the refrigerant loop is completed, the
appliance can function, the appliance
holds the complete and proper charge,
and is ready for use for its intended
purposes. For refrigerators and room airconditioners, manufacture may be
complete while the appliance is still at
a manufacturing facility. For instance, if
such an appliance has been pre-charged
with the desired amount of refrigerant,
has gone through the entire
manufacturing line so that all
mechanical, electrical, labeling and
painting/marking procedures are
complete, and is ready to be packaged
and shipped, and is a ‘‘stand-alone’’
piece of equipment (i.e., it only needs to
be plugged into an electrical outlet and
turned on to function properly), then
EPA would consider the appliance as
‘‘manufactured.’’ The situation differs,
however, for other appliances, such as
commercial refrigeration and industrial
process refrigeration, involving more
complex installation processes. Such
devices are field charged with
refrigerant; the refrigerant loop typically
is completed onsite, and—particularly
with industrial process refrigeration—
the parts are custom-built. EPA would
consider these field-charged appliances
‘‘manufactured’’ at the point installation
of all parts is completed and fully
charged refrigerant (whether or not the
appliance had started operation). For
some appliances, such as condensing
(outside) units for split-system air
conditioners, refrigerant charge is often
included in the product during the
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Federal Register / Vol. 73, No. 247 / Tuesday, December 23, 2008 / Proposed Rules
section 605(a). Export production
allowances allow an HCFC that is
subject to a domestic phaseout to be
produced for export to Parties that
continue to allow imports of that
substance (40 CFR 82.18(b)). Currently,
entities that hold baseline production
allowances for HCFC–141b are allocated
export production allowances equal to
100 percent of their baseline production
allowances. EPA is proposing to sunset
this provision on December 31, 2009, in
order to avoid a conflict with the section
605(a) restrictions on use and
introduction into interstate commerce.
Under the proposed interstate
commerce definition, ‘‘introduction into
interstate commerce’’ would include
release of HCFCs by the domestic
manufacturer for distribution and
transport prior to export. EPA is not
proposing to allocate export production
allowances for any other HCFCs. EPA
seeks comment on the sunset of
provisions for export production
allowances.
manufacturing process but then is
typically adjusted in the field to account
for different line sizes and indoor unit
configurations. EPA would consider the
‘‘manufacture’’ of this type of appliance
similar to that for field-charged
equipment; that is, manufacture would
not be complete until the device is
installed in the field, connected with
the indoor unit, and charged to the
proper level.
EPA does not interpret ‘‘use’’ to
include destruction, recovery for
disposal, discharge consistent with all
other regulatory requirements or other
similar actions where the substance is
part of a disposal chain. At the point
disposal-related actions occur, other
statutory and regulatory provisions
generally govern. For example, Congress
addressed the issue of disposal under
section 608. EPA has promulgated
regulations to implement section 608 for
appliances: These safe disposal
requirements are codified at 40 CFR part
82 subpart F. In some instances, HCFCs
may need to be introduced into
interstate commerce in order to reach an
appropriate destruction facility.
Consistent with its interpretation of
‘‘use,’’ EPA is interpreting the interstate
commerce prohibition to exclude
introduction into interstate commerce
for the purpose of destruction.
As noted above, the current regulatory
provisions already preclude production
or import of HCFC–22 and HCFC–142b
in 2010 and beyond for purposes that
are not exempted at § 82.16(c) consistent
with section 605(a).9 However, EPA is
proposing through this action to amend
§ 82.15 to add prohibitions that
specifically preclude any person from
introducing into interstate commerce or
using (according to the interpretations
above) any HCFCs for purposes that are
not consistent with section 605. EPA
believes that this is appropriate because
section 605(a) specifically bans use and
introduction into interstate commerce.
In addition, under the current regulatory
structure the prohibitions apply to the
producer or importer of the HCFC
compounds. The provisions EPA is
proposing to add to the regulations
would apply to manufacturers of
appliances and other HCFC products, as
well as anyone who services such
products. EPA requests comments on
adding these prohibitions and on its
interpretation of section 605(a).
Finally, EPA is proposing revisions to
its regulations on export production
allowances to ensure consistency with
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order (EO) 12866
(58 FR 51735, October 4, 1993), this
action is a ‘‘significant regulatory
action.’’ Accordingly, EPA submitted
this action to the Office of Management
and Budget (OMB) for review under EO
12866 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 NPRM. 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.
9 As discussed earlier in this action, there is an
additional exception for production to meet the
• The 2007 Memorandum
Preliminary estimates of the incremental
cost of the HCFC phaseout in Article 5
countries.
• 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.
basic domestic needs of Article 5 countries,
consistent with section 605(d).
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IV. Statutory and Executive Order
Reviews
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Copies of these documents and a
summary memorandum 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 requirements and through this
action is not proposing to amend those
provisions. However, 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.
For purposes of assessing the impacts
of this proposal on small entities, 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-for-profit
enterprise which is independently
owned and operated and is not
dominant in its field.
This proposal will affect the following
categories:
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Federal Register / Vol. 73, No. 247 / Tuesday, December 23, 2008 / Proposed Rules
Category
NAICS code
SIC code
Chlorofluorocarbon gas manufacturing ..................
325120
2869
Chlorofluorocarbon gas importers ..........................
325120
2869
Chlorofluorocarbon gas exporters ..........................
325120
2869
Manufacturers of air conditioners and refrigerators
333415
Importers of air conditioners and refrigerators .......
333415
After considering the economic
impacts of the proposed rule on small
entities, I certify that this action will not
have a significant economic impact on
a substantial number of small entities.
EPA is not proposing to change the
methodology for the 2010–2014 control
periods. Instead, EPA is continuing to
allocate production and consumption
allowances using the same approach
currently used for control periods 2003–
2009. Thus the 13 small businesses
eligible for allowances for HCFC–22 and
HCFC–142b identified in that
rulemaking (68 FR 2845) are still
eligible for allowances under this rule.
In addition, small businesses eligible for
HCFC–123, HCFC–124, HCFC–225ca,
and HCFC–225cb using the same
methodology, will also be eligible for
allowances. EPA is not proposing any
changes to the recordkeeping or
reporting provisions and thus will not
have any impact on the burden to these
businesses.
While EPA does not believe this
proposal will have a significant
economic impact on a substantial
number of small entities, nonetheless,
EPA continues to try to reduce further
any impacts on small entities. With
respect to the allowance allocation
system as a whole, EPA is proposing to
continue to provide flexibility.
Consistent with the methodology for
establishing baselines for HCFC–141b,
HCFC–22, and HCFC–142b, while small
entities will be on the same footing as
larger entities, EPA is again is proposing
to use the highest year of consumption.
EPA is also to limit consideration of
company-specific baseline adjustments
to reflect permanent inter-company or
inter-pollutant transfers made prior to
June 16, 2008 as discussed elsewhere in
the preamble to avoiding skewing
baselines to entities with ample
resources or access to information. EPA
also believes that the ability to transfer
allowances among entities provides the
greatest flexibility for small entities to
manage their allocation. As noted in the
2003 allocation (68 FR 2846), unlike
with the class I substances, there is no
restriction to limit inter-pollutant
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3585
Examples of regulated entities
Chlorodifluoromethane manufacturers; Dichlorofluoroethane
manufacturers; Chlorodifluoroethane manufacturers.
Chlorodifluoromethane importers; Dichlorofluoroethane importers; Chlorodifluoroethane importers.
Chlorodifluoromethane exporters; Dichlorofluoroethane exporters; Chlorodifluoroethane exporters.
Air-Conditioning Equipment and Commercial and Industrial
Refrigeration Equipment Manufacturing.
Air-Conditioning Equipment and Commercial and Industrial
Refrigeration Equipment Manufacturing.
transfers to groups of substances. Both
inter-pollutant and inter-company
transfers of allowances are possible,
either on a calendar-year or permanent
basis. A small entity can opt for shortterm or long-term decisions concerning
the allowances it holds after evaluating
its place in the overall market. EPA
continues to be interested in the
potential impacts of the proposed rule
on small entities and welcomes
comments on issues related to such
impacts.
D. Unfunded Mandates Reform Act
This rule does not contain a Federal
mandate that may result in expenditures
of $100 million or more for State, local,
and tribal governments, in the aggregate,
or the private sector in any one year.
