HCFC Files (rule and court filings)

Luke Hall-Jordan to: Amanda_I._Lee 05/31/2011 12:49 PM

Hi Amanda,

Per our discussion, here are the clean and tracked changes copies of the rule and the court filings from 

the Arkema v. EPA and Honeywell and DuPont v. EPA cases.

IFR:

Arkema v. EPA Files:

Honeywell/DuPont v. EPA Files:

Best,

Luke

Luke Hall-Jordan

U.S. Environmental Protection Agency

1200 Pennsylvania Ave, NW (MC-6205J)

Washington, DC 20460

Office: 202-343-9591

Cell: 202-230-7589
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EO12866_CAA Part 82A 2060 AQ82 IFR FRN_20110531 

ENVIRONMENTAL PROTECTION AGENCY 

40 CFR Part 82 

[EPA-HQ-OAR-2010-1040; FRL-xxxx-x] 

RIN 2060-AQ82 

Protection of Stratospheric Ozone: Adjustments to the Allowance System for Controlling 

HCFC Production, Import, and Export 

AGENCY: Environmental Protection Agency [EPA]. 

ACTION: Interim final rule. 

SUMMARY: EPA is adjusting the allowance system controlling U.S. consumption and 

production of hydrochlorofluorocarbons (HCFCs) as a result of a recent court decision vacating a 

portion of the rule titled “Protection of Stratospheric Ozone: Adjustments to the Allowance 

System for Controlling HCFC Production, Import, and Export; Final Rule.” EPA interprets the 

court’s vacatur as applying to the part of the rule that establishes the company-by-company 

baselines and calendar-year allowances for HCFC-22 and HCFC-142b. This action relieves the 

regulatory ban on production and consumption of these two chemicals following the court’s 

vacatur by establishing new company-by-company HCFC-22 and HCFC-142b baselines and 

allocating production and consumption allowances for 2011. 

DATES: This rule is effective [INSERT DATE OF PUBLICATION IN FEDERAL 

REGISTER]. While the urgent need for certainty regarding the consumption allowance 

allocations in the 2011 control period precludes the Agency from considering any adjustments to 

the consumption allowances allocated in this action, EPA will consider all written comments 

received by [INSERT DATE 30 DAYS AFTER PUBLICATION DATE] to determine 

whether to issue additional production allowances for the time period covered by this action. 

Commenters may also submit comments on the issues addressed in this action as they pertain to 
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future control periods. 

ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-OAR-2010-

1040, by one of the following methods: 

• www.regulations.gov: Follow the on-line instructions for submitting comments. 

 • Email: a-and-r-docket@epa.gov

 • Fax: 202-566-1741 

• Mail: Docket # EPA-HQ-OAR-2010-1040, 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-2010-1040 Air and Radiation Docket at 

EPA West, 1301 Constitution Avenue NW, Room B108, Mail Code 6102T, 

Washington, D.C. 20004. Such deliveries are only accepted during the Docket’s 

normal hours of operation, and special arrangements should be made for 

deliveries of boxed information. 

Instructions: Direct your comments to Docket ID No. EPA-HQ-OAR-2010-1040. EPA's policy 

is that all comments received will be included in the public docket without change and may be 

made available online at www.regulations.gov, including any personal information provided, 

unless the comment includes information claimed to be Confidential Business Information (CBI) 

or other information whose disclosure is restricted by statute. Do not submit information that you 

consider to be CBI or otherwise protected through www.regulations.gov or e-mail. The 

www.regulations.gov website 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 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, 
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EPA recommends that you include your name and other contact information in the body of your 

comment and with any disk or CD-ROM you submit. If EPA cannot read your comment due to 

technical difficulties and cannot contact you for clarification, EPA may not be able to consider 

your comment. Electronic files should avoid the use of special characters, any form of 

encryption, and be free of any defects or viruses. For additional information about EPA’s public 

docket, visit the EPA Docket Center homepage at www.epa.gov/epahome/dockets.htm. 

FOR FURTHER INFORMATION CONTACT: Luke H. Hall-Jordan by telephone at (202) 

343-9591, or by e-mail at hall-jordan.luke@epa.gov, or by mail at U.S. Environmental 

Protection Agency, Stratospheric Protection Division, Stratospheric Program Implementation 

Branch (6205J), 1200 Pennsylvania Avenue, NW, Washington, D.C., 20460. You may also visit 

the Ozone Protection website of EPA’s Stratospheric Protection Division at 

www.epa.gov/ozone/strathome.html for further information about EPA’s Stratospheric Ozone 

Protection regulations, the science of ozone layer depletion, and related topics. 

SUPPLEMENTARY INFORMATION: 

Acronyms and Abbreviations. The following acronyms and abbreviations are used in this 

document. 

APA – Administrative Procedure Act 

CAA – Clean Air Act 

CAAA – Clean Air Act Amendments of 1990 

CFC – Chlorofluorocarbon 

CFR – Code of Federal Regulations 

EPA – Environmental Protection Agency 

FR – Federal Register 

HCFC – Hydrochlorofluorocarbon 

HVAC – Heating, Ventilating, and Air Conditioning 
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Montreal Protocol – Montreal Protocol on Substances that Deplete the Ozone Layer 

MOP – Meeting of the Parties 

MT – Metric Ton 

ODP – Ozone Depletion Potential 

ODS – Ozone-Depleting Substances 

Party – States and regional economic integration organizations that have consented to be bound 

by the Montreal Protocol on Substances that Deplete the Ozone Layer

Organization of This Document. The following outline is provided to aid in locating 

information in this preamble. 

I. Regulated Entities 

II. Background 

A. How Does the Montreal Protocol Phase Out HCFCs? 

B. How Does the Clean Air Act Phase Out HCFCs? 

C. What Sections of the Clean Air Act Apply to This Rulemaking? 

D. How Does This Action Relate to the Recent Court Decision? 

1. Addressing 2010 Allowances 

III. Justification for this Interim Final Rule 

IV. Summary of this Interim Final Action 

V. Allocation of Allowances for the 2011 Control Period 

 A. Baselines for HCFC-22 and HCFC-142b Allowances 

 1. Adjusting the Baseline for Inter-company and Inter-pollutant 

Transfers 

B. Factors for Considering Allocation Amounts for HCFC-22 and HCFC-142b 

1. The Importance of HCFC-22 Relative to HCFC-142b Servicing Needs for 

Existing Equipment 
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2. Meeting Servicing Needs with Virgin and Recovered Material 

3. Annual Reduction in Allocated Amounts 

C. Allocations of HCFC-22 and HCFC-142b 

1. HCFC-22 Consumption Allowances for 2011 

2. HCFC-22 Production Allowances for 2011 

3. HCFC-142b Allowances for 2011 

4. How the Aggregate for HCFC-22 and HCFC-142b Translates Entity-byEntity 

D. HCFC-141b, HCFC-123, HCFC-124, HCFC-225ca, and HCFC-225cb 

Allowances 

E. Other HCFCs 

VI. Statutory and Executive Order Reviews 

 A. Executive Order 12866: Regulatory Planning and Review and Executive Order 

13563: Improving Regulation and Regulatory Review 

 B. Paperwork Reduction Act 

 C. Regulatory Flexibility Act (RFA) 

 D. Unfunded Mandates Reform Act 

 E. Executive Order 13132: Federalism 

 F. Executive Order 13175: Consultation and Coordination with Indian Tribal 

Governments 

 G. Executive Order 13045: Protection of Children from Environmental Health and 

Safety Risks 

 H. Executive Order 13211: Actions that Significantly Affect Energy Supply, 

Distribution, or Use 

 I. National Technology Transfer Advancement Act 
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 J. Executive Order 12898: Federal Actions to Address Environmental Justice in 

Minority Populations and Low-Income Populations 

 K. Congressional Review Act 

I. Regulated Entities

 This rule will affect the following categories: 

Category NAICS code SIC code Examples of regulated entities 

Industrial Gas Manufacturing 

325120 2869 

Fluorinated hydrocarbon gases 

manufacturers and reclaimers 

Other Chemical and Allied 

Products Merchant 

Wholesalers 422690 5169 

Chemical gases and compressed 

gases merchant wholesalers 

Air-Conditioning and Warm 

Air Heating Equipment and 

Commercial and Industrial 

Refrigeration Equipment 

Manufacturing 333415 3585 

Air-conditioning equipment and 

commercial and industrial 

refrigeration equipment 

manufacturers 

Air-Conditioning Equipment 

and Supplies Merchant 

Wholesalers 423730 5075 

Air-conditioning (condensing unit, 

compressors) merchant wholesalers

Electrical and Electronic 

Appliance, Television, and 

Radio Set Merchant 

Wholesalers 423620 5064 

Air-conditioning (room units) 

merchant wholesalers 

Plumbing, Heating, and AirConditioning Contractors 

238220 1711, 7623 

Central air-conditioning system and 

commercial refrigeration 

installation; HVAC contractors 

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 could 

potentially be regulated by this action. Other types of entities not listed in this table could also be 

affected. To determine whether your facility, company, business organization, or other entity is 

regulated by this action, you should carefully examine these regulations. If you have questions 

regarding the applicability of this action to a particular entity, consult the person listed in the 

“FOR FURTHER INFORMATION CONTACT” section. 
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II. Background 

EPA is undertaking this rulemaking as a result of the decision issued by the U.S. Court of 

Appeals for the District of Columbia Circuit (Court) in Arkema v. EPA (618 F.3d 1, D.C. Cir. 

2010) regarding the December 15, 2009 final rule titled “Protection of Stratospheric Ozone: 

Adjustments to the Allowance System for Controlling HCFC Production, Import, and Export,” 

published at 74 FR 66413 (2009 Final Rule). Certain allowance holders affected by the 2009 

Final Rule filed petitions for judicial review of the rule under section 307(b) of the Clean Air 

Act. Among other arguments, the petitioners contended that the rule was impermissibly 

retroactive because in setting the baselines for the new regulatory period, EPA did not take into 

account certain inter-pollutant baseline transfers that petitioners had performed during the prior 

regulatory period. 

The Court issued a decision on August 27, 2010, agreeing with petitioners that “the 

[2009] Final Rule unacceptably alters transactions the EPA approved under the 2003 Rule” 

(Arkema v. EPA, 618 F.3d at 3). The Court vacated the rule in part, “insofar as it operates 

retroactively,” and remanded to EPA “for prompt resolution,” (618 F.3d at 10). The Court 

withheld the mandate for the decision pending the disposition of any petition for rehearing. 

EPA’s petition for rehearing was denied on January 21, 2011. The mandate issued on February 4, 

2011. More detail is provided on the case and EPA’s interpretation of the Court’s decision in 

Section II.D. 

A. How Does the Montreal Protocol Phase Out HCFCs? 

The Montreal Protocol on Substances that Deplete the Ozone Layer is the international 

agreement aimed at reducing and eventually eliminating the production and consumption of 

stratospheric ozone-depleting substances (ODS). The U.S. was one of the original signatories to 

the 1987 Montreal Protocol and the U.S. ratified the Protocol on April 12, 1988. Congress then 

enacted, and President George H.W. Bush signed into law, the Clean Air Act Amendments of 
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1990 (CAAA), which included Title VI on Stratospheric Ozone Protection, codified as 42 U.S.C. 

Chapter 85, Subchapter VI, to ensure that the U.S. could satisfy its obligations under the 

Montreal Protocol. Title VI includes restrictions on production, consumption, and use of ODS 

that are subject to acceleration if “the Montreal Protocol is modified to include a schedule to 

control or reduce production, consumption, or use . . . more rapidly than the applicable schedule” 

prescribed by the statute (CAA §606). Both the Montreal Protocol and the Clean Air Act (CAA) 

define consumption as production plus imports minus exports. 