The requirements already established at
40 CFR part 82 subpart A already govern
the production, import, and export of
ODS. The regulatory changes for the
next major milestone in the general
phaseout continue to implement the
same general framework previously
established. EPA does not anticipate
that this proposed rulemaking will have
any significant direct impacts or State,
local and tribal governments or private
sector entities. Thus, this rule is not
subject to the requirements of sections
202 or 205 of UMRA.
This rule 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
proposed rule would apportion
production and consumption
allowances and establish baselines for
private entities, not small governments.
E. Executive Order 13132: Federalism
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires EPA to develop an
accountable process to ensure
‘‘meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications.’’ ‘‘Policies that have
federalism implications’’ is defined in
the Executive Order to include
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78701
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 proposed rule does not have
federalism implications. It will not have
substantial direct effects on the States,
on the relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. Today’s
proposal is expected to primarily affect
producers, importers, and exporters of
HCFCs. Thus, the requirements of
section 6 of the Executive Order do not
apply. In the spirit of Executive Order
13132, and consistent with EPA policy
to promote communications between
EPA and State and local governments,
EPA specifically solicits comment on
this proposed rule from State and local
officials.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249, November 9, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’ This proposed rule does
not have tribal implications, as specified
in Executive Order 13175. This proposal
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 proposed rule.
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
This action is not subject to EO 13045
(62 F.R. 19885, April 23, 1997) because
it is not economically significant as
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Federal Register / Vol. 73, No. 247 / Tuesday, December 23, 2008 / Proposed Rules
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) Whieman 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. The public is invited to submit or
identify peer-reviewed studies and data,
of which EPA may not be aware, that
assess results of early-life exposure to
UV radiation.
This action proposes to reduce the
potential continued use of Class II
controlled substances and the emissions
of such substances. It implements the
United States 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 United States can take to complete
the overall phaseout of ODS and further
decrease impacts on children’s health
from stratospheric ozone depletion. EPA
requests comments regarding the
impacts of this proposal on the
continued efforts to protect children’s
health.
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H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This rule is not a ‘‘significant energy
action’’ as defined in Executive Order
13211, ‘‘Actions Concerning Regulations
That Significantly Affect Energy Supply,
Distribution, or Use’’ (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 proposed regulation predominately
impacts HCFC production, imports,
exports, and trades. The Agency has
concluded that this rule is not likely to
have any adverse energy effects.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law No.
104–113, 12(d) (15 U.S.C. 272 note)
directs EPA to use voluntary consensus
standards in its regulatory activities
unless to do so would be inconsistent
with applicable law or otherwise
impractical. Voluntary consensus
standards are technical standards (e.g.,
materials specifications, test methods,
sampling procedures, and business
practices) that are developed or adopted
by voluntary consensus standards
bodies. The NTTAA directs EPA to
provide Congress, through OMB,
explanations when the Agency decides
not to use available and applicable
voluntary consensus standards. This
proposed rulemaking does not involve
technical standards. Therefore, EPA is
not considering 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 United States.
EPA has determined that this
proposed rule will not have
disproportionately high and adverse
human health or environmental effects
on minority or low-income populations
because it increases the level of
environmental protection for all affected
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populations without having any
disproportionately high and adverse
human health or environmental effects
on any population, including any
minority or low-income population. By
allocating allowances for HCFCs and
thus restricting the amount of HCFCs
available as of January 1, 2010, this rule
avoids emissions of these ozonedepleting substances, lessening 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,
Chlorofluorocarbons, Exports,
Hydrochlorofluorocarbons, Imports,
Reporting and recordkeeping
requirements.
Dated: December 11, 2008.
Stephen L. Johnson,
Administrator.
40 CFR part 82 is proposed to be
amended 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–
7671(q).
Subpart A—Production and
Consumption Controls
2. Amend § 82.3 by adding in
alphabetical order the definition of
‘‘Interstate Commerce’’ to read as
follows:
§ 82.3 Definitions for Class I and Class II
Controlled Substances.
*
*
*
*
*
Interstate Commerce means the
distribution or transportation of any
controlled substance between one state,
territory, possession or the District of
Columbia, and another state, territory,
possession or the District of Columbia,
or the sale, use or manufacture of any
controlled substance in more than one
state, territory, possession or District of
Columbia. The entry points for which a
controlled substance is introduced into
interstate commerce are the release of a
controlled substance from the facility in
which the controlled substance was
manufactured, the entry into a
warehouse from which the domestic
manufacturer releases the controlled
substance for sale or distribution, and at
the site of United States customs
clearance.
*
*
*
*
*
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3. Amend § 82.15 by revising
paragraph (c) and adding paragraph (g)
to read as follows:
§ 82.15 Prohibitions for Class II Controlled
Substances.
*
*
*
*
*
(c) Production with Article 5
allowances. No person may introduce
into U.S. interstate commerce any class
II controlled substance produced with
Article 5 allowances, except for export
to an Article 5 Party as listed in
Appendix E of this subpart. Every
kilogram of a class II controlled
substance produced with Article 5
allowances that is introduced into
interstate commerce other than for
export to an Article 5 Party constitutes
a separate violation under this subpart.
No person may export any class II
controlled substance produced with
Article 5 allowances to a non-Article 5
Party. Every kilogram of a class II
controlled substance that was produced
with Article 5 allowances that is
exported to a non-Article 5 Party
constitutes a separate violation under
this subpart.
*
*
*
*
*
(g) Introduction into interstate
commerce or use. (1) Effective January
1, 2010, no person may introduce into
interstate commerce or use HCFC–141b
(unless used, recovered, and recycled)
for any purpose except for use in a
process resulting in its transformation or
Control period
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
2013
2014
*
its destruction; for export to Article 5
Parties under § 82.18(a); for HCFC–141b
exemption needs; as a transshipment or
heel; or for exemptions permitted in
§ 82.15(f).
(2) Effective January 1, 2010, no
person may introduce into interstate
commerce or use HCFC–22 or HCFC–
142b (unless used, recovered, and
recycled) for any purpose other than for
use in a process resulting in its
transformation or its destruction, for use
as a refrigerant in equipment
manufactured before January 1, 2010;
for export to Article 5 Parties under
§ 82.18(a); as a transshipment or heel; or
for exemptions permitted in § 82.15(f).
(3) Effective January 1, 2015, no
person may introduce into interstate
commerce or use HCFC–141b (unless
used, recovered, and recycled) for any
purpose other than for use in a process
resulting in its transformation or its
destruction; for export to Article 5
Parties under § 82.18(a), as a
transshipment or heel; or for
exemptions permitted in § 82.15(f).
(4) Effective January 1, 2015, no
person may introduce into interstate
commerce or use any class II controlled
substance not governed by paragraphs
(g)(1) through (3) of this section (unless
used, recovered, and recycled) for any
purpose other than for use in a process
resulting in its transformation or its
destruction; for use as a refrigerant in
equipment manufactured before January
HCFC–141b
.....................................................
.....................................................
.....................................................
.....................................................
.....................................................
.....................................................
.....................................................
.....................................................
.....................................................
.....................................................
.....................................................
.....................................................
HCFC–22
0
0
0
0
0
0
0
0
0
0
0
0
100
100
100
100
100
100
100
35.2
35.2
35.2
35.2
35.2
1, 2020; for export to Article 5 Parties
under § 82.18(a); as a transshipment or
heel; or for exemptions permitted in
§ 82.15(f).
(5) Effective January 1, 2030, no
person may introduce into interstate
commerce or use any class II controlled
substance (unless used, recovered, and
recycled) for any purpose other than for
use in a process resulting in its
transformation or its destruction; for
export to Article 5 Parties under
§ 82.18(a); as a transshipment or heel; or
for exemptions permitted in § 82.15(f).
(6) Effective January 1, 2040, no
person may introduce into interstate
commerce or use any class II controlled
substance (unless used, recovered, and
recycled) for any purpose other than for
use in a process resulting in its
transformation or its destruction, as a
transshipment or heel, or for
exemptions permitted in § 82.15(f).
4. Revise § 82.16(a) to read as follows:
§ 82.16 Phaseout Schedule of Class II
Controlled Substances.
(a) In each control period as indicated
in the following table, 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:
HCFC–142b
HCFC–123
HCFC–124
HCFC–
225ca
HCFC–
225cb
100
100
100
100
100
100
100
4.9
4.9
4.9
4.9
4.9
....................
....................
....................
....................
....................
....................
....................
125
125
125
125
125
....................
....................
....................
....................
....................
....................
....................
125
125
125
125
125
....................
....................
....................
....................
....................
....................
....................
125
125
125
125
125
....................
....................
....................
....................
....................
....................
....................
125
125
125
125
125
§ 82.17 Apportionment of Baseline
Production Allowances for Class II
Controlled Substances.
*
*
*
*
5. Revise § 82.17 to read as follows:
Effective January 1, 2010, the
following persons are apportioned
baseline production allowances for
HCFC–22, HCFC–141b, HCFC–142b,
HCFC–123, HCFC–124, HCFC–225ca,
and HCFC–225cb, as set forth in the
following table:
Person
Controlled substance
AGC Chemicals Americas ............................................................................................
HCFC–225ca ............................................
HCFC–225cb ............................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–142b ..............................................
HCFC–22 ..................................................
HCFC–124 ................................................
Arkema .........................................................................................................................
DuPont ..........................................................................................................................
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E:\FR\FM\23DEP1.SGM
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Allowances
(kg.)
266,608
373,952
46,692,336
24,647,925
484,369
42,638,049
2,269,210
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Person
Controlled substance
Honeywell .....................................................................................................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–142b ..............................................
HCFC–124 ................................................
HCFC–22 ..................................................
HCFC–142b ..............................................
MDA Manufacturing ......................................................................................................
Solvay Solexis ..............................................................................................................
6. Revise § 82.18(a) and (b) to read as
follows:
§ 82.18 Availability of Production in
Addition to Baseline Production Allowances
for Class II Controlled Substances.
(a) Article 5 allowances.
(1) Effective January 1, 2003, a person
apportioned baseline production
allowances for HCFC–141b, HCFC–22,
or HCFC–142b under § 82.17 is also
apportioned Article 5 allowances, equal
to 15 percent of their baseline
production allowances, for the specified
HCFC for each control period up until
December 31, 2009, to be used for the
production of the specified HCFC for
export only to foreign states listed in
Appendix E to this subpart.
(2) Effective January 1, 2010, a person
apportioned baseline production
allowances under § 82.17 for HCFC–
141b, HCFC–22, or HCFC–142b is also
apportioned Article 5 allowances, equal
to 10 percent of their baseline
production allowances, for the specified
HCFC for each control period up until
December 31, 2019, to be used for the
production of the specified HCFC for
export only to foreign states listed in
Appendix E to this subpart.
(3) Effective January 1, 2015, a person
apportioned baseline production
allowances under § 82.17 for HCFC–123,
HCFC–124, HCFC–225ca, and HCFC–
225cb is also apportioned Article 5
allowances, equal to 10 percent of their
baseline production allowances, for the
specified HCFC for each control period
up until December 31, 2019, to be used
for the production of the specified
HCFC for export only to foreign states
listed in Appendix E to this subpart.
(b) Export Production Allowances.
(1) Effective January 1, 2003, a person
apportioned baseline production
§ 82.19 Apportionment of Baseline
Consumption Allowances for Class II
Controlled Substances.
(a) Effective January 1, 2010, the
following persons are apportioned
baseline consumption allowances for
HCFC–22, HCFC–141b, HCFC–142b,
HCFC–123, HCFC–124, HCFC–225ca,
and HCFC–225cb, as set forth in the
following table:
Controlled substance
ABCO Refrigeration Supply .........................................................................................
AGC Chemicals Americas ............................................................................................
HCFC–22 ..................................................
HCFC–225ca ............................................
HCFC–225cb ............................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–142b ..............................................
HCFC–124 ................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–124 ................................................
HCFC–141b ..............................................
HCFC–141b ..............................................
HCFC–123 ................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–142b ..............................................
HCFC–123 ................................................
HCFC–124 ................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–142b ..............................................
HCFC–124 ................................................
HCFC–141b ..............................................
HCFC–124 ................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–123 ................................................
Arkema .........................................................................................................................
Automatic Equipment Sales .........................................................................................
Condor Products ..........................................................................................................
Continental Industrial Group ........................................................................................
Coolgas, Inc .................................................................................................................
Coolgas Investment Property .......................................................................................
Discount Refrigerants ...................................................................................................
Dupont ..........................................................................................................................
Full Circle .....................................................................................................................
H.G. Refrigeration Supply ............................................................................................
Honeywell .....................................................................................................................
ICC Chemical Corp ......................................................................................................
ICOR .............................................................................................................................
Ineos Fluor Americas ...................................................................................................
Kivlan & Company ........................................................................................................
MDA Manufacturing ......................................................................................................
Mondy Global ...............................................................................................................
National Refrigerants ....................................................................................................
VerDate Aug<31>2005
15:42 Dec 22, 2008
Jkt 217001
PO 00000
Frm 00044
Fmt 4702
Sfmt 4702
37,378,252
28,705,200
2,417,534
1,804,121
2,383,835
6,541,764
allowances for HCFC–141b under
§ 82.17 is also apportioned export
production allowances, equal to 100
percent of their baseline production
allowances, for HCFC–141b for each
control period up until December 31,
2009 to be used for the production of
HCFC–141b for export only, in
accordance with this section.
(2) [Reserved]
*
*
*
*
*
7. Revise § 82.19 to read as follows:
Person
Altair Partners ...............................................................................................................
Allowances
(kg.)
E:\FR\FM\23DEP1.SGM
23DEP1
Allocation (kg)
279,366
285,328
286,832
302,011
48,637,642
25,405,570
483,827
3,719
54,088
74,843
3,746
20,315
16,097,869
20,000
590,737
375,328
994
38,814,862
9,049
52,797
2,933,906
743,312
14,865
40,068
35,392,492
20,749,489
1,315,819
1,284,265
81,225
81,220
2,546,305
2,081,018
2,541,545
281,824
5,528,316
72,600
Federal Register / Vol. 73, No. 247 / Tuesday, December 23, 2008 / Proposed Rules
Person
Controlled substance
Refricenter of Miami .....................................................................................................
Refricentro ....................................................................................................................
R-Lines .........................................................................................................................
Saez Distributors ..........................................................................................................
Solvay Fluorides ...........................................................................................................
Solvay Solexis ..............................................................................................................
Tulstar Products ...........................................................................................................
(b) [Reserved]
[FR Doc. E8–29965 Filed 12–22–08; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 82
[EPA–HQ–OAR–2007–0163; FRL–8752–6]
RIN 2060–AH67
Protection of Stratospheric Ozone:
Ban on the Sale or Distribution of PreCharged Appliances
AGENCY: Environmental Protection
Agency [EPA].
ACTION: Proposed rule.
SUMMARY: EPA is proposing to ban the
sale or distribution of air-conditioning
and refrigeration appliances containing
HCFC–22, HCFC–142b, or blends
containing one or both of these
substances, beginning January 1, 2010.
In addition, EPA is proposing to extend
these requirements to air-conditioning
and refrigeration appliances that are
suitable only for use with newly
produced HCFC–22, HCFC–142b, or
blends containing one or both of these
controlled substances as the refrigerant,
and pre-charged appliance parts. We are
proposing these restrictions to protect
stratospheric ozone.
DATES: Comments must be received on
or before January 22, 2009, unless a
public hearing is requested. Comments
must then be received on or before
February 6, 2009. 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 2, 2009. If a
hearing is held, it will take place on
January 7, 2009.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2007–0163, by one of the
following methods:
• https://www.regulations.gov: Follow
the on-line instructions for submitting
comments.
VerDate Aug<31>2005
15:42 Dec 22, 2008
Jkt 217001
HCFC–124 ................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–22 ..................................................
HCFC–141b ..............................................
HCFC–142b ..............................................
HCFC–141b ..............................................
HCFC–123 ................................................
HCFC–124 ................................................
• E-mail: a-and-r-Docket@epa.gov.
• Fax: 202–566–1741.
• Mail: Docket #, 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–2003–0163, Air and Radiation
Docket at EPA West, 1301 Constitution
Avenue, NW., Room B108, Mail Code
6102T, Washington, DC 20460. 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–2007–
0163. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
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 https://
www.regulations.gov or e-mail. The
https://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 e-mail comment directly
to EPA without going through https://
www.regulations.gov your e-mail
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
PO 00000
Frm 00045
Fmt 4702
Sfmt 4702
78705
Allocation (kg)
50,380
381,293
45,979
63,172
37,936
3,781,691
3,940,115
194,536
89,913
34,800
229,582
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 https://
www.epa.gov/epahome/dockets.htm.