 In 1990, as part of the London Amendment to the Montreal Protocol, the Parties 

identified HCFCs as “transitional substances” to serve as temporary, lower ozone depletion 

potential (ODP) substitutes for CFCs and other ODS. EPA similarly viewed HCFCs as 

“important interim substitutes that will allow for the earliest possible phaseout of CFCs and other 

Class I substances1

” (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 U.S. 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 (MT), effective January 1, 1996. This became the U.S. 

consumption baseline for HCFCs. 

 The 1992 Copenhagen Amendment created a schedule with graduated reductions and the 

eventual phaseout of HCFC consumption (Copenhagen, 23-25 November, 1992, Decision IV/4). 

Prior to a later adjustment in 2007, the schedule initially called for a 35 percent reduction of the 

consumption cap in 2004, followed by a 65 percent reduction in 2010, a 90 percent reduction in 

 

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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2015, a 99.5 percent reduction in 2020 (restricting the remaining 0.5 percent of baseline to the 

servicing of existing refrigeration and air-conditioning equipment), with a total phaseout in 2030. 

The Copenhagen Amendment did not cap HCFC production. In 1999, the Parties created 

a cap on production for 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 ODPweighted MT, effective January 1, 2004. This became the U.S. production baseline for HCFCs. 

To further protect human health and the environment, the Parties to the Montreal Protocol 

adjusted the Montreal Protocol’s phaseout schedule for HCFCs at the 19th Meeting of the Parties 

in September 2007. In accordance with Article 2(9)(d) of the Montreal Protocol, the adjustment 

to the phaseout schedule was effective on May 14, 2008.2

 As a result of the 2007 Montreal Adjustment (reflected in Decision XIX/6), the U.S. and 

other industrialized countries are obligated to reduce HCFC production and consumption 75 

percent below the established baseline by 2010, rather than 65 percent as previously required. 

The other milestones remain the same. The adjustment also resulted in a phaseout schedule for 

HCFC production that parallels the consumption phaseout schedule. All production and 

consumption for Article 2 Parties is phased out by 2030. 

 Decision XIX/6 also adjusted the provisions for Parties operating under paragraph 1 of 

Article 5 (developing countries): (1) to set HCFC production and consumption baselines based 

on the average 2009-2010 production and consumption, respectively; (2) to freeze HCFC 

production and consumption at those baselines in 2013; and (3) to add stepwise reductions of 10 

 

2

 Under Article 2(9)(d) of the Montreal Protocol, an adjustment enters into force six months from the date the 

depositary (the Ozone Secretariat) circulates it to the Parties. The depositary accepts all notifications and documents 

related to the Protocol and examines whether all formal requirements are met. In accordance with the procedure in 

Article 2(9)(d), the depositary communicated the adjustment to all Parties on November 14, 2007. The adjustment 

entered into force and become binding for all Parties on May 14, 2008. 
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percent below baselines by 2015, 35 percent by 2020, 67.5 percent by 2025, and 97.5 percent by 

2030 – allowing, between 2030 and 2040, an annual average of no more than 2.5 percent to be 

produced or imported solely for servicing existing air-conditioning and refrigeration equipment. 

All production and consumption for Article 5 Parties will be phased out by 2040. 

 In addition, Decision XIX/6 adjusted Article 2F to allow 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 2020.3 Paragraph 14 of Decision XIX/6 notes that no later than 2015, 

the Parties would consider “further reduction of production for basic domestic needs” in 2020 

and beyond. Under paragraph 13 of Decision XIX/6, the Parties will review in 2015 and 2025, 

respectively, the need for the “servicing tails” for 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. 

B. How Does the Clean Air Act Phase Out HCFCs? 

The U.S. has chosen to implement the Montreal Protocol phaseout schedule on a 

chemical-by-chemical basis. In 1992, environmental and industry groups petitioned EPA to 

 

3

 Paragraphs 4-6 of adjusted Article 2F read as follows: 

 “4. Each Party shall ensure that for the twelve-month period commencing on 1 January 2010, and in each twelve-month period thereafter, its 

calculated level of consumption of the controlled substances in Group I of Annex C does not exceed, annually, twenty-five per cent of the 

sum referred to in paragraph 1 of this Article. Each Party producing one or more of these substances shall, for the same periods, ensure that 

its calculated level of production of the controlled substances in Group I of Annex C does not exceed, annually, twenty-five per cent of the 

calculated level referred to in paragraph 2 of this Article. However, in order to satisfy the basic domestic needs of the Parties operating under 

paragraph 1 of Article 5, its calculated level of production may exceed that limit by up to ten per cent of its calculated level of production of 

the controlled substances in Group I of Annex C as referred to in paragraph 2. 

5. Each Party shall ensure that for the twelve-month period commencing on 1 January 2015, and in each twelve-month period thereafter, its 

calculated level of consumption of the controlled substances in Group I of Annex C does not exceed, annually, ten per cent of the sum 

referred to in paragraph 1 of this Article. Each Party producing one or more of these substances shall, for the same periods, ensure that its 

calculated level of production of the controlled substances in Group I of Annex C does not exceed, annually, ten per cent of the calculated 

level referred to in paragraph 2 of this Article. However, in order to satisfy the basic domestic needs of the Parties operating under paragraph 

1 of Article 5, its calculated level of production may exceed that limit by up to ten per cent of its calculated level of production of the 

controlled substances in Group I of Annex C as referred to in paragraph 2. 

6. Each Party shall ensure that for the twelve-month period commencing on 1 January 2020, and in each twelve-month period thereafter, its 

calculated level of consumption of the controlled substances in Group I of Annex C does not exceed zero. Each Party producing one or more 

of these substances shall, for the same periods, ensure that its calculated level of production of the controlled substances in Group I of Annex 

C does not exceed zero. However: 

 i. each Party may exceed that limit on consumption by up to zero point five per cent of the sum referred to in paragraph 1 of this Article 

in any such twelve-month period ending before 1 January 2030, provided that such consumption shall be restricted to the servicing of 

refrigeration and air conditioning equipment existing on 1 January 2020; 

ii. each Party may exceed that limit on production by up to zero point five per cent of the average referred to in paragraph 2 of this 

Article in any such twelve-month period ending before 1 January 2030, provided that such production shall be restricted to the servicing of 

refrigeration and air conditioning equipment existing on 1 January 2020.”
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implement the required phaseout by eliminating the most ozone-depleting HCFCs first. Based on 

the available data at that time, EPA believed the U.S. could meet, and possibly exceed, the 

required Montreal Protocol reductions through a chemical-by-chemical phaseout that employed a 

“worst-first” approach focusing on certain chemicals earlier than others. In 1993, as authorized 

by section 606 of the CAA, the U.S. established a phaseout schedule that eliminated HCFC-141b 

first and would greatly restrict HCFC-142b and HCFC-22 next, followed by restrictions on all 

other HCFCs and ultimately a complete phaseout (58 FR 15014, March 18, 1993; 58 FR 65018, 

December 10, 1993). 

 On January 21, 2003 (68 FR 2820), EPA promulgated regulations (2003 Final Rule) to 

ensure compliance with the first reduction milestone in the HCFC phaseout: the requirement that 

by January 1, 2004, the U.S. reduce HCFC consumption by 35 percent and freeze HCFC 

production. In the 2003 Final Rule, EPA established chemical-specific consumption and 

production baselines for HCFC-141b, HCFC-22, and HCFC-142b for the initial regulatory 

period ending December 31, 2009. Section 601(2) states that EPA may select “a representative 

calendar year” to serve as the company baseline for HCFCs. In the 2003 Final Rule, EPA 

concluded that because the entities eligible for allowances had differing production and import 

histories, no single year was representative for all companies. Therefore, EPA assigned an 

individual consumption baseline year to each company by selecting its highest ODP-weighted 

consumption year from among the years 1994 through 1997. EPA assigned individual production 

baseline years in the same manner. EPA also provided an exception allowing new entrants 

provided that they began importing after the end of 1997 but before April 5, 1999, the date the 

advanced notice of proposed rulemaking was published. EPA believed that such small businesses 

might not have been aware of the impending rulemaking that would affect their ability to 

continue in the HCFC market. 
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 The 2003 Final Rule apportioned production and consumption baselines to each company 

in amounts equal to the amounts in the company’s highest “production year” or “consumption 

year,” as described above. It completely phased out the production and import of HCFC-141b by 

granting 0 percent of that substance’s baseline for production and consumption in the table at 40 

CFR 82.16. EPA did, however, create a petition process to allow applicants to request very small 

amounts of HCFC-141b beyond the phaseout. The 2003 Final Rule also granted 100 percent of 

the baselines for production and consumption of HCFC-22 and HCFC-142b for each of the years 

2003 through 2009. EPA was able to allocate allowances for HCFC-22 and HCFC-142b at 100 

percent of baseline because, in light of the concurrent complete phaseout of HCFC-141b, the 

allocations for HCFC-22 and HCFC-142b, combined with projections for consumption of all 

other HCFCs, remained below the 2004 cap of 65 percent of the U.S. baseline. 

 EPA allocates allowances for specific years; they are valid between January 1 and 

December 31 of a given control period (i.e., calendar year). Prior to December 15, 2009, EPA 

had not allocated any HCFC allowances for year 2010 or beyond. The regulations at section 

82.15(a) and (b) only addressed the production and import of HCFC-22 and HCFC-142b for the 

years 2003-2009. Through the 2009 Final Rule (74 FR 66412), EPA addressed the production 

and import of HCFC-22 and HCFC-142b for the 2010-2014 control periods. Absent the granting 

of calendar-year allowances, section 82.15 would have prohibited the production and import of 

HCFC-22 and HCFC-142b after December 31, 2009. The 2009 Final Rule allowed for continued 

production and consumption, at specified amounts, of HCFC-142b, HCFC-22, and other HCFCs 

not previously included in the allowance system, for the 2010-2014 control periods. 

 In the U.S., an allowance is the unit of measure that controls production and consumption 

of ODS. EPA establishes company-by-company baselines (also known as “baseline allowances”) 

and allocates calendar-year allowances equal to a percentage of the baseline for specified control 

periods. A calendar-year allowance represents the privilege granted to a company to produce or 
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import one kilogram (not ODP-weighted) of the specific substance. EPA allocates two types of 

calendar-year allowances – production allowances and consumption allowances. “Production 

allowance” and “consumption allowance” are defined at section 82.3. To produce an HCFC for 

which allowances have been allocated, an allowance holder must expend both production and 

consumption allowances. To import an HCFC for which allowances have been allocated, an 

allowance holder must expend consumption allowances. An allowance holder exporting HCFCs 

for which it has expended consumption allowances may obtain a refund of those consumption 

allowances upon submittal of proper documentation to EPA. 

 Since EPA is implementing the phaseout on a chemical-by-chemical basis, it allocates 

and tracks production and consumption allowances on an absolute kilogram basis for each 

chemical. Upon EPA approval, an allowance holder may transfer calendar-year allowances of 

one type of HCFC for calendar-year allowances of another type of HCFC, with transactions 

weighted according to the ODP of the chemicals involved. Pursuant to section 607 of the CAA, 

EPA applies an offset to each HCFC transfer by deducting 0.1 percent from the transferor’s 

allowance balance. The offset benefits the ozone layer since it “results in greater total reductions 

in the production in each year of . . . class II substances than would occur in that year in the 

absence of such transactions” (42 U.S.C. 7671f). 

The U.S. remained comfortably below the aggregate HCFC cap through 2009. The 2003 

Final Rule announced that EPA would allocate allowances for 2010-2014 in a subsequent action 

and that those allowances would be lower in aggregate than for 2003-2009, consistent with the 

next stepwise reduction for HCFCs under the Montreal Protocol. EPA stated its intention to 

determine the number of allowances that would be needed for HCFC-22 and HCFC-142b, 

bearing in mind that other HCFCs would also contribute to total HCFC consumption. EPA noted 

that it would likely achieve the 2010 reduction step by applying a percentage reduction to the 

HCFC-22 and HCFC-142b baselines. EPA subsequently monitored the market to estimate 
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servicing needs and market adjustments in the use of HCFCs, including HCFCs for which EPA 

did not establish baselines in the 2003 Final Rule. 