FOR FURTHER INFORMATION CONTACT:
Cindy Axinn Newberg, EPA,
Stratospheric Protection Division, Office
of Atmospheric Programs, Office of Air
and Radiation (6205J), 1200
Pennsylvania Avenue, NW.,
Washington, DC 20460, (202) 343–9729,
newberg.cindy@epa.gov.
SUPPLEMENTARY INFORMATION: (1) Under
the Montreal Protocol on Substances
that Deplete the Ozone Layer (Protocol),
as amended, the U.S. and other
industrialized countries that are Parties
to the Protocol have agreed to limit
production and consumption of
hydrochlorofluorocarbons (HCFCs) and
to phase out consumption in a step-wise
fashion over time, culminating in a
complete phaseout in 2030. Title VI of
the Clean Air Act Amendments of 1990
(CAAA) authorizes EPA to promulgate
regulations to manage the consumption
and production of HCFCs until the total
phaseout in 2030. EPA promulgated
final regulations establishing an
allowance tracking system for HCFCs on
January 21, 2003 (68 FR 2820). These
regulations were amended on June 17,
2004 (69 FR 34024) and July 20, 2006
(71 FR 41163). This action proposes a
ban on sale or distribution of airconditioning and refrigeration
appliances that contain HCFC–22,
HCFC–142b, or blends containing one or
both of these controlled substances. In
addition, EPA is proposing to extend
these requirements to air-conditioning
and refrigeration appliances that are
suitable only for use with newly
produced HCFC–22, HCFC–142b, or
blends containing one or both of these
controlled substances as the refrigerant.
(2) Abbreviations and Acronyms Used
in This Document.
CAAA—Clean Air Act Amendments of
1990
CFC—chlorofluorocarbon
HCFC—hydrochlorofluorocarbon
E:\FR\FM\23DEP1.SGM
23DEP1
Agencies
[Federal Register Volume 73, Number 247 (Tuesday, December 23, 2008)]
[Proposed Rules]
[Pages 78680-78705]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-29965]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 82
[EPA-HQ-OAR-2008-0496; FRL-8752-7]
RIN 2060-A076
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 for control of
U.S. consumption and production of
[[Page 78681]]
hydrochlorofluorocarbons (HCFCs) by apportioning baselines and
allocating production and consumption allowances for several HCFCs for
which the Agency previously allocated allowances and other HCFCs that
were not allocated allowances previously, for the control periods 2010-
2014. The HCFC allowance system is part of EPA's Clean Air Act program
to phase out ozone-depleting substances (ODSs) to protect the
stratospheric ozone layer. Protection of the stratospheric ozone layer
helps reduce rates of skin cancer and cataracts, as well as other
health and ecological effects. The U.S. is obligated under the Montreal
Protocol on Substances that Deplete the Ozone Layer (Montreal Protocol)
to limit HCFC consumption and production to a specific level and, using
stepwise reductions, to decrease the specific level culminating in a
complete HCFC phaseout in 2030. The next major milestone, to occur on
January 1, 2010, is a 75 percent reduction from the aggregate U.S. HCFC
baseline for production and consumption. In this action EPA proposes to
allocate the allowances for 2010-2014 that will ensure compliance with
the international stepwise reduction, consistent with the 1990 Clean
Air Act Amendments. In addition, EPA proposes to amend the regulatory
provisions concerning allowances for HCFC production for developing
countries' basic domestic needs to be consistent with the September
2007 adjustments to the Montreal Protocol. Also, the Agency is
providing its interpretation of a self-effectuating ban on introduction
into interstate commerce and use of HCFCs contained in section 605(a)
of the Clean Air Act and proposes to amend existing regulatory
provisions to facilitate implementation of the statutory requirements.
DATES: Comments must be received on or before February 23, 2009, unless
a public hearing is requested. If a public hearing is requested,
comments must then be received on or before March 9, 2009. Any party
requesting a public hearing must notify the contact listed below under
FOR FURTHER INFORMATION CONTACT by 5 p.m. Eastern Daylight Time on
January 2, 2009. If a hearing is held, it will take place on January 7,
2009 and the comment period will then close on March 9, 2009.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
OAR-2008-0496, by one of the following methods:
https://www.regulations.gov: Follow the on-line
instructions for submitting comments.
E-mail: a-and-r-Docket@epa.gov.
Fax: 202-566-1741.
Mail: Docket , 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-2008-0496 Air
and Radiation Docket at EPA West, 1301 Constitution Avenue, NW., Room
B108, Mail Code 6102T, Washington, DC 20460. 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-
2008-0496. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
https://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 e-mail. The https://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 e-mail comment directly to EPA without going through https://
www.regulations.gov your e-mail 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 https://www.epa.gov/epahome/dockets.htm.
FOR FURTHER INFORMATION CONTACT: Cindy Axinn Newberg, EPA,
Stratospheric Protection Division, Office of Atmospheric Programs,
Office of Air and Radiation (6205J), 1200 Pennsylvania Avenue, NW.,
Washington, DC 20460, (202) 343-9729, newberg.cindy@epa.gov.
SUPPLEMENTARY INFORMATION: Under the Montreal Protocol on Substances
that Deplete the Ozone Layer (Montreal Protocol), as amended, the U.S.
and other industrialized countries that are Parties to the Protocol
have agreed to limit production and consumption of
hydrochlorofluorocarbons (HCFCs), and to phase out production and
consumption in a step-wise fashion over time, culminating in a general
phaseout by 2020 while permitting a small amount of HCFC production to
continue solely for servicing existing appliances until 2030. Title VI
of the Clean Air Act Amendments of 1990 (CAAA of 1990) also mandates
restrictions on HCFCs, culminating in a complete production and
consumption phaseout in 2030. For purposes of both the Montreal
Protocol and the Clean Air Act, ``consumption'' is defined as
production plus imports minus exports. Sections 605 and 606 of the
Clean Air Act authorize EPA to promulgate regulations to manage the
consumption and production of HCFCs until the terminal phaseout. In
1993 EPA established a chemical-by-chemical, ``worst-first,'' approach
to implement the Montreal Protocol's graduated phaseout in overall HCFC
levels (58 FR 65018). Key concepts in the ``worst-first'' approach
included ``distinguishing among HCFCs based on their [ozone depletion
potential (ODP)] and phasing out use in new equipment prior to use for
servicing existing equipment'' (58 FR 65026). The consumption cap
became effective in 1996, and HCFC consumption in the U.S. remained
about 15 percent below the cap for the first two years. In 1998 and
1999, consumption rose to levels that approached the cap. On January
21, 2003, EPA established an allowance tracking system for HCFCs (68 FR
2820), noting at that time that EPA would again pursue a notice-and-
comment rulemaking to implement a 2010 stepwise reduction. EPA
promulgated minor amendments to these regulations on June 17, 2004 (69
FR 34024), and July 20, 2006 (71 FR 41163).
In this action, EPA proposes the next step in the chemical-by-
chemical phaseout the United States uses to meet its international
obligations. Specifically, EPA proposes for HCFC-141b, HCFC-22, and
HCFC-142b, to grant specified percentages of the consumption and
production baselines for the control periods 2010-2014; and for other
HCFCs to apportion company-by-company consumption and production
baselines as well as grant
[[Page 78682]]
specified percentages of the consumption and production baselines for
the control periods 2010-2014. EPA is also proposing to amend the
provisions for HCFC production allowances to meet the basic domestic
needs of developing countries. In addition, EPA is proposing regulatory
changes to complete the implementation of the section 605(a) ban on
introduction into interstate commerce or use of HCFCs and clarifies its
interpretation of this Clean Air Act provision.
Abbreviations and Acronyms Used in this Document
CAA--Clean Air Act
CAAA--Clean Air Act Amendments of 1990
CFC--chlorofluorocarbon
EPA--Environmental Protection Agency
HCFC--hydrochlorofluorocarbon
Montreal Protocol--Montreal Protocol on Substances that Deplete the
Ozone Layer
NPRM--Notice of Proposed Rulemaking
ODP--ozone depletion potential
ODS--ozone-depleting substance
Party--States and regional economic integration organizations that have
consented to be bound by the Montreal Protocol on Substances that
Deplete the Ozone Layer
SNAP--Significant New Alternatives Policy
UNEP--United Nations Environment Programme
Tips for Preparing Your Comments
When submitting comments, remember to:
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; suggest alternatives
and substitute language for your requested changes.
Describe any assumptions and provide any technical
information and/or data that you used.
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.
Table of Contents
I. Regulated Entities
II. Background
A. How Do the Montreal Protocol and Clean Air Act Phase Out
HCFCs?
B. What Sections of the Clean Air Act Apply to This Rulemaking?
III. This Proposal
A. How Does EPA Propose to Issue Production and Consumption
Allowances for 2010-2014?
1. What Actions Did EPA Take in the 2003 Allocation Rule?
2. How Will EPA Allocate 2010-2014 Allowances for HCFC-22 and
HCFC-142b?
3. How Should EPA Consider Servicing Needs for Existing
Equipment?
4. How Will the Allocated Allowances Appear in the Regulations?
5. What Other Methods Could Be Used to Determine the Allocation
for HCFC-22 and HCFC-142b Allowances?
6. How Important Is HCFC-22 in Determining the Allocation of
Allowances?
7. HCFC-22 Allowances for 2010-2014
8. HCFC-142b Allowances for 2010-2014
9. How Does the Aggregate for HCFC-22 and HCFC-142b Translate to
Entity-by-Entity?
10. Baselines for HCFC-123, HCFC-124, HCFC-225ca, and HCFC-225cb
11. What Percentage of the Baseline Will EPA Allocate for HCFC-
123, HCFC-124, HCFC-225ca, and HCFC-225cb for the Control Periods
2010-2014?
12. What About Other HCFCs?
B. Does the Article 5 Allowance Provision Change Given the
Adjustments to the Montreal Protocol?
C. How Does EPA Interpret ``Introduce into Interstate Commerce
or Use?''
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and 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 Advancement Act
J. Executive Order 12898: Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income
Populations
I. Regulated Entities
These proposed amendments will affect the following categories:
----------------------------------------------------------------------------------------------------------------
Category NAICS code SIC code Examples of regulated entities
----------------------------------------------------------------------------------------------------------------
Chlorofluorocarbon gas manufacturing....... 325120 2869 Chlorodifluoromethane
manufacturers;
Dichlorofluoroethane
manufacturers;
Chlorodifluoroethane
manufacturers.
Chlorofluorocarbon gas importers........... 325120 2869 Chlorodifluoromethane importers;
Dichlorofluoroethane importers;
Chlorodifluoroethane importers.
Chlorofluorocarbon gas exporters........... 325120 2869 Chlorodifluoromethane exporters;
Dichlorofluoroethane exporters;
Chlorodifluoroethane exporters.
Manufacturers of air conditioners and 333415 .............. Air-Conditioning Equipment and
refrigerators. Commercial and Industrial
Refrigeration Equipment
manufacturers.
Importers of air conditioners and 333415 3585 Air-Conditioning Equipment and
refrigerators. Commercial and Industrial
Refrigeration Equipment importers.
----------------------------------------------------------------------------------------------------------------
This table is not intended to be exhaustive, but rather provides a
guide for readers regarding entities likely to be regulated by this
action. This table lists the types of entities that EPA is now aware
potentially could 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.
II. Background
A. How Do the Montreal Protocol and Clean Air Act 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
[[Page 78683]]
stratospheric ozone-depleting substances. 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 of 1990), which included Title VI on
Stratospheric Ozone Protection, codified as 42 U.S.C. Chapter 85,
Subchapter VI, to ensure that the United States could satisfy its
obligations under the Montreal Protocol. Title VI includes restrictions
on production, consumption, and use of ozone-depleting substances 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. Both the Montreal Protocol and the Clean Air Act 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-ODP substitutes for CFCs and other ODSs. 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 industrialized (Article
2) Parties, a schedule to which the United States adheres. The
consumption cap for each Article 2 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, 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 the 2007 adjustment, the
schedule called for a 35 percent reduction of the consumption cap in
2004, followed by a 65 percent 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,
however, the Parties created a cap on production for Article 2 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
metric tons, effective January 1, 2004. This became the U.S. production
baseline for 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 that 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). EPA explained that its action modified the
schedule contained in paragraphs (a) and (b) of section 605 (58 FR
65025). Paragraph (a) addresses use and introduction into interstate
commerce, while paragraph (b) addresses production.
On January 21, 2003 (68 FR 2820), EPA promulgated regulations to
ensure compliance with the first 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 that rule EPA established
chemical-specific consumption and production baselines for HCFC-141b,
HCFC-22, and HCFC-142b. To further carry out the 1993 phaseout
schedule, EPA issued calendar-year allowances equal to 100 percent of
baseline for HCFC-22 and HCFC-142b for each control period \2\ from
2003 through 2009. For those same control periods EPA issued calendar-
year allowances equal to zero for HCFC-141b; under the 1993 rule HCFC-
141b was subject to a complete phaseout on January 1, 2003, which
allowed the United States to meet and exceed the 2004 stepwise
reduction of 35 percent below the baseline for all HCFCs. EPA did,
however, create a petition process to allow applicants to request very
small amounts of HCFC-141b beyond the phaseout. EPA considered
establishing baselines for all HCFCs in that rule but deferred such
action for all but HCFC-141b, HCFC-142b, and HCFC-22. These regulations
were amended with a technical correction on July 16, 2003 (68 FR
41925), and with direct final rules adopting minor amendments on June
17, 2004 (69 FR 34024) and July 20, 2006 (71 FR 41163).
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\2\ A control period, as defined at 40 CFR 82.3, is a twelve-
month period from January 1 through December 31.
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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.\3\
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\3\ 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 become binding for all Parties on May 14,
2008.
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As a result of the 2007 Montreal Adjustment (reflected in Decision
XIX/6), the United States and other industrialized countries are
obligated to reduce HCFC production and consumption 75 percent below
the established baseline by 2010, rather than 65 percent as was the
previous requirement. The other milestones remain the same: 90 percent
below the baseline by 2015, and 99.5 percent below the baseline by
2020--allowing, during 2020 to 2030, production and consumption at only
0.5 percent of baseline solely for servicing existing air-conditioning
and refrigeration equipment. The adjustment also resulted in a phaseout
schedule for HCFC production that parallels the consumption phaseout
schedule. All production and consumption for Article 2 Parties is
phased out by 2030.
Decision XIX/6 also adjusted the provisions for Parties operating
under
[[Page 78684]]
paragraph 1 of Article 5 (developing countries): (1) To set production
and consumption baselines based on the average 2009-2010 production and
consumption, respectively; (2) to freeze 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 is
phased out by 2040.
In addition, Decision XIX/6 adjusted Article 2F to allow
industrialized 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.\4\ 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
industrialized 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.
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\4\ 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.''
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B. What Sections of the Clean Air Act Apply to This Rulemaking?
Several sections of the Clean Air Act apply to this proposed
rulemaking. Section 605 of the Clean Air Act phases out production and
consumption and restricts the use of HCFCs in accordance with the
schedule set forth in that section. Section 606 provides for
acceleration of the schedule in section 605 based on a determination by
EPA regarding current scientific information or the availability of
substitutes, or to conform to any acceleration under the Montreal
Protocol. EPA has previously accelerated the section 605 schedule
through a rulemaking published December 10, 1993 (58 FR 65018). Though
this action, EPA is further accelerating the section 605 HCFC
production and consumption phaseouts.
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. EPA believes that in this instance, all
three criteria have been met.
The first criterion allows the Administrator, based on an
assessment of credible current scientific information, to determine
that a more stringent schedule may be necessary to protect human
health. The recent scientific findings by the Montreal Protocol's
Science Assessment Panel, Science Assessment of Ozone Depletion: 2006,
available in the docket for this rulemaking, were initially presented
to the Parties to the Montreal Protocol in October 2006 at the 18th
Meeting of the Parties in New Delhi, India. The Assessment was
published in March 2007, and hard copies were available to the Parties
in advance of the 26th Open-Ended Working Group Meeting held in June
2007 in Nairobi, Kenya. The assessment report shows that
notwithstanding the evidence of a healing of the ozone layer, there
continue to be human health and environmental effects associated with
ozone depletion and that recovery continues to rely on a successful
total global phaseout of ODSs. The report includes scenarios where
additional actions taken by the Parties would result in a faster
recovery. While these specific scenarios (including complete phaseout
by the end of that calendar year) were not all necessarily deemed to be
practical, they demonstrated to the Parties what could be achieved with
additional actions and contributed in part to the willingness of many
Parties, including the United States, to consider the adjustments to
the Montreal Protocol's HCFC phaseout schedule that were successfully
negotiated in September 2007. EPA published a notice of data
availability (72 FR 35230) concerning the potential changes in HCFC
consumption from proposed adjustments to the Montreal Protocol
submitted by the United States for consideration at the 19th Meeting of
the Parties held in Montreal September 2007. The data made available
through that notice were specific to the United States' proposal but
had general applicability to the other five proposals submitted by
various Parties to the Protocol and to what was ultimately agreed to by
the Parties at the 19th Meeting.