In the 2009 Final Rule, EPA determined both the estimated demand for HCFC-22 during 

the 2010-2014 regulatory period and the percentage of that estimated demand for which it was 

appropriate to allocate allowances. As described in Section V.B. of this action, EPA determined 

that the percentage of the estimated demand allocated in the form of allowances should not 

remain constant from year to year but rather should decline on an annual basis. For 2010, EPA 

allocated allowances equal to 80 percent of the estimated demand for HCFC-22, concluding that 

reused, recycled, and reclaimed material could meet the remaining 20 percent. Under the 2009 

Final Rule, the percentage of estimated demand for which there was no allocation, and therefore 

would need to be met through recycling and reclamation, rose from 20 percent in 2010 to 29 

percent in 2014 to ensure the U.S. market would have a viable reclamation industry and could 

meet the 2015 stepwise reduction under the Montreal Protocol. The determinations EPA made in 

the 2009 Final Rule regarding (1) the total estimated demand for HCFC-22 in 2010-2014 and (2) 

the percentage of that estimated demand that EPA would address through an allowance 

allocation were not at issue in the litigation and are unaffected by the Court’s decision. EPA is 

not revisiting either determination with respect to 2011 in this interim final action, but rather is 

relying on the existing record for the 2009 Final Rule. However, EPA welcomes comment on 

whether it should revisit these determinations in the future. EPA is also interested in comments 

on whether it could and should allocate a different percentage of baseline for calendar-year 

production than for calendar-year consumption, while still meeting U.S. obligations under the 

Montreal Protocol and complying with the CAA. 

C. What Sections of the Clean Air Act Apply to This Rulemaking? 

 Several sections of the CAA apply to this rulemaking. Section 605 of the CAA phases out 

production and consumption and restricts the use of HCFCs in accordance with the schedule set 
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forth in that section. As discussed in the 2009 Final Rule (74 FR 66416), section 606 provides 

EPA authority to set a more stringent phaseout schedule than the schedule in section 605 based 

on an EPA determination regarding current scientific information or the availability of 

substitutes, or to conform to any acceleration under the Montreal Protocol. EPA previously set a 

more stringent schedule than the section 605 schedule through a rule published December 10, 

1993 (58 FR 65018). Through the 2009 Final Rule, EPA made a further adjustment to the section 

605 schedule based on the acceleration under the Montreal Protocol as agreed to at the Meeting 

of the Parties in September 2007. The more stringent schedule established in that rule is 

unaffected by the recent Court decision and is therefore still in effect. 

Section 606 provides authority for EPA to promulgate regulations that establish a 

schedule for production and consumption that is more stringent than what is set forth in section 

605 if: “(1) based on an assessment of credible current scientific information (including any 

assessment under the Montreal Protocol) regarding harmful effects on the stratospheric ozone 

layer associated with a class I or class II substance, the Administrator determines that such more 

stringent schedule may be necessary to protect human health and the environment against such 

effects, (2) based on the availability of substitutes for listed substances, the Administrator 

determines that such more stringent schedule is practicable, taking into account technological 

achievability, safety, and other relevant factors, or (3) the Montreal Protocol is modified to 

include a schedule to control or reduce production, consumption, or use of any substance more 

rapidly than the applicable schedule under this title.” It is only necessary to meet one of the three 

criteria. In the 2009 Final Rule, EPA determined that all three criteria had been met with respect 

to the schedule for phasing out production and consumption of HCFC-22 and HCFC-142b. 

As noted in the 2009 Final Rule, while section 606 is sufficient authority for establishing 

a more stringent schedule than the section 605 phaseout schedule, section 614(b) of the CAA 

provides that in the case of a conflict between the CAA and the Montreal Protocol, the more 
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stringent provision shall govern. Thus, section 614(b) requires the Agency to establish phaseout 

schedules at least as stringent as the schedules contained in the Montreal Protocol. To meet the 

2010 stepdown requirement, EPA is continuing to allocate HCFC allowances at a level that will 

ensure the aggregate HCFC production and consumption will not exceed 25 percent of the U.S. 

baselines. For more discussion of this point, see 74 FR 66416. 

Finally, section 607 addresses transfers of allowances both between companies and 

chemicals. EPA is further clarifying its policy on inter-pollutant transfers in this action. 

D. How Does This Action Relate to the Recent Court Decision?

 Certain allowance holders affected by the 2009 Final Rule filed petitions for review in the 

U.S. Court of Appeals for the District of Columbia Circuit. Among other arguments, the 

petitioners, Arkema Inc., Solvay Fluorides, LLC, and Solvay Solexis, Inc., contended that the 

rule was impermissibly retroactive because in setting the baselines for the new regulatory period, 

EPA did not take into account certain inter-pollutant baseline transfers that petitioners had 

performed during the prior regulatory period. The transfers at issue occurred in 2008. Solvay 

Solexis, Inc. submitted two Class II Controlled Substance Transfer Forms for consumption 

allowance transfers to Solvay Fluorides, LLC on February 15, 2008, and March 4, 2008. 

Arkema, Inc. submitted two Class II Controlled Substance Transfer Forms for consumption and 

production allowance transfers on April 18, 2008. Each company requested EPA’s approval to 

convert HCFC-142b allowances to HCFC-22 allowances, and checked a box on the EPA transfer 

form indicating that “baseline” allowances would be transferred. EPA sent non-objection notices 

to both Solvay Solexis and Solvay Fluorides on February 21, 2008 and March 20, 2008 and to 

Arkema, Inc. in April 2008. The transfer requests and EPA’s approvals were attached to 

petitioners’ court filings and are available in the docket for this action. 

 In the Notice of Proposed Rulemaking titled “Protection of Stratospheric Ozone: 

Adjustments to the Allowance System for Controlling HCFC Production, Import, and Export,” 
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published in the Federal Register at 73 FR 78680 on December 23, 2008 (2008 Proposed Rule), 

EPA requested comments on establishing baselines for the 2010-2014 regulatory period “with or 

without” taking into account baseline inter-pollutant transfers made during the 2003-2009 

regulatory period (73 FR 78687). The proposed regulatory text accounted for the inter-pollutant 

transfers discussed above. The increase in HCFC-22 baseline allowances for Arkema, Inc. and 

Solvay Fluorides, LLC presented in the 2008 Proposed Rule resulted in a larger amount of 

HCFC-22 baseline allowances overall and therefore a lower percentage of HCFC-22 baselines 

allocated across the board in each control period. Specifically, the proposed shift resulted in a 16 

percent decrease in market share for all other allowance holders, and increases for the 

petitioners: Arkema and Solvay. For more detail on the impact of these transfers, see Section 

V.C. of this preamble. 

In the 2009 Final Rule, after considering comments, EPA determined that allowing interpollutant transfers to carry forward from one regulatory period to the next could undermine the 

Agency’s chemical-by-chemical phaseout approach and could encourage market manipulation. 

For a more detailed discussion, see Section V.A.1. EPA also concluded that section 607 of the 

CAA was best read as limiting inter-pollutant transfers to those conducted on an annual basis. 

For these reasons, EPA did not take the 2008 inter-pollutant transfers into account in establishing 

the baselines for the 2009 Final Rule covering 2010-2014. 

The Court issued a decision on August 27, 2010, agreeing with petitioners that “the 

[2009] Final Rule unacceptably alters transactions the EPA approved under the 2003 Rule” 

(Arkema v. EPA, 618 F.3d at 3). The Court vacated the rule in part, “insofar as it operates 

retroactively,” and remanded to EPA “for prompt resolution,” (618 F.3d at 10). The Court 

withheld the mandate for the decision pending the disposition of any petition for rehearing. On 

November 12, 2010, EPA filed a petition for rehearing, which was denied on January 21, 2011. 

The mandate issued on February 4, 2011. 
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Because the Court vacated the rule only in part, without specifying which part or parts 

were vacated, EPA may adopt a reasonable interpretation of the vacatur’s extent. In doing so, 

EPA is relying on its expertise in administering the HCFC phaseout regulations under Title VI of 

the CAA. First, EPA notes that the rule contains elements that were not at issue in the litigation. 

EPA concludes that the vacatur has no effect on allowances for any substances other than HCFC142b and HCFC-22, since the petitioners’ claims and the opinion itself discuss only those two 

substances. Similarly, EPA concludes that other discrete portions of the rule, such as the 

provisions on use and introduction into interstate commerce, are unaffected by the vacatur. 

The baselines for HCFC-142b and HCFC-22 were clearly at issue in the litigation and 

indeed are the focus of the Court’s opinion. The Court found that “the Agency’s refusal to 

account for the Petitioners’ baseline transfers of inter-pollutant allowances in the Final Rule is 

impermissibly retroactive,” (618 F.3d at 9). Because baseline and calendar year allowances are 

inextricably linked4

, EPA has determined that the Court’s vacatur voids the HCFC-22 and 

HCFC-142b baselines in 40 CFR 82.17 and 82.19 as well as the percentage of baseline allocated 

for those specific substances in 40 CFR 82.16 for all companies listed in those sections.5

 This 

means that until EPA establishes new baselines and allocates new calendar-year allowances, 

production and import of these two substances is prohibited under 40 CFR 82.15. Recognizing 

this scenario, on January 28, 2011, EPA sent letters to affected stakeholders informing them that 

the Agency would exercise enforcement discretion for a limited period provided their production 

 

4

 The reason baseline and calendar-year allocations are inextricable is because calendar-year allocations are 

expressed as a percentage of baseline, and the percentage of baseline allocated for a specific substance varies 

depending on the sum of all company baselines for that substance. The process works as follows for each specific 

HCFC: First, all the company-specific baselines listed in the tables at 40 CFR 82.17 and 82.19 are added to 

determine the aggregate amount of baseline production and consumption, respectively. Second, EPA determines 

how many consumption allowances the market needs for a given year, taking into account recycled, reused, and 

reclaimed material, and divides that amount by the aggregate amount of baseline allowances. The resulting 

percentage listed in the table at section 82.16 becomes what each company is allowed to consume in a given control 

period. For example, a company with 100,000 kg of HCFC-22 baseline allowances would multiply that number by 

the percentage allowed for 2011 (for example, 32 percent) to determine its calendar-year allowance is 32,000 kg. 

Historically and in this interim final rule, EPA has allocated the same percentage of baseline allowances for 

production as it does for consumption. 

5

 The companies’ allocations are inter-related because, as noted in footnote 4, the percentage of baseline allocated 

varies according to the sum of the company-specific baselines. 
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and import did not exceed specified levels and provided that they adhered to additional 

conditions. 

In determining the meaning of the Court’s vacatur, EPA considered whether this 

interpretation was consistent with what the Court intended and a good fit for the specific 

circumstances, which include the goals and design of the HCFC allowance program and the 

basic structure of the 2009 Final Rule. While this interpretation is appropriate in this instance, it 

is possible that another interpretation would be more appropriate in a case involving a program 

with different goals, design, or structure. 

In the 2009 Final Rule, EPA relied on its assessment of the amount of virgin and 

recovered HCFC-22 and HCFC-142b needed to service existing equipment and transition to the 

2015 stepdown under the Montreal Protocol. The Court did not take issue with this assessment. 

At this time, EPA has not received information indicating that demand will be higher than the 

Agency’s assessment predicted. On the contrary, EPA has heard from several anecdotal sources 

that the amount of actual market demand for HCFC-22 may in fact be lower than the amount 

identified in the Servicing Tail Report. However, since EPA does not have sufficient data to 

support this conclusion at this time, and recognizes the urgent need to act quickly to establish 

allowances for the 2011 control period, the Agency is relying on the record for the 2009 Final 

Rule, which includes the Agency’s prior assessment of demand for HCFC-22 and HCFC-142b in 

2011. Therefore, through this action, EPA is establishing new baselines for 2011 reflecting the 

court’s decision and allocating the percentage of baseline needed to ensure that the total 

allocation for 2011 remains the same as in the 2009 Final Rule. If sufficient information becomes 

available in future, EPA may adjust the aggregate allocation level for future control periods. 

1. Addressing 2010 Allowances 

 EPA interprets the Court’s decision as applying, at a minimum, to the HCFC-22 and 

HCFC-142b baseline and calendar-year allowances for 2011-2014. EPA is not addressing 2010 
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allowances in this action. The Agency plans to take comment in a future notice-and-comment 

rulemaking on whether the vacatur and remand should be interpreted as applying to the 2010 

allocations, and if so, how allowances in future control periods might be adjusted to reflect this. 

The 2011 control period is already well underway, and as discussed in the good cause finding in 

Section III, it is important that EPA establish a definitive 2011 allocation now to dispel 

confusion and allow normal business activities to proceed. In particular, EPA believes the urgent 

need for certainty regarding the consumption allowance allocations in the 2011 control period 

precludes the Agency from considering any adjustments during 2011. However, EPA intends to 

address this issue in detail in a separate notice-and-comment rulemaking with respect to future 

control periods. 

III. Justification for this Interim Final Rule 

 EPA is taking this action as an interim final rule without prior proposal and public 

comment because EPA finds that the good cause exemption from the notice-and-comment 

rulemaking requirement of the Administrative Procedure Act (APA), 5 U.S.C. 551 et seq., 

applies here. Section 307(d) of the CAA states that in the case of any rule to which section 

307(d) applies, notice of proposed rulemaking must be published in the Federal Register (CAA 

§307(d)(3)). The promulgation or revision of regulations under Title VI of the CAA is generally 

subject to section 307(d). However, section 307(d) does not apply to any rule referred to in 

subparagraphs (A) or (B) of section 553(b) of the APA. Section 553(b)(B) of the APA, 5 U.S.C. 

553(b)(B), provides that, when an agency for good cause finds that notice-and-comment public 

procedures are impracticable, unnecessary, or contrary to the public interest, the agency may 

issue a rule without providing notice and an opportunity for public comment. 

EPA has determined that there is good cause for making today's rule final without prior 

proposal and opportunity for comment because such notice and opportunity for comment is 

unnecessary, impracticable, and contrary to the public interest. In reaching this determination, 
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EPA considered several factors: (1) taking interim final action for 2011 avoids regulatory 

confusion, disruption of normal business activities, and effects on consumers pending 

development of a notice-and-comment rulemaking (see, e.g., Brae Corp. v. United States, 740 

F.2d 1023 (D.C. Cir. 1984)); (2) the Agency is relying on the existing record from the 2009 Final 

Rule for this action (see, e.g., Chamber of Commerce v. SEC, 443 F.3d 890 (D.C. Cir. 2006)); 

and (3) the rule’s duration is limited (see, e.g., Small Refiner Lead Phase-Down Task Force v. 

EPA, 705 F.2d 506 (D.C. Cir. 1983)). 

First, it is in the public interest to dispel confusion, allow normal business activities to 

proceed, and avoid adverse effects on consumers. EPA has received numerous questions from 

industry about what, if any, allowances companies currently hold in light of the Court’s decision. 

The primary purpose of this interim final rule is to dispel confusion and provide regulatory 

certainty for the near term. EPA interprets the vacatur as voiding company baselines and 

calendar-year allowances for HCFC-22 and HCFC-142b, and because entities are prohibited 

from producing or importing HCFCs without allowances, quick action is necessary to ensure the 

continued production and import of those two HCFCs. This interim final action will provide 

industry with certainty for 2011, and allow normal business operations to continue. It also gives 

EPA time to develop notice-and-comment rules that will cover subsequent control periods. 

This action will also avoid unintended consequences for consumers and businesses who 

own appliances containing HCFC-22 and/or HCFC-142b (e.g., refrigerators and air 

conditioners), as well as the businesses that service these appliances. Absent this rulemaking, 

there could be a shortage of these HCFCs. Consumers and businesses unable to service their 

existing HCFC-22 equipment with HCFCs would instead have to retrofit their existing 

appliances before the end of their useful life to use a refrigerant other than that which was 

intended for the appliance, or purchase new equipment to replace existing appliances. Not only 

would this be expensive and unexpected, especially for those who bought a new unit shortly 
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before January 1, 2010, but the shortage could lead to improper retrofits that decrease a unit’s 

effectiveness and energy efficiency, cost the consumer more to operate, and result in further 

refrigerant emissions to the atmosphere. Considering the current state of the economy, shortages 

of HCFC-22 could lead appliance owners, who likely do not have the same level of experience 

as a licensed professional, to recharge their units on their own. Improper retrofits and recharging 

could raise the potential for mixing refrigerants, which could damage systems and increase the 

likelihood of mixed refrigerants being vented into the atmosphere, since mixtures may not work 

properly and likely could not be reclaimed. 

At worst, these scenarios could lead to an unanticipated changeover of significant 

quantities of equipment, which would be at odds with EPA’s goal of minimizing impacts to 

business and consumers by supporting a gradual turnover of the installed base of equipment as 

individual equipment reaches the end of its useful life, allowing existing equipment to continue 

to operate properly. In the preamble to the 2009 Final Rule, EPA stated: “Congress intended to 

permit the continued use of previously-manufactured appliances” (74 FR 66438). EPA discussed 

this issue in detail at that time, in the context of the section 605(a) ban on the “use” of HCFCs 

(74 FR 66437-66438). In this action, the Agency is not revisiting its analysis or conclusions with 

respect to this issue. Accordingly, EPA is allocating production and consumption allowances for 

HCFC-22 and HCFC-142b in a way that avoids shortening the useful lifetime of appliances that 

were manufactured prior to the effective date of the use ban (January 1, 2010). 

Furthermore, a supply shortage could raise the price of affected gases, thereby increasing 

incentives for entities to illegally smuggle HCFC-22 into the country to meet the demand of 

consumers and businesses. There are numerous cases cited on the EPA website 

(www.epa.gov/ozone/enforce/index.html) documenting the smuggling of CFCs and HCFCs. Not 

only would this hurt entities that are abiding by the law, it could even hurt consumers and 

businesses that unknowingly receive inferior material. For all these reasons, it is important that 
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EPA take action quickly. Since it is impracticable to complete a notice-and-comment rulemaking 

prior to the 2011 summer season, when working air conditioners are most important, and delay 

would be contrary to the public interest, interim final action is necessary. 

The second reason for invoking the good cause exemption is that EPA is relying on the 

existing record for the 2009 Final Rule, which is still applicable and sufficiently current for the 

purposes of this action. In this interim final rule, EPA is not revisiting the determination made in 

the 2009 Final Rule regarding the total amount of HCFC production and import that the Agency 

will allow for 2011. EPA is simply addressing what share of that total amount should be 

allocated to particular companies. The 2008 Proposed Rule (73 FR 78680) provided all interested 

parties an opportunity to comment on the total HCFC production and import amount for 2011. 

Thus, it is unnecessary to provide a second opportunity to comment on that amount prior to 

issuing this interim final rule. 

Third, this interim final rule only addresses 2011—the current control period—and is 

thus limited in duration. The specific duration is defined by the structure of the stratospheric 

ozone protection program, which operates in control periods that correspond to calendar years. 

Allowances are allocated for a specific control period. EPA intends to initiate a notice-andcomment rulemaking or rulemakings as soon as possible to address subsequent control periods. 

For the reasons explained above, and given the Court’s statement that it was remanding 

to EPA “for prompt resolution,” notice and public procedure are impracticable, unnecessary, and 

contrary to the public interest. EPA finds that this constitutes good cause under 5 U.S.C. 

553(b)(B). Nonetheless, EPA is providing 30 days for submission of public comments following 

this action. EPA will consider all written comments submitted in the allotted time period to 

determine whether to issue additional production allowances for 2011. 

Section 553(d) of the Administrative Procedure Act (APA), 5 U.S.C. Chapter 5, generally 

provides that rules may not take effect earlier than 30 days after they are published in the Federal 
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Register. APA section 553(d) excepts from this provision any action that grants or recognizes an 

exemption or relieves a restriction. Since today's action relieves a restriction from the regulatory 

ban on the production and consumption of HCFC-22 and HCFC-142b in the U.S., EPA is 

making this action effective immediately upon publication to ensure the availability of these 

HCFCs for servicing air conditioning and refrigeration equipment in 2011. 

IV. Summary of this Final Action 

In response to the Court’s decision, EPA is (1) establishing 2011 company-by-company 

consumption and production baselines for HCFC-22 and HCFC-142b in the tables at 40 CFR 

82.17 and 82.19 in a manner that reflects the 2008 inter-pollutant baseline transfers and (2) 

allocating company-by-company production and consumption allowances for these substances 

for 2011 by establishing percentages of baseline in the table at section 82.16. EPA is also 

updating the tables at sections 82.17 and 82.19 to reflect 2010 inter-company, single-pollutant 

baseline transfers and revising the list of allowance holders to update company names. These 

actions are consistent with actions taken in the 2009 Final Rule. To reflect the court’s vacatur, 

EPA is removing the allocation percentages from the table at section 82.16 for the years 2011-

2014. In this rulemaking, EPA is adding an allocation percentage for 2011. In a separate noticeand-comment rulemaking or rulemakings, EPA will address the allocations for the control 

periods 2012-2014. All aspects of the 2009 Final Rule promulgated on December 15, 2009 (74 

FR 66412) that are not addressed in this interim final rule are unchanged. 

As a Party to the Montreal Protocol, and having ratified the Montreal Protocol and all of 

its amendments, the U.S. was required to decrease its amount of HCFC consumption and 

production to 25 percent of the U.S. baseline in 2010. The cap is the same for the years 2010-

2014 before it drops down to 10 percent of baseline in 2015. Under the cap, the aggregate 

allowances for all U.S. HCFC consumption in 2011 cannot exceed 3,810 ODP-weighted MT (25 

percent of the aggregate U.S. consumption baseline) annually, and the aggregate allowances for 
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all U.S. HCFC production in 2011 cannot exceed 3,884.25 ODP-weighted MT (25 percent of the 

aggregate U.S. production baseline) annually. 

 To stay below the cap set by the Montreal Protocol for the 2011 control period addressed 

in this rulemaking, EPA is using the historical production and consumption baselines as adjusted 

in the 2009 Final Rule, with further adjustments to reflect the 2008 inter-pollutant baseline 

transfers and inter-company, single-pollutant baseline transfers that occurred after issuance of the 

2009 Final Rule. 

 EPA determined in the 2009 Final Rule that for HCFC-22, it was necessary to allocate a 

percentage of baseline that would decrease on an annual basis to reflect a projected decrease in 

demand as well as to promote recycling and reclamation. EPA is not revisiting that determination 

in this rulemaking. EPA concluded in the 2009 Final Rule that this approach would help prevent 

shortages that might otherwise occur upon the stepdown in 2015. In this action, EPA is 

allocating 32.0 percent of baseline for HCFC-22 in 2011, which reflects an annual decline from 

the 2010 amount. EPA is allocating 4.9 percent of baseline for HCFC-142b in 2011. The HCFC142b number relates solely to the aggregate baselines for this substance and does not reflect an 

annual decline. The reasons for establishing these allocation percentages for 2011 are discussed 

in Section V. 

 EPA’s allocations for both HCFC-22 and HCFC-142b meet U.S. obligations under the 

Montreal Protocol and reflect the use restrictions under section 605(a) of the CAA while 

providing for servicing needs consistent with those restrictions. The allocations for HCFC-22 

and HCFC-142b reflect EPA’s analysis of market data for these chemicals, as prepared in 

advance of the 2009 Final Rule. The allocation levels for these HCFCs meet the demand for 

virgin material and avoid shortages during 2011. 