Reductions in stratospheric ozone levels lead to higher levels of
ultraviolet radiation reaching the Earth's surface, and a higher risk
of negative health
[[Page 78685]]
effects. According to the American Cancer Society, one in five
Americans will develop skin cancer in their lifetime, and one American
dies every hour from this disease. While medical research continues to
improve the understanding of the causes and effects of skin cancer,
many health and education groups are working to reduce the incidence of
this disease. EPA believes the recent scientific findings on
stratospheric ozone depletion, together with the well-established
relationship between ozone depletion and increased risk of human health
effects, support a determination that a more stringent HCFC phaseout
schedule may be necessary to protect against such effects.
The second criterion allows the Administrator to determine a more
stringent schedule is practicable based on the availability of
substitutes for ODS, taking into account technological achievability,
safety, and other relevant factors. Since the establishment of the
domestic chemical-by-chemical phaseout in the United States, advances
by industry have resulted in the availability of substitutes for a
large variety of end-use applications. Under section 612 of the CAA,
EPA's Significant New Alternatives Policy (SNAP) program evaluates and
lists alternatives for ODSs that reduce overall risk to human health
and the environment and are currently or potentially available.
Alternatives include chemical replacements, product substitutes, and
alternative technologies. The SNAP program has reviewed approximately
450 combinations of alternatives and end uses to date. EPA makes
information available concerning potential alternatives for various
end-use applications. Suitable alternatives--in many cases, multiple
suitable alternatives--are available for all end-use applications for
the HCFCs considered in this action. The SNAP program has reviewed
substitutes for the following industrial sectors:
Refrigeration & Air Conditioning.
Foam Blowing Agents.
Cleaning Solvents.
Fire Suppression and Explosion Protection.
Aerosols.
Sterilants.
Tobacco Expansion.
Adhesives, Coatings & Inks.
HCFCs have been used in almost all of these industrial sectors. For
example, within the air conditioning and refrigeration industrial
sector, end uses where HCFCs have been used include chillers,
industrial process refrigeration systems, ice skating rinks, cold
storage warehouses, refrigerated transport, retail food refrigeration,
household appliances, and residential and light commercial air
conditioning and heat pumps. The SNAP program lists substitutes for
each of the end uses. (For a complete list of substitutes the reader is
directed to: https://www.epa.gov/ozone/snap/lists/.) EPA
believes that given the availability of substitutes, a more stringent
HCFC phaseout schedule now is practicable.
The last criterion is that the Montreal Protocol be modified to
include a schedule to control or reduce production, consumption, or use
of any substance more rapidly than section 605 would dictate. The
United States submitted a proposal to adjust the Montreal Protocol in
March 2007 to accelerate the phaseout of HCFCs. This was one of six
proposals considered by the Parties at their 19th Meeting. Due to the
efforts of the United States and others, the Parties agreed to
adjustments that result in a more aggressive phaseout schedule for both
developed and developing countries. Therefore, this third criterion has
been met. Through this action, EPA is proposing to incorporate a
schedule that reflects the 2007 Montreal Adjustment in its regulations.
In order to meet the 2010 stepdown, EPA is proposing to allocate HCFC
allowances for the years 2010 through 2014 at a level that will ensure
the aggregate HCFC production and consumption will not exceed 25
percent of the U.S. baselines.
While section 606 is sufficient authority for this acceleration of
the section 605 phaseout schedule, EPA also notes that section 614(b)
of the Clean Air Act provides that in the case of a conflict between
the Act and the 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
Protocol.
In addition to implementing the 2007 Montreal Adjustment, today's
proposed rule would also address provisions in section 605 of the Clean
Air Act that relate to use and introduction intro interstate commerce
of class II substances. In today's action, EPA is proposing to complete
its implementation (begun in 1993) of the section 605 provisions on use
of class II substances. EPA is also proposing regulatory language to
reflect the section 605 provisions on introduction into interstate
commerce of class II substances. EPA previously addressed the
provisions concerning use of class II substances in a 1993 rulemaking
that accelerated the phaseout schedule for HCFC-22 and HCFC-142b (58 FR
15014, 58 FR 65018). The intent of the 1993 rulemaking was to
accelerate not only the production and consumption schedule, but also
the use restrictions for those two substances. In the March 18, 1993
notice of proposed rulemaking, EPA stated that the effect of this
acceleration was ``to prohibit the use of the chemicals (virgin
material only) for any use except as a feedstock or as a refrigerant in
existing equipment as of January 1, 2010'' (58 FR 15028). EPA noted in
the December 10, 1993 notice of final rulemaking that ``HCFC
restrictions and the approach included in today's final rule have not
changed from those proposed by the Agency in March'' (58 FR 65028). The
regulatory prohibitions included with that notice, however, did not
control use directly, but instead banned production and import for most
uses. In today's action, EPA is proposing to add the direct use
prohibitions contemplated in the 1993 rule as well as the corresponding
prohibitions on introduction into interstate commerce. EPA is also
clarifying its interpretation of section 605(a).
III. This Proposal
EPA is proposing to adjust existing regulations to address the next
major milestone in the HCFC phaseout. As a Party to the Montreal
Protocol, and having ratified the Montreal Protocol and all of its
amendments, the United States is required to decrease its amount of
HCFC consumption and production to 25 percent of the U.S. baseline by
2010. Our domestic chemical-by-chemical approach results in differing
schedules for the phaseout of individual HCFC compounds. EPA believes
that the chemical-by-chemical HCFC allocation of allowances proposed in
this notice of proposed rulemaking (NPRM) will ensure that the United
States continues to maintain an overall HCFC production and consumption
level that is below the 2010 cap specified by the September 2007
Montreal Adjustment, while at the same time ensuring that servicing
needs consistent with Section 605(a) of the Clean Air Act and EPA's
implementing regulations continue to be met. Thus the aggregate
allowances for all U.S. HCFC consumption in the years 2010-2014 will
not exceed 3,810 ODP-weighted metric tons (25 percent of the aggregate
U.S. consumption baseline) annually and the aggregate allowances for
all U.S. HCFC production in the years 2010-2014 will not exceed
3,884.25 ODP-weighted metric tons (25 percent of the aggregate U.S.
production baseline) annually.
[[Page 78686]]
To meet the 2010 cap for the 2010-2014 control periods, EPA is
proposing to continue its past practice of apportioning company-
specific production and consumption baselines for individual HCFCs, and
granting a certain percent of that baseline as necessary to achieve
compliance with the cap. For HCFC-141b, HCFC-22, and HCFC-142b, EPA is
proposing to apportion company-specific baselines in amounts that are
equivalent to those currently published at Sec. 82.17 (for production)
and Sec. 82.19 (for consumption), adjusted as necessary to reflect
permanent transfers of baseline allowances and changes to the names of
entities identified in the tables at Sec. 82.17 and Sec. 82.19.
Companies are currently granted, in Sec. 82.16, 0 percent of baseline
for HCFC-141b and 100 percent of baseline for HCFC-22 and HCFC-142b.
For 2010-2014, given the previous phaseout of HCFC-141b, EPA will
continue to allocate zero percent for HCFC-141b, continuing to allow
only limited amounts of production via an EPA petition process.\5\ EPA
is proposing to allocate less than 100 percent of baseline for HCFC-22
and HCFC-142b to meet our obligations under the Montreal Protocol and
reflecting the use restrictions under section 605(a) that are discussed
later in this proposal while providing for servicing needs consistent
with those restrictions.
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\5\ EPA is not proposing any changes and thus is not seeking
comment with regard to the HCFC-141b petition process for the 2010-
2014 control periods.
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EPA is proposing a similar approach for HCFC-123, HCFC-124, HCFC-
225ca, and HCFC-225cb, which currently do not have baselines. EPA is
proposing to apportion company-specific baselines for these HCFCs based
on production and import data available to the Agency. For control
periods 2010-2014, EPA is proposing to grant 125 percent of baseline
for these HCFCs.