 In this action, EPA is not changing the methodology used in the 2009 Final Rule to 

calculate the total number of calendar-year consumption and production allowances. While the 
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number of total calendar-year consumption allowances is unchanged, the number of production 

allowances is slightly lower (less than two percent lower) than in the 2009 Final Rule due to the 

changes in aggregate baseline allowances. This is explained in more detail in Section V.C. The 

only other difference is in the distribution of those allowances. 

 At this time, EPA is allocating a total of 2,504 ODP-weighted MT of HCFC-22 and 

HCFC-142b calendar-year consumption allowances and 2,302 ODP-weighted MT of HCFC-22 

and HCFC-142b calendar-year production allowances for 2011. Both allocations remain below 

the limit established by the Montreal Protocol for the 2010-2014 phasedown step of 75 percent 

below baseline. The difference between the cap and the total allocation reflects EPA’s estimate 

(developed for the 2009 Final Rule) of the demand for HCFCs during these control periods. It 

also will accommodate minor adjustments in the market, particularly to allow potential market 

growth for other allowed HCFCs. As discussed in more detail in Section V.B.3. and in the 

preamble to the 2009 Final Rule, it will also encourage greater reclamation of recovered 

refrigerant and thus facilitate preparation for the 2015 step down in the consumption cap to 10 

percent of baseline. 

 This action also clarifies EPA’s policy on inter-pollutant transfers for 2011 and all future 

control periods in Section V.A.1. 

V. Allocation of Allowances for the 2011 Control Period 

A. Baselines for HCFC-22 and HCFC-142b Allowances 

In the 2009 Final Rule, EPA presented the allocation structure for HCFC-22 and HCFC142b for the control periods 2010-2014: allocating a percentage of the baseline production and 

consumption allowances. The rationale for this system is discussed further at 74 FR 66412. The 

Court found no fault with EPA’s framework for allocating HCFCs in the 2009 Final Rule, except 

the aspects of the rule they deemed to be retroactive, i.e., not taking into account inter-pollutant 

baseline transfers that occurred in the prior regulatory period in establishing company-specific 
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baseline allowances. To address this, EPA is establishing HCFC-22 and HCFC-142b baseline 

allowances for 2011 that reflect past inter-pollutant baseline transfers deemed permanent by the 

Court. 

1. Adjusting the Baseline for Inter-company and Inter-pollutant Transfers

Sections 607(b) and (c) of the CAA address inter-pollutant and inter-company transfers 

of allowances, respectively. Inter-pollutant transfers are the transfer of an allowance of one 

substance to an allowance of another substance on an ODP-weighted basis. Inter-company 

transfers are transfers of allowances for the same ODS from one company to another company. 

Section 607(c) also authorizes inter-company transfers combined with inter-pollutant transfers, 

so long as the requirements of both are met. The corresponding regulatory provisions for HCFCs 

appear at 40 CFR 82.23. 

The 2009 Final Rule updated the baselines for HCFC-22 and HCFC-142b to reflect name 

changes and inter-company baseline transfers, i.e., transfers of baseline for a specific type of 

HCFC from one company to another. Doing so reflected the changes in the marketplace that had 

occurred since EPA promulgated the 2003 Final Rule. Inter-company baseline transfers provide 

a mechanism for new entrants to join the HCFC market and for other companies to expand their 

business. EPA recognizes that in some cases, entities are no longer actively involved in HCFC 

production, import, and/or export activities. EPA retained the baseline for such entities, noting 

that this had been a mechanism by which new entrants had entered the HCFC allowance system 

in the past. 

 The 2009 Final Rule also addressed four inter-pollutant baseline transfers made during 

the prior regulatory period (see Section II.D. of this action for more detail). EPA had proposed to 

adjust the company baselines to reflect these four inter-pollutant baseline transfers in the 2008 

Proposed Rule. Eight commenters opposed, and two commenters supported, these proposed 
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adjustments. At issue was whether the inter-pollutant baseline transfers should carry forward as 

part of the companies’ baseline allowances in the next regulatory period. 

 After reviewing the comments, EPA concluded that adjusting the baselines to reflect 

inter-pollutant baseline transfers could create incentives for future manipulation of the allocation 

system in anticipation of future control periods. EPA remains concerned about the potential for 

such future manipulation if inter-pollutant baseline transfers during the current regulatory period 

are carried forward as a change in a company’s baseline for future regulatory periods. For 

example, in 2020 EPA will no longer be issuing HCFC-22 production or consumption 

allowances (see section 82.16(e)). EPA expects that companies with HCFC-22 allowances would 

no longer be in the HCFC market at that date if they did not hold allowances for other HCFCs 

that may still be produced after 2020. If EPA were to allow inter-pollutant baseline transfers that 

carried forward into the new regulatory period, companies with HCFC-22 baselines in 2019 

could convert them all to baselines for HCFC-123. Perpetuating the HCFC-22 baselines in a new 

form would be counter to the design of the chemical-by-chemical phaseout, under which the 

baseline allowances for a particular chemical are intended to drop out of the system upon the 

phase-out of that chemical. As another example, in 2015, a producer or importer that previously 

had not participated in the HCFC-123 market could dominate that market by converting its 

HCFC-22 baseline in 2014 to HCFC-123 baseline. Given the different ODPs of HCFC-22 and 

HCFC-123 (0.055 and 0.02, respectively), converting one baseline allowance of HCFC-22 would 

result in 2.75 baseline allowances of HCFC-123. Also, since companies hold many more HCFC22 baseline allowances than HCFC-123 baseline allowances, converting those HCFC-22 baseline 

allowances would have an overwhelming effect on the current HCFC-123 baseline allowance 

holders and the overall market. EPA agrees with commenters on the 2008 Proposed Rule that 

taking inter-pollutant baseline transfers into account in setting baselines could have the effect of 

moving the U.S. HCFC phasedown from a chemical-by-chemical phaseout, as established under 
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the “worst-first” approach in the 1993 Final Rule, towards an ODP-weighted phasedown. Thus, 

there are important policy reasons going forward for not taking inter-pollutant transfers into 

account in establishing baselines for new regulatory periods. 

 Some commenters on the 2008 Proposed Rule stated that modifying the baselines by 

taking into account inter-pollutant transfers would be contrary to the CAA. One commenter 

argued that section 607 of the CAA allows EPA to approve inter-pollutant transfers of 

allowances only on a year-to-year basis. That commenter pointed to language in section 607(b) 

stating that EPA regulations are to permit “a production allowance for a substance for any year to 

be transferred for a production allowance for another substance for the same year on an ozone 

depletion weighted basis.” The commenter also discussed the legislative history of the 1990 

CAA Amendments. 

 EPA does not agree with the commenter that the language of section 607(b) is clear on its 

face. However, where the statutory language is ambiguous, EPA has discretion to choose a 

reasonable interpretation of that language. EPA determined in the 2009 Final Rule that section 

607(b) is best read as permitting only year-by-year inter-pollutant transfers. EPA continues to 

believe that this is the best interpretation of the statutory language. Section 607(b) states that 

EPA’s rules are to permit “a production allowance for a substance for any year to be transferred 

for a production allowance for another substance for the same year.” This language emphasizes 

the year-by-year nature of such transactions. No parallel language appears in section 607(c). That 

section does, however, provide that any inter-pollutant transfers between two or more persons 

must meet the requirements of section 607(b). 

 As the Court noted, “the Agency is certainly entitled to . . . institute a program that 

forbids baseline inter-pollutant transfers in the future,” (Arkema v. EPA, 618 F.3d at 9). Hence, 

EPA concludes that requiring all inter-pollutant transfers to be conducted on a yearly – and thus 

temporary – basis going forward is the approach most consistent with the wording of section 
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607(b). Further discussion of the reasons for limiting inter-pollutant transfers to those conducted 

on a calendar-year basis is available in the Response to Comments on the 2008 Proposed Rule 

(included in the docket for this rulemaking). 

 Consistent with the Court’s decision regarding past inter-pollutant transfers (those 

conducted during the prior regulatory period), the baselines established in this action for 2011 

take into account the 2008 inter-pollutant baseline transfers discussed earlier in this notice. EPA 

is clarifying, however, that it has not approved any inter-pollutant transfers of baseline 

allowances in the current regulatory period, and for the reasons given in the 2009 Final Rule and 

in this action, in future EPA intends to approve inter-pollutant transfers only on a year-by-year 

basis. Thus, in the context of the protection of stratospheric ozone allowance system, companies 

should not expect that any inter-pollutant transfers they conduct will affect their baselines either 

in the current regulatory period or any future regulatory period. 

 As it did in the 2009 Final Rule, EPA is adjusting baseline allowances to reflect intercompany, single-pollutant baseline transfers that occurred since the last final rule was signed. 

 In summary, this interim final rule reflects the changes in consumption and production 

baseline allowances from (1) the 2008 inter-pollutant transfers deemed permanent by the Court 

and (2) inter-company, single-pollutant baseline transfers that have occurred since the 2009 Final 

Rule was signed, and (3) clarifies the types of inter-pollutant transfers that will be permitted in 

the future. The consumption and production baseline amounts for HCFC-22 and HCFC-142b for 

2011 are shown below in Table 3. 

B. Factors for Considering Allocation Amounts for HCFC-22 and HCFC-142b 

In the 2009 Final Rule, EPA decided to allocate HCFC-22 and HCFC-142b allowances 

based on the projected servicing needs for those compounds, taking into account the amount of 

those needs that can be met through recycling and reclamation. EPA is not changing that 

approach in this interim final rule. However, the specific amounts allocated per company are 
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different due to the changed baselines and the need to apply a different allocation percentage to 

company baselines in order to keep the aggregate amount allocated the same. Because it is 

necessary to promote use of reused, recycled, and reclaimed material in anticipation of the 2015 

phasedown step, EPA does not intend to allocate the difference between the consumption 

allocation authorized by the Parties to the Montreal Protocol and the consumption allocation 

authorized by this rule except under unforeseen extenuating circumstances. 

1. The Importance of HCFC-22 Relative to HCFC-142b Servicing Needs for Existing 

Equipment 

HCFC-22 is the most widely-used HCFC. The demand for its use in servicing existing 

equipment was the primary factor affecting EPA’s allocation of production and consumption 

allowances of HCFCs for the current regulatory period. Prior to issuing the 2009 Final Rule, 

EPA issued and sought comment on three versions of a draft report analyzing servicing demand 

for the HCFC appliances in the U.S. refrigeration and air-conditioning sector projected to be in 

service from 2010-2019 (all versions available at Docket EPA-HQ-OAR-2008-0496: published 

November 4, 2005 at 70 FR 67172; released at a stakeholder meeting on September 29, 2006; 

published December 23, 2008, with 2008 Proposed Rule). The Servicing Tail Report focuses on 

air-conditioning and refrigeration appliances because such equipment represents the bulk of the 

servicing need. In addition, the servicing exception to the use ban for HCFC-22 and HCFC-142b 

pertains only to use as a refrigerant in such equipment. Under section 605(a) of the CAA and 

EPA’s implementing regulations, nearly all other uses of these two HCFCs were banned 

effective January 1, 2010. The projected servicing need for HCFC-22 in 2011 is approximately 

57,900 MT (3,185 ODP-weighted MT), or approximately 84 percent of the consumption cap for 

all HCFCs in 2011 under the Montreal Protocol, which is 3,810 ODP-weighted MT. HCFC-142b 

has primarily been used as a foam blowing agent, a use that was phased out in 2010. The 

projected servicing demand for existing refrigeration equipment containing HCFC-142b is 
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extremely low: approximately 100 MT (7 ODP-weighted MT). EPA therefore focused the 

analysis on HCFC-22 because that compound is the predominant HCFC in the installed base of 

air-conditioning and refrigerant equipment for which servicing in the U.S. will likely continue. 

As discussed in the 2009 Final Rule, the majority of HCFC-22 equipment that is 

projected to be in use from this point onward will be air-conditioning applications, including 

window units, packaged terminal units, unitary air-conditioning, chillers, dehumidifiers, water 

and ground source heat pumps, and motor vehicle air-conditioning in buses and trains. The report 

projected that approximately 145.6 million units of all such types of HCFC-22 air-conditioning 

equipment were in use in 2010, decreasing by about 41 percent in 2015 and 86 percent in 2020. 

In addition, approximately 3.8 million units of HCFC-22 refrigeration equipment were in use in 

2010. The installed base of HCFC-22 refrigeration equipment is projected to decrease from 2010 

levels by about 44 percent in 2015 and 75 percent in 2020. For more on the Servicing Tail Report

and the Vintaging Model, which was used to develop the report, see 74 FR 66424 and the 

Servicing Tail Report included in the docket. 

 EPA estimates that the servicing need for HCFC-22 will continue to decrease each year, 

and consistent with the 2009 Final Rule, this interim final rule accounts for this by allocating a 

smaller amount for 2011 than was allocated for 2010. This approach is described in Section 

V.B.3. In this interim final action, EPA is maintaining the overall HCFC-22 allocation levels for 

2011 that the Agency determined were appropriate in the 2009 Final Rule. EPA’s decision not to 

allocate above the need projected in the Servicing Tail Report is discussed in the preamble to the 

2009 Final Rule. 

2. Meeting Servicing Needs with Virgin and Recovered Material 

In the 2009 Final Rule, the Agency recognized that servicing demand can be met with a 

combination of newly-manufactured or imported HCFCs (virgin HCFCs) and HCFCs that have 

been recovered and either reused, recycled or reclaimed. Therefore, EPA did not anticipate that 
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virgin HCFC-22 would need to be produced or imported to meet the entire HCFC-22 servicing 

demand (estimated to be 3,185 ODP-weighted MT in 2011). The Servicing Tail Report analyzes 

various scenarios regarding reclamation. EPA continues to believe that reused, recycled, and 

reclaimed material can help meet HCFC-22 servicing needs and is therefore not changing course 

at this time. Should new data be presented, EPA reserves the option of increasing the amount of 

demand for servicing existing equipment that should be met by reused, recycled, and reclaimed 

material in future control periods. 

3. Annual Reduction in Allocated Amounts

As explained in the preamble to the 2009 Final Rule, without year-to-year reductions in 

the allocations for virgin HCFC-22, the HCFC-22 market could be oversaturated, and the 

contribution of reused, recycled, and reclaimed refrigerant would decrease, both in the total 

number of kilograms and as the proportion of overall need. 

EPA is particularly concerned with encouraging a smooth transition to the 2015 

stepdown. At that date, the U.S. must meet a 90 percent reduction below the baseline for all 

HCFCs, which is equivalent to 1,524 ODP-weighted MT. EPA’s Servicing Tail Report shows 

that even a 20 percent recovery rate would be insufficient to meet the demand for HCFC-22 in 

2015. As shown in Table 4-5 in the report, demand for HCFC-22 in 2015 is projected to be 

38,800 MT while the cap for all HCFCs equates to 27,709 MT of HCFC-22 (assuming no 

allocation for any other HCFCs). A 20 percent recovery rate would allow for the additional use 

of 8,800 MT but would still leave a shortfall of 2,291 MT in 2015. In developing the 2009 Final 

Rule, EPA calculated that to meet the total demand in 2015, the recovery rate would have to 

increase to 26 percent (representing 29 percent of total servicing demand). 

In the 2009 Final Rule, EPA determined that it was desirable to institute a year-by-year 

reduction for the period 2010-2014. The Agency is maintaining that policy in this interim final 

action for 2011. A smooth transition for stakeholders – including continued availability of 
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needed material for approved uses – has historically been an essential aspect of U.S. success in 

implementing the Montreal Protocol and CAA requirements. To ease the transition to 2015 and 

avoid disruptions to the market and shortages in HCFC-22 at that date, it is necessary to take 

steps now to foster the development of a robust recovery and recycling industry in the U.S. 

 EPA determined in the 2009 Final Rule the level of allocation that would meet the 

servicing demand over 2010-2014. In this interim final action, EPA is maintaining the overall 

HCFC-22 allocation levels for 2011 that the Agency determined were appropriate in the 2009 

Final Rule. Since EPA is not banning the use of existing HCFC-22 appliances manufactured 

prior to January 1, 2010, reused, recycled, and reclaimed HCFC-22 will become more valuable 

as the phaseout progresses. The demand for HCFC-22 to service existing equipment will provide 

an economic incentive to increase the quantities of recovered HCFC-22 available for reuse, 

recycling, and reclamation. The docket for the 2009 Final Rule (EPA-HQ-OAR-2008-0496) 

provides further information on EPA’s assumptions regarding the availability of reused, recycled 

and reclaimed HCFC-22 to meet servicing demand. 

Because the primary benefit of annually reducing the allocation is to ensure demand in 

2015 is met through greater recovery and reclamation, EPA continues to believe that it is 

appropriate to base the allocation on that goal. In developing the 2009 Final Rule, EPA estimated 

demand in 2015 for HCFC-22 would be 38,800 MT. Were the allocations to consist entirely of 

HCFC-22, the cap would limit the 2015 HCFC-22 allocation to only 27,709 MT, a difference of 

11,091 MT that would have to be made up with recovered material. Furthermore, it is likely that 

the allocation in 2015 will not consist entirely of HCFC-22, as EPA will need to reserve room 

under the cap for other HCFCs. In the 2009 Final Rule, EPA determined it was appropriate to 

establish an annual step-down such that the amount of total demand to be met from recovered 

HCFC-22 would equal 12,500 MT each year. This is approximately the amount EPA projected 

would be needed to meet the servicing demand in 2015. EPA is retaining this approach for 2011 
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in the interim final rule. Under this approach, the allocations equal approximately 45,400 MT in 

2011. These values, shown in the table below, are derived by subtracting 12,500 MT from the 

estimated demand each year. EPA will not issue HCFC-22 and HCFC-142b allowances for 2012 

or later until a future rulemaking. Consistent with the 2009 Final Rule, EPA plans to reduce the 

allocation amount annually in future rulemakings to reflect the declining servicing demand. 

2010 2011 

Estimated Demand (MT) 62,500 57,900 

Total Allocation (MT) 50,000 45,400 

Recovered Amount (MT) 12,500 12,500 

As the total demand decreases, maintaining the supply of recovered HCFCs at a constant 

level results in recovered material comprising a greater proportion of the total demand each year. 

Under this approach, the percentage of the total demand to be met with recovered material will 

rise from 20 percent of total demand in 2010 to 21.6 percent in 2011, though the total amount of 

recovered material needed remains at 12,500 MT for both years. EPA still believes this is 

appropriate as it facilitates meeting the demand in 2015, of which at least 29 percent must be met 

with recovered material, but takes comment on whether demand for HCFC-22 has changed since 

the 2009 Final Rule was published. Additionally, EPA is taking comment on whether there is 

surplus HCFC-22 on the U.S. market. In particular, EPA is interested in learning more about (1) 

the current amount of recovered HCFC-22 that is available for reclamation or reuse in another 

HCFC-22 system; (2) the amount of surplus HCFC-22 (virgin and reclaimed) in inventory; and 

(3) the amount of recovered HCFC-22 abroad awaiting import into the U.S. for reclamation 

and/or reuse. If new information shows a different amount of HCFC-22 should be allocated in 

future control periods to encourage reclamation and ensure a smooth transition, EPA will explore 

options to address this in a later proposed rule. 

C. Allocations of HCFC-22 and HCFC-142b 
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 EPA is revising the tables in 40 CFR 82 that together specify the production and 

consumption allowances available to allowance holders during specified control periods. The 

tables at sections 82.17 and 82.19 apportion baseline production allowances and baseline 

consumption allowances, respectively, to individual companies for individual HCFCs during a 

particular regulatory period. Complementing these tables, the table at section 82.16 lists the 

percentage of baseline allocated to allowance holders for specific control periods. In the interim 

final rule, EPA is retaining this framework of complementary tables, revising them to reflect the 

Court’s vacatur, responding to the Court’s remand by making adjustments to the previous 

baselines consistent with the Court’s ruling, and granting percentages of baselines in a manner 

that achieves the 2010 phaseout step and lays the groundwork for the next phaseout step in 2015. 

 In the 2009 Final Rule, the percent allocation for HCFC-22 for 2011 was 38.0 percent of 

baseline. In the interim final rule, the value is 32.0 percent. The percent allocation for HCFC142b for 2011 was 0.47 percent of baseline in the 2009 Final Rule and is 4.9 percent of baseline 

in this interim final rule. These changes do not reflect a change in the total consumption 

allocation amounts for each substance, as the total allocation for HCFC-22 in 2011 remains 

approximately 45,400 MT (the same as the 2009 Final Rule), and the total allocation for HCFC142b in 2011 remains at approximately 100 MT. Using the same percentage of baseline to 

allocate production allowances as consumption allowances, the total HCFC-22 production 

allocation is smaller than in the 2009 final rule by less than two percent. The lower amount is 

due to the change in company baselines to reflect the Court’s decision on the 2008 inter-pollutant 

baseline transfers, and not a change in the methodology used to determine allowances. More 

information is available on this subject in Section V.C.2. 

 The 2009 Final Rule, which did not treat the 2008 transfers of HCFC-142b to HCFC-22 

baseline allowances as carrying forward into the next regulatory period, had a total HCFC-22 

consumption baseline of 119,384 MT. In this interim final rule, EPA is reflecting the baseline 
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transfers in section 82.19 in accordance with the Court’s decision. As a result, the aggregate 

HCFC-22 consumption baseline has increased to 141,865 MT. Since the aggregate HCFC-22 

baseline is now higher due to the increase in the number of HCFC-22 baseline allowances for 

Arkema, Inc. and Solvay Fluorides, LLC, EPA is allocating a smaller percentage of the 

company-specific baselines than in the 2009 Final Rule to achieve the same total number of 

allowances. Thus, 45,400 MT of HCFC-22 consumption (the aggregate allocation amount in 

2011) is equal to 38.0 percent of 119,384 MT (baseline) of HCFC-22 in the 2009 Final Rule, and 

32.0 percent of 141,865 MT (baseline) in this interim final rule. The aggregate HCFC-22 

production baseline is also increasing from 110,619 MT in the 2009 Final Rule to 129,093 MT in 

this interim final rule to reflect Arkema, Inc.’s transfer of HCFC-142b baseline production 

allowances to HCFC-22 baseline production allowances. 

 The opposite is true for HCFC-142b, which had a larger aggregate consumption baseline 

in the proposed rule (21,089 MT), but now has a smaller baseline (2,047 MT) since EPA is 

accounting for inter-pollutant transfers from HCFC-142b to HCFC-22. Thus, 100 MT of HCFC142b consumption allowances (the aggregate allocation amount in 2011) are equal to 0.47 

percent of 21,089 MT of HCFC-142b in the 2009 Final Rule, and 4.9 percent of 2,047 MT in this 

interim final rule. Aggregate HCFC-142b baseline production allowances are decreasing from 

25,090 MT in the 2009 Final Rule to 9,444 MT in this interim final rule to reflect Arkema, Inc.’s 

transfer of HCFC-142b baseline production allowances. 

 EPA is removing the vacated text relating to HCFC-22 and HCFC-142b from the tables 

in sections 82.16, 82.17, and 82.19; adding new production and consumption baselines for those 

substances for 2011 to the tables at sections 82.17 and 82.19; and adding new specified 

percentages of baseline for those substances to the table in section 82.16 for the 2011 control 

period. 