The allocations described above for HCFC-22, HCFC-142b, HCFC-123,
HCFC-124, HCFC-225ca, and HCFC-225cb reflect EPA's analysis of market
data for these chemicals. The proposed allocations were developed to
allow the need for virgin material to be met and to avoid shortages
during the affected control periods, as well as to accommodate some
market growth for HCFCs-123, -124, -225ca, and -225cb, for which
baselines were not developed in the 2003 allocation rule. The total
proposed allocation of HCFC allowances to meet the U.S. need for virgin
material is less than the 3,810 ODP-ton cap. The differential between
the cap and the total proposed allocation will have the effect of
accommodating minor adjustments in the market, particularly to allow
potential market growth for HCFCs that have not been produced or
imported since 2003 (and which are therefore not reflected here). In
summary, of the 3,810 ODP tons of consumption and 3,884.25 ODP tons of
production allowable for the 2010-2014 control periods as established
by the Montreal Protocol, EPA is proposing to allocate allowances, in
aggregate, for 2,920 ODP tons of consumption and 2,646 ODP tons of
production.
These proposed allocations represent 77 percent of the consumption
cap and 68 percent of the production cap established by the Montreal
Protocol for 2010. EPA seeks comment on whether the proposed
allocations, together with the amounts assumed to be available from
reclaimed refrigerant, will suffice to meet HCFC needs for the existing
uses (primarily refrigerant servicing) that will still be permitted in
2010, as well as potential adjustments in the HCFC market. Please
provide information and documentation on newly emerging uses of HCFCs
and other uses of HCFCs, if any, that are not accounted for by EPA
currently. EPA is especially interested in information pertaining to
the years 2010 through 2014.
EPA is proposing two other changes in this proposed rule. First, to
reflect the September 2007 Montreal Adjustments, EPA is proposing to
adjust the amount of Article 5 allowances for control periods 2010-
2019. Second, EPA is completing its implementation of the provisions in
section 605 of the Clean Air Act that relate to use and introduction
into interstate commerce of class II substances.
EPA is not proposing changes to other provisions of 40 CFR part 82
subpart A, such as the recordkeeping and reporting obligations, the
essential use and critical use provisions, and the HCFC-141b petition
process. EPA is only seeking comments on the portions of 40 CFR part 82
subpart A that are specifically addressed by this proposal.
A. How Does EPA Propose to Issue Production and Consumption Allowances
for 2010-2014?
In the United States, an allowance is the unit of measure that
controls production and consumption of ozone-depleting substances. An
allowance represents the privilege granted to a company to produce or
import one kilogram (not ODP-weighted) of the specific substance. 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. EPA has
allocated two types of calendar-year allowances--production allowances
and consumption allowances--for HCFC-22 and HCFC-142b. ``Production
allowance'' and ``consumption allowance'' are defined at 40 CFR 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 trade allowances for one type of HCFC for
allowances of another type of HCFC, with transactions weighted
according to the ozone depletion potential of the chemicals involved.
Pursuant to section 607 of the Clean Air Act, EPA applies an offset to
each HCFC trade by deducting 0.1 percent from the transferor's
allowance balance. The offset is viewed as a benefit to 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).
Under current regulations at 40 CFR 82.15(a) and (b), HCFC-22 and
HCFC-142b may not be produced or imported in excess of the calendar-
year allowances held by the producer or importer. EPA has not yet
allocated any calendar-year allowances for HCFC-142b or HCFC-22 to
cover the 2010 control period and beyond. Absent a grant of calendar-
year allowances for these HCFCs, Sec. 82.15 would prohibit their
production and import after December 31, 2009. EPA intends to avoid
that result by issuing a final rule in advance of that date that will
allocate calendar-year allowances for 2010-2014.
1. What Actions Did EPA Take in the 2003 Allocation Rule?
In the January 21, 2003, allocation rule, EPA established baselines
for HCFC-141b, HCFC-22, and HCFC-142b. Section 601(2) states that EPA
may select ``a representative calendar year'' to serve as the baseline
for HCFCs. In the 2003 allocation rule, however,
[[Page 78687]]
EPA concluded that because the entities eligible for allowances had
differing production and import histories, no one year was
representative for all companies. Therefore, in the 2003 allocation
rule 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. EPA assigned individual production
baseline years in the same manner. EPA did not consider years after
1997 to avoid creating an uneven playing field that would skew
allocations to those companies with ample resources and good access to
information regarding the impending phaseout. EPA is not proposing to
revisit decisions made in the 2003 allocation rule, such as the
Agency's discretion to consider data from multiple years in
establishing a baseline.
The 2003 allocation 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, with the limited exception described above, by granting 0
percent of that chemical's baseline for production and consumption in
the table at Sec. 82.16. The rule granted 100 percent of baseline for
production and consumption of HCFC-22 and HCFC-142b. 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 baseline.
Because EPA has allocated the same amount of allowances every year
from 2004 to 2009--with minor changes reflecting permanent trades of
baseline allowances--and because EPA tracks the production and
consumption of all HCFCs (including those for which baselines are not
allocated), the Agency can ascertain that the U.S. will remain
comfortably below the cap through 2009. The January 2003 allocation
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 exact amount 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 stated that it would likely
achieve the 2010 reduction step by applying a percentage reduction to
the HCFC-22 and HCFC-142b baseline allowances. EPA has monitored the
market to ascertain servicing needs and market adjustments in the use
of HCFCs, including HCFCs for which EPA did not establish baselines in
the 2003 allocation rule.
2. How Will EPA Allocate 2010-2014 Allowances for HCFC-22 and HCFC-
142b?
This proposal identifies five primary options for allocating HCFC-
22 and HCFC-142b allowances for the control periods 2010-2014: (1)
Allocating a percentage of the baseline allowances (Sec. Sec. 82.17
and 82.19) for each HCFC respectively with or without considering any
permanent baseline transfers and/or inter-pollutant transfers that
resulted in a different amount of production or consumption for a
specific HCFC; (2) allocating allowances based on evaluation of the
most recent three years of production, import, and/or export data as
reported to EPA; (3) allocating allowances based on evaluation of past
sales of HCFCs by allowance holders by considering how the HCFCs were
ultimately used (e.g., servicing refrigeration or air-conditioning,
original manufacture of refrigeration or air-conditioning equipment,
foam blowing); (4) allocating allowances based on aggregated ODP tons;
or (5) allocating a total amount of allowances and allowing for
purchase by establishing an auction system. These options are described
in more detail in section III.A.9 of this preamble. Each of these five
methods offers advantages and disadvantages for potential allowance
holders which vary according to whether a particular entity is
predominantly a producer or importer; whether it currently sells HCFC-
22 and HCFC-142b to original equipment manufacturers, wholesalers,
retailers, or companies that service appliances; whether the portion of
its business that is ODS-based is expanding or contracting as the next
major milestone in the phaseout approaches; its liquidity; whether it
holds both HCFC-142b and HCFC-22 allowances and/or engages in inter-
pollutant transfers; and whether it sold HCFCs for applications that do
not lend themselves to servicing. Without regard to the practices of
individual entities, each of the potential allocation schemes also
offers advantages and disadvantages associated with the ease of
implementation and other administrative burdens. EPA has placed in the
docket to this NPRM a memorandum titled ``Draft Regulatory Options for
Allocating HCFC Allowances after 2009'' that explores the advantages
and disadvantages of the various options. In addition to the
memorandum, EPA has also placed in the docket written correspondence by
entities that also discusses various options for allocating HCFC
allowances.
EPA provided notice of the leading option for implementing the 2010
milestone in the preamble to the 2003 allocation rule by indicating
that EPA ``intends to achieve this reduction step through notice and
comment prior to 2010 and will likely implement the reduction by simply
listing a percent of baseline allowances to be granted in Sec. 82.16
for the years after 2009'' (68 FR 2823). The Agency said that it would
allocate allowances for HCFC-22 and HCFC-142b at less than 100 percent
of the respective baselines during the control periods 2010-2014. EPA
continues to believe that this option is the most appropriate, but
seeks comment on other options. This approach offers a transparent
design and provides stability in that it uses a well-vetted baseline.
EPA believes this option also is the least burdensome because it would
not require additional one-time or periodic reporting obligations that
may be necessary if EPA were to adopt a different option. Producers and
importers have adapted to the current HCFC allocation method and
aligned their business activities around the baselines set forth in the
2003 allocation rule. Currently, EPA manages a tracking system and
issues calendar-year allowances per control period to specific entities
listed in Sec. 82.17 and Sec. 82.19. An option that utilizes this
system would limit administrative burdens for the Agency and allowance
holders.