Table 1- Phaseout Schedule for Class II Controlled Substances in 40 CFR 82.16 
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Control 

Period 

Percent of 

HCFC141b 

Percent of 

HCFC-22 

Percent of 

HCFC142b 

Percent of 

HCFC-123

Percent of 

HCFC-124

Percent of 

HCFC225ca 

Percent of 

HCFC225cb 

2003 0 100 100 -- -- -- -- 

2004 0 100 100 -- -- -- -- 

2005 0 100 100 -- -- -- -- 

2006 0 100 100 -- -- -- -- 

2007 0 100 100 -- -- -- -- 

2008 0 100 100 -- -- -- -- 

2009 0 100 100 -- -- -- -- 

2010 0 41.9 0.47 125 125 125 125 

2011 0 32.0 4.9 125 125 125 125 

2012 0 -- -- 125 125 125 125 

2013 0 -- -- 125 125 125 125 

2014 0 -- -- 125 125 125 125 

 Consistent with the 2009 Final Rule, EPA is allocating different baseline percentages for 

HCFC-22 and HCFC-142b because EPA projects that the needs will differ for servicing airconditioning and refrigeration appliances during the 2011 control period. As discussed in Section 

V.B.1., the analysis prepared for the 2009 Final Rule showed there will be a significantly greater 

need for HCFC-22 than for HCFC-142b during 2011. Based on the Servicing Tail Report and 

reporting information already required by EPA regulations, the needs for individual HCFCs are 

not uniform. EPA determined in the 2009 Final Rule 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. While annual inter-pollutant transfers in accordance with 

section 82.23(b) could be used to transfer allowances of one HCFC for another on a temporary 

basis, EPA continues to believe it is not appropriate to rely on such transfers as a mechanism for 

large-scale corrections. Instead, EPA anticipates that the continued availability of annual, 

temporary inter-pollutant transfers will permit the market to self-correct for unforeseen changes 

in demand and allow entities to consider a range of options for their allowances. EPA seeks to 

avoid unnecessary disruptions in the marketplace and to promote a smooth transition for society. 
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1. HCFC-22 Consumption Allowances for 2011 

For 2011, EPA is allocating HCFC-22 consumption allowances to meet about 78 percent 

of the servicing need, assuming the remainder will be met by recovered HCFC-22 that is either 

reused, recycled, or reclaimed. This translates into approximately 45,400 MT (2,497 ODPweighted MT), or 66 percent of the total HCFC consumption cap for the 2011 control period. 

2. HCFC-22 Production Allowances for 2011 

For purposes of the 2011 interim final rule, EPA is not revisiting its determination in the 

2009 Final Rule to use the same percentages for production and consumption allocations – 

deriving the percentages based on estimated need for each individual HCFC. Therefore, this rule 

allocates 41,310 MT (2,272 ODP-weighted MT of the 3,884.25 ODP-weighted metric ton 

production cap) to HCFC-22 production in 2011. The 2011 aggregate allocation is 1.7 percent 

lower than the amount allocated in the 2009 Final Rule (41,310 MT in this Interim Final Rule vs. 

42,035 MT in the 2009 Final Rule) because the aggregate amount of baseline production 

allowances in this rulemaking did not increase by the same relative amount as aggregate baseline 

consumption allowances. Because Solvay did not transfer its HCFC-142b production allowances 

to HCFC-22 production allowances, consumption allowances are 18.8 percent higher in this rule, 

while production allowances are only 16.7 percent higher. The memo to the docket for this 

rulemaking (EPA-HQ-OAR-2010-1040) titled “HCFC-22 and HCFC- 142b Allocation 

Adjustments: 2009 Final Rule vs. 2011 Interim Final Rule,” discusses the slight differences in 

allocation amounts in more detail. 

While some allowance holders have encouraged EPA to increase the number of 

production allowances allocated in 2011, EPA is not allocating additional production allowances 

in this interim final rule for several reasons. First, EPA is relying on the existing record for the 

2009 Final Rule, in which the Agency determined it was appropriate to allocate production and 

consumption allowances at the same percentage of baseline. EPA believes it is important to 
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obtain public comment on this issue before changing course. Second, in the 2009 Final Rule, 

EPA stated that allocating the same percentage of baseline for production and consumption was 

“consistent with section 605(c) of the Clean Air Act, which requires that the phaseout schedule 

for HCFC consumption be the same as that for HCFC production” (74 FR 66429). EPA has 

given further thought to this provision and is seeking public comment on its interpretation before 

any changes in policy. Third, EPA has not previously taken comment on whether there would be 

environmental implications associated with such a change. Given these three considerations, 

EPA believes it would not be appropriate to increase the production amount without providing 

notice and an opportunity to comment. 

While this interim final rule contains the same allocation percentages for production and 

consumption, EPA welcomes comment on whether it should use different percentages to allocate 

HCFC-22 production and consumption allowances in 2011 and/or future control periods. From a 

policy perspective, EPA is interested in comments on whether an increase in the total number of 

HCFC-22 production allowances would result in greater total HCFC production, either in the 

U.S. or globally. EPA notes that production of 1 kilogram of an HCFC requires both a 

production allowance and a consumption allowance (82.15(a)(1),(2)). Thus, an increase in 

production allowances without a corresponding increase in consumption allowances does not 

automatically result in greater production. The most likely scenario is that an increase in 

production allowances would result in greater U.S. production for export. This is because as 

stated in 82.20(a), “A person may obtain at any time during the control period...consumption 

allowances equivalent to the quantity of class II controlled substances that the person exported 

from the U.S. and its territories to a foreign state...when that quantity of class II controlled 

substance was produced in the U.S. ...with expended consumption allowances.” In effect, 

current EPA regulations allow exporters to receive a refund of one consumption allowance for 

each kilogram they export if they show one consumption and one production allowance were 
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expended for the material exported. Therefore, EPA would not expect an increase in production 

allowances to result in greater amounts of HCFCs being used in the U.S. EPA welcomes 

comment on whether an increase in the level of production allowances would result in more U.S. 

production, either for domestic use or for export, and whether any additional U.S. production for 

export would result in greater worldwide production of HCFCs. 

From a legal perspective, EPA is interested in comments on whether section 605(c) 

would preclude allocating a different percentage of baseline for production than for 

consumption. Section 605(c) states that EPA must “promulgate regulations phasing out the 

production . . . of class II substances in accordance with [section 605],” subject to any 

acceleration under section 606. It further states that EPA must “promulgate regulations to insure 

that the consumption of class II substances in the United States is phased out and terminated in 

accordance with the same schedule . . . as is applicable to the phase-out and termination of 

production of class II substances under [Title VI].” EPA is considering three possible 

interpretations of the term “schedule” as referenced in section 605(c): (1) the schedule that 

appears on the face of section 605, which contains no deadlines until 2015; (2) the schedule that 

appears on the face of section 605, as accelerated under section 606; and (3) the specific 

allocation percentages or amounts established by EPA through rulemaking for each control 

period. EPA believes that the second interpretation is the most consistent with the statutory 

language and purpose. 

In past actions, the Agency has accelerated the initial schedule in section 605 to reflect 

modifications to the Montreal Protocol phaseout schedule for HCFCs. Under the 2007 Montreal 

Adjustment (reflected in Decision XIX/6), the U.S. is obligated to reduce HCFC production and 

consumption 75 percent below its aggregate baseline by 2010. EPA is not proposing to increase 

production to an amount that would be inconsistent with that obligation. Instead, EPA is taking 

comment on whether to allow production to increase relative to consumption, without 
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encroaching on the cap. Specifically, EPA is taking comment on whether to issue additional 

production allowances in the amount of 7,746 MT when compared to this interim final rule. 

If EPA were to decide to increase production allowances in 2011, its preferred approach 

would be to decouple the percentage of baseline allocated for production from the percentage of 

baseline allocated for consumption. EPA would effectuate this change in its regulations by 

replacing the table at 40 CFR 82.16 with two tables. One would allocate 32 percent of baseline 

for consumption allowances in 2011. The other would allocate 38 percent of baseline for 

production allowances in 2011. This approach would still provide the petitioners in Arkema v. 

EPA the benefit of their 2008 baseline transfers while giving other companies with production 

baselines approximately the same number of production allowances as they received in the 2009 

Final Rule. Compared to the 2009 Final Rule, the net result would be 7,020 MT (386 ODPweighted MT) additional HCFC-22 production allowed in 2011 for a total of 49,055 MT (2,698 

ODP-weighted MT). Under this scenario, the U.S. would be 1,021 ODP-weighted MT below the 

production cap and in compliance with its obligations under the Montreal Protocol. EPA is 

seeking comment on whether this increase would hinder the transition to the 2015 phaseout step, 

under which the U.S. is obligated to reduce HCFC production and consumption 90 percent below 

its aggregate baseline. EPA’s preference is to continue to use the same percentages for 

production and consumption allocations. This is because EPA is concerned this action could 

increase U.S. production of HCFCs, might decrease the U.S.’s ability to transition to the 2015 

stepdown under the Montreal Protocol, and potentially increase global production of HCFCs. 

Nevertheless, the Agency welcomes comment on this option for increasing 2011 and/or future 

HCFC-22 production allowances. After reviewing comments, EPA may either issue a 

supplemental allocation of production allowances for 2011 or leave the 2011 production 

allocation in this interim final rule unchanged. 

3. HCFC-142b Allowances for 2011
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 Establishing HCFC-142b baseline allowances that take into account the 2008 interpollutant transfers discussed in Section II.D. results in 2,047 MT of aggregate baseline 

consumption allowances and 9,444 MT of aggregate baseline production allowances. Consistent 

with the 2009 Final Rule, EPA is allocating 100 percent of the projected servicing need for 

HCFC-142b identified in that rule: 100 MT (7 ODP-weighted MT) of consumption. To get to 

that level of consumption, EPA is allocating 4.9 percent of the aggregate consumption baseline, 

as reflected in the table at section 82.16. The aggregate allocation number for consumption is the 

same as in the 2009 Final Rule. 

 Using the same percentage (4.9 percent), EPA is allocating 463 MT (30.1 ODP-weighted 

MT) of HCFC-142b production allowances for 2011. The 2011 aggregate allocation for 

production is higher than the amount allocated in the 2009 Final Rule (463 MT in this interim 

final rule vs. 118 MT in the 2009 Final Rule). The allocated amount is 292 percent higher than in 

the 2009 Final Rule because the aggregate amount of baseline HCFC-142b consumption 

allowances in this rulemaking decreased by a significantly larger amount than aggregate baseline 

HCFC-142b production allowances. Baseline consumption allowances are 90.3 percent lower in 

this rule, while baseline production allowances are only 62.4 percent lower. This occurred 

because Solvay did not transfer its HCFC-142b production allowances to HCFC-22 production 

allowances. This higher amount of calendar-year production does not affect the U.S.’s ability to 

meet its obligations under the Montreal Protocol. The memo to the docket for this rulemaking 

(EPA-HQ-OAR-2010-1040) titled “HCFC-22 and HCFC- 142b Allocation Adjustments: 2009 

Final Rule vs. 2011 Interim Final Rule,” discusses the differences in exact allocation amounts in 

more detail. 

 4. How the Aggregate for HCFC-22 and HCFC-142b Translates Entity-by-Entity

 EPA is allocating (1) approximately 45,400 MT of HCFC-22 consumption allowances, 

(2) 41,310 MT of HCFC-22 production allowances, (3) approximately 100 MT of HCFC-142b 
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consumption allowances, and (4) 463 MT of HCFC-142b production allowances for 2011. 

However, EPA actually allocates allowances to individual companies (i.e., legal entities).

 Company-specific production and consumption baselines (also referred to as “baseline 

allowances”) for HCFC-142b and HCFC-22 are listed at sections 82.17 and 82.19, respectively. 