In the 2003 allocation rule, EPA did not forecast the amount of
reduction for HCFC-22 and HCFC-142b that would be needed to ensure that
the United States stayed sufficiently below the 2010 stepwise
reduction, which at the time was a reduction of 65 percent from the
Montreal Protocol baseline. EPA did not determine whether it would
reduce the allocations for the two substances by the same percentage or
by different percentages. Several factors affect determination of the
appropriate percentage of the HCFC-22 and HCFC-142b production and
consumption baselines to allocate for 2010-2014. Factors include the
percentage of the aggregate U.S. production and consumption caps that
other HCFCs comprise as well as provisions in the Clean Air Act and
implementing
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regulations that include use restrictions (discussed in section III.C
of this NPRM).
EPA uses information from quarterly, annual, and other periodic
reporting requirements to monitor consumption, production, imports, and
exports of all HCFCs. EPA uses this information to ensure companies'
compliance with regulatory requirements and to develop reports that are
requested by the Parties to the Montreal Protocol, including reports
ascertaining U.S. compliance with the phaseout caps. The information
enables EPA to monitor production and consumption for all HCFCs,
including HCFCs for which baselines have not yet been established and
for which allowances have not yet been allocated.
Although EPA's July 20, 2001, proposed HCFC allocation rulemaking
would have allocated production and consumption allowances for all
HCFCs, the January 2003 final rule apportioned company-specific
baselines, and allocated a specific percentage of baseline allowances
for the 2003-2009 control periods, only for HCFC-141b, HCFC-22, and
HCFC-142b. EPA applied a ``worst-first'' approach to these HCFCs since
they are the most damaging to the stratospheric ozone layer. The 2003
final rule noted that the HCFC market was continuing to evolve. At that
time, the market for HCFCs with lower ODPs did not reflect rapid
expansion and thus it was not necessary to establish specific baselines
by chemical and issue allowances to ensure that the United States
remained below its cap. Later in this proposal, EPA further discusses
establishing and apportioning baselines as well as allocating calendar-
year allowances for these lower-ODP HCFCs for the control periods 2010-
2014.
3. How Should EPA Consider Servicing Needs for Existing Equipment?
EPA is proposing to use projected servicing needs in its
determination of the amounts of HCFC-22 and HCFC-142b allowances to be
allocated for the 2010-2014 control periods. EPA is focusing on
servicing needs because under section 605(a) of the Clean Air Act and
EPA's implementing regulations, nearly all other uses of these two
HCFCs will be banned effective January 1, 2010. EPA has previously
issued a draft analysis of servicing demand for the HCFC appliances in
the U.S. refrigeration and air-conditioning sector projected to be in
service from 2010-2019. The report is titled The U.S. Phaseout of
HCFCs: Projected Servicing Needs in the U.S. Air-Conditioning and
Refrigeration Sector (the ``Servicing Tail'' report). On November 4,
2005, EPA published a notice of data availability (70 FR 67172) making
a draft of the report available for public review and comment. On
September 29, 2006, EPA held a stakeholder meeting presenting the
findings of a revision to the Servicing Tail report along with other
important information regarding the next major milestones in the HCFC
phaseout. EPA solicited comments on the findings presented at the
meeting. Some stakeholders, including representatives of manufacturers,
chemical producers, importers, reclaimers, industry associations, and
environmental organizations, commented on the projected amount of HCFCs
needed to service this installed base of equipment and on the amounts
expected to be available from reclamation.
EPA focused the analysis on air-conditioning and refrigeration
appliances because such equipment will represent 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. EPA also focused the analysis on HCFC-22 because HCFC-22 is
the predominant HCFC in the installed base of air-conditioning and
refrigerant equipment for which servicing in the U.S. will likely
continue. The findings in the Servicing Tail report have helped to
shape EPA's views regarding the allocation for the control periods
2010-2014.
The majority of HCFC-22 equipment that is projected to be in use
from 2010 onward will be air-conditioning applications, including
window units, packaged terminal units, residential and commercial
unitary air-conditioning, chillers, dehumidifiers, water and ground
source heat pumps, and non-light duty mobile air-conditioning in buses
and trains. Approximately 147.5 million units of all such types of
HCFC-22 air-conditioning equipment will be in use in 2010, decreasing
from 2010 levels by about 41 percent by 2015 and 76 percent by 2020. In
2010, approximately 2.2 million units of HCFC-22 refrigeration
equipment will be in use, including retail food, industrial process
refrigeration, and transport refrigeration equipment (but not including
cold storage warehouses). The installed base of HCFC-22 refrigeration
equipment is projected to decrease from 2010 levels by about 29 percent
by 2015 and 51 percent by 2020. EPA developed these estimates using its
Vintaging Model, a tool for estimating the annual chemical emissions
from industrial sectors that have historically used ozone-depleting
substances in their products. Additional information on the Vintaging
Model is available in the docket for this rulemaking.
As a result of the September 2007 Montreal Adjustment, in which the
Parties agreed to adjust the stepwise reduction in 2010 from 65 percent
of baseline to 75 percent of baseline for non-Article 5 Parties, and
recognizing the overall advances by industry in transitioning to non-
ODS substitutes, EPA has prepared a draft revised Servicing Tail report
to: (1) Reflect the 75 percent reduction in 2010; (2) consider more
recent production and consumption data in the United States; and (3)
consider more recent trends in the air-conditioning and refrigeration
sectors. This revised draft report is available in the docket for this
rulemaking. EPA is accepting comments on the analysis and the draft
findings until February 23, 2009 or March 9, 2009 if a hearing
regarding this rulemaking is held.
The Servicing Tail report utilizes production, import, and export
data reported to the Agency on a quarterly, annual, and transactional
basis, as required by Sec. 82.24. EPA's analysis of the reported data
confirms that the United States is satisfying its obligations as it
phases out ODSs and enables EPA to consider trends in the HCFC markets
on a chemical-by-chemical basis. EPA also uses this information to
submit an annual report to the Ozone Secretariat as requested by the
Parties to the Montreal Protocol.
Using the reported data, the draft revised Servicing Tail report,
and the comments provided at the September 2006 stakeholder meeting and
submitted in subsequent correspondence (available in the docket), EPA
believes it has sufficient information to propose through this action
to allocate a percentage of baseline allowances for HCFC-22 and for
HCFC-142b for production and consumption for the control periods 2010-
2014 that will address servicing needs. The specific percentage of
baseline for each of the affected compounds is discussed below. EPA
requests comments regarding whether it should consider other sources of
information in addition to the required reports, the Servicing Tail
report, and stakeholder comments. In particular, EPA is interested in
whether these sources provide sufficient information to allow EPA to
reasonably estimate servicing needs for 2010-2014, especially for HCFC-
22, which accounts for the majority of the market.
4. How Will the Allocated Allowances Appear in the Regulations?
EPA is proposing to revise two types of tables in 40 CFR part 82
that together
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specify the production and consumption allowances available to
allowance holders during specified control periods. Tables at Sec.
82.17 and Sec. 82.19 apportion baseline production and consumption
amounts (also referred to as baseline production allowances and
baseline consumption allowances), respectively, to individual companies
for individual HCFCs. Complementing these tables, the table at Sec.
82.16 lists the percentage of baseline allocated to allowance holders
for specific control periods. EPA is proposing to retain this framework
of complementary tables, revising them to reflect adjustments to
baselines, and to grant percentages of baselines in a manner that
achieves the 2010 phasedown goal.
Currently the table at Sec. 82.16 allocates zero percent of
baseline to HCFC-141b and 100 percent of baseline to HCFC-22 and HCFC-
142b (combined in a single column) for each control period spanning
2003-2009. EPA is proposing to amend the table by including control
periods 2010-2014, by continuing to allocate zero percent to HCFC-141b,
and by allocating specified percentages (in separate columns) to HCFC-
22, HCFC-142b, and--as will be discussed later--other HCFCs.
The proposed percentages for HCFC-22 and HCFC-142b differ because
EPA projects that the needs will differ for servicing air-conditioning
and refrigeration appliances during the 2010-2014 control periods.
EPA's analysis shows that there will be a significantly greater need
for HCFC-22 than for HCFC-142b during the control periods 2010-2014.
Based on the Serv