The percentage of baseline each entity will receive in 2011 appears at section 82.16(a), as shown 

in Table 1 above. 

 Allowances allocated for individual control periods are called “calendar-year allowances” 

to distinguish them from the baseline production or consumption. For 2011, EPA is apportioning 

production and consumption baselines for HCFC-22 and HCFC-142b on the same basis as in the 

2009 Final Rule, except that EPA is making adjustments to reflect (1) the 2008 inter-pollutant 

transfers of baseline allowances deemed permanent by the Court, (2) inter-company, singlepollutant transfers of baseline allowances that occurred in 2010, and (3) changes in company 

names that occurred after the 2009 Final Rule was signed. Applying the approach described 

above, EPA is apportioning production and consumption baselines for HCFC-22 and HCFC142b to the following entities in the following amounts: 

Table 2: Baseline Production Allowances of HCFC-22 and HCFC-142b in 40 CFR 82.17 

Person Controlled Substance Allowances (kg) 

Arkema 

HCFC-22 46,692,336

HCFC-142b 484,369

DuPont HCFC-22 42,638,049

Honeywell 

HCFC-22 37,378,252

HCFC-142b 2,417,534

MDA Manufacturing HCFC-22 2,383,835

Solvay Solexis HCFC-142b 6,541,764

Table 3: Baseline Consumption Allowances of HCFC-22 and HCFC-142b in 40 CFR 82.19 

Person Controlled Substance Allowances (kg) 

ABCO Refrigeration Supply HCFC-22 279,366

Altair Partners HCFC-22 302,011

Arkema HCFC-22 48,637,642
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HCFC-142b 483,827

Carrier Corporation HCFC-22 54,088

Coolgas Investment Property HCFC-22 1,040,458

DuPont HCFC-22 38,814,862

HCFC-142b 52,797

H.G. Refrigeration Supply HCFC-22 40,068

Honeywell HCFC-22 35,392,492

HCFC-142b 1,315,819

Mexichem Fluor Inc. HCFC-22 2,546,305

Kivlan & Company HCFC-22 2,081,018

MDA Manufacturing HCFC-22 2,541,545

Mondy Global HCFC-22 281,824

National Refrigerants HCFC-22 5,528,316

Refricenter of Miami HCFC-22 381,293

Refricentro HCFC-22 45,979

R-Lines HCFC-22 63,172

Saez Distributors HCFC-22 37,936

Solvay Fluorides HCFC-22 3,781,691

Solvay Solexis HCFC-142b 194,536

USA Refrigerants HCFC-22 14,865

D. HCFC-141b, HCFC-123, HCFC-124, HCFC-225ca, and HCFC-225cb Allowances 

Other than adjustments for inter-company, single-pollutant transfers of baseline 

allowances, baselines and percentages of baseline allocated as calendar-year allowances for 

HCFC-141b, HCFC-123, HCFC-124, HCFC-225ca, and HCFC-225cb are unchanged from the 

2009 Final Rule. In the case of HCFC-141b, EPA is continuing to allocate 0 percent of baseline 

for U.S. consumption and production, consistent with 40 CFR 82.16(b). 

E. Other HCFCs 

 As a result of EPA’s allocation process, which is largely based on projected demand for 

HCFC-22 and HCFC-142b, minus an amount of HCFC-22 that is assumed to be reused, 

recycled, or reclaimed, the total allocation is lower than the aggregate HCFC cap under the 

Montreal Protocol. EPA recognizes that there could be some additional need for HCFCs not 

specifically included in this rule. While some niche applications in the U.S. use other HCFCs, 

such as HCFC-21, EPA is not aware of additional need for production or import of these 

substances at this time, as adequate amounts appear to be in inventory. However, EPA is not 
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foreclosing the possibility of additional production or import for these niche uses. Also, some 

amount of HCFC-141b will likely continue to be produced or imported via the petition process 

during 2011. EPA believes there is sufficient room under the cap for such continued production 

and import. The current regulations at 40 CFR 82.15 ban the production and import of class II 

substances for which EPA has apportioned baseline production and consumption allowances in 

excess of allowances held by the producer or importer, but do not ban the production and import 

of class II substances for which EPA has not apportioned baseline production and consumption 

allowances. This rule does not alter the current regulations in that respect. The producer or 

importer of an HCFC that is not subject to the allowance system would be required to report to 

EPA consistent with the existing recordkeeping and reporting requirements. If necessary, EPA 

could amend the regulations to set and apportion baselines and issue allowances for these 

HCFCs. Therefore, retaining room under the cap provides the benefit of accounting for 

unanticipated growth in HCFCs that do not have allocations or other unforeseen events. 

However, EPA is not reserving room under the cap for the above-described reasons. EPA is 

allocating allowances based on modeled demand for virgin and recovered material in preparation 

for the next major stepdown period under the Montreal Protocol in 2015. 

VI. Statutory and Executive Order Reviews 

A. Executive Order 12866: Regulatory Planning and Review and Executive Order 13563: 

Improving Regulation and Regulatory Review 

 Under Executive Order (EO) 12866 (58 FR 51735, October 4, 1993), this action is a 

"significant regulatory action” since it raises “novel legal or policy issues.” Accordingly, EPA 

submitted this action to the Office of Management and Budget (OMB) for review under 

Executive Orders 12866 and 13563 (76 FR 3821, January 21, 2011) and any changes made in 

response to OMB recommendations have been documented in the docket for this action. 

 EPA did not conduct a specific analysis of the benefits and costs associated with this 
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action. Many previous analyses provide a wealth of information on the costs and benefits of the 

U.S. HCFC phaseout including: 

• The 1993 Addendum to the 1992 Phaseout Regulatory Impact Analysis: Accelerating the 

Phaseout of CFCs, Halons, Methyl Chloroform, Carbon Tetrachloride, and HCFCs. 

• The 1999 Report Costs and Benefits of the HCFC Allowance Allocation System. 

• The 2000 Memorandum Cost/Benefit Comparison of the HCFC Allowance Allocation 

System. 

• The 2005 Memorandum Recommended Scenarios for HCFC Phaseout Costs Estimation. 

• The 2006 ICR Reporting and Recordkeeping Requirements of the HCFC Allowance 

System. 

• The 2007 Memorandum Preliminary Estimates of the Incremental Cost of the HCFC 

Phaseout in Article 5 Countries. 

• The 2007 Memorandum Revised Ozone and Climate Benefits Associated with the 2010 

HCFC Production and Consumption Stepwise Reductions and a Ban on HCFC Precharged Imports. 

A memorandum summarizing these analyses is available in the docket. 

B. Paperwork Reduction Act 

 This action does not impose any new information collection burden. EPA already 

requires recordkeeping and reporting for HCFCs, and this action does not amend those 

provisions. The Office of Management and Budget (OMB) has previously approved the 

information collection requirements contained in the existing regulations at 40 CFR part 82, 

subpart A under the provisions of the Paperwork Reduction Act, 44 U.S.C. 3501 et seq. and has 
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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. Because this rule is not subject to notice-and-comment rulemaking 

requirements, the RFA does not apply and the Agency is not required to conduct a regulatory 

flexibility analysis. 

Nevertheless, in the spirit of the RFA, we have considered the economic impacts of this 

interim final rule on small entities. For purposes of assessing the impacts of this rule on small 

entities, a small entity is defined as: (1) a small business as defined by the Small Business 

Administration’s (SBA) regulations at 13 CFR 121.201; (2) a small governmental jurisdiction 

that is a government of a city, county, town, school district or special district with a population of 

less than 50,000; and (3) a small organization that is any not-for-profit enterprise which is 

independently owned and operated and is not dominant in its field. 

 This action will affect the following categories: 

Category NAICS code SIC code Examples of regulated entities 

Industrial Gas Manufacturing 

325120 2869 

Fluorinated hydrocarbon gases 

manufacturers and reclaimers 

Other Chemical and Allied 

Products Merchant 

Wholesalers 422690 5169 

Chemical gases and compressed 

gases merchant wholesalers 
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Category NAICS code SIC code Examples of regulated entities 

Air-Conditioning and Warm 

Air Heating Equipment and 

Commercial and Industrial 

Refrigeration Equipment 

Manufacturing 333415 3585 

Air-conditioning equipment and 

commercial and industrial 

refrigeration equipment 

manufacturers 

Air-Conditioning Equipment 

and Supplies Merchant 

Wholesalers 423730 5075 

Air-conditioning (condensing unit, 

compressors) merchant wholesalers

Electrical and Electronic 

Appliance, Television, and 

Radio Set Merchant 

Wholesalers 423620 5064 

Air-conditioning (room units) 

merchant wholesalers 

Plumbing, Heating, and AirConditioning Contractors 

238220 1711, 7623 

Central air-conditioning system and 

commercial refrigeration 

installation; HVAC contractors 

 After considering the economic impacts of this interim final rule on small entities, I 

certify this action will not have a significant economic impact on a substantial number of small 

entities as it relieves a regulatory ban on production and consumption that would otherwise apply 

in the wake of the Court’s vacatur. EPA is continuing to allocate production and consumption 

allowances using the same approach described in the 2009 Final Rule with adjustments to reflect 

(1) 2008 inter-pollutant transfers of baseline allowances deemed permanent by the Court, (2) 

inter-company, single-pollutant transfers of baseline allowances that occurred in 2010, and (3) 

changes in company names that occurred after the 2009 Final Rule was signed. EPA is not 

modifying the recordkeeping or reporting provisions and thus is not increasing the burden to 

small businesses. 

D. Unfunded Mandates Reform Act 

 This action contains no Federal mandates under the provisions of Title II of the Unfunded 

Mandates Reform Act of 1995 (UMRA), 2 U.S.C. 1531-1538 for State, local, or tribal 

governments or the private sector. First, UMRA does not apply to rules that are necessary for the 

implementation of international treaty obligations. This rule implements the 2010 milestone for 
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the phaseout of HCFCs under the Montreal Protocol. Second, this action relieves the regulatory 

ban on production and consumption that would otherwise apply. This action will not have any 

significant direct impacts or State, local and tribal governments or private sector entities. 

Therefore, 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 action apportions production and consumption allowances and establishes 

baselines for private entities, not small governments. 

E. Executive Order 13132: Federalism 

 Executive Order 13132, titled “Federalism” (64 FR 43255, August 10, 1999), requires 

EPA to develop an accountable process to ensure “meaningful and timely input by State and 

local officials in the development of regulatory policies that have federalism implications.” 

“Policies that have federalism implications” is defined in the Executive Order to include 

regulations that have “substantial direct effects on the States, on the relationship between the 

national government and the States, or on the distribution of power and responsibilities among 

the various levels of government.” 

 This action does not have federalism implications. It does not have substantial direct 

effects on the States, on the relationship between the national government and the States, or on 

the distribution of power and responsibilities among the various levels of government, as 

specified in Executive Order 13132. This action is expected to primarily affect producers, 

importers, and exporters of HCFCs. Thus, the requirements of section 6 of the Executive Order 

do not apply. 

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

 This action does not have tribal implications, as specified in Executive Order 13175 (65 

FR 67249, November 9, 2000). This action does not significantly or uniquely affect the 
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communities of Indian tribal governments. It does not impose any enforceable duties on 

communities of Indian tribal governments. Thus, Executive Order 13175 does not apply to this 

action. 

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

Risks 

 This action is not subject to EO 13045 (62 F.R. 19885, April 23, 1997) because it is not 

economically significant as defined in EO 12866. The Agency nonetheless has reason to believe 

that the environmental health or safety risk addressed by this action may have a disproportionate 

effect on children. Depletion of stratospheric ozone results in greater transmission of the sun’s 

ultraviolet (UV) radiation to the earth’s surface. The following studies describe the effects of 

excessive exposure to UV radiation on children: (1) Westerdahl J, Olsson H, Ingvar C. “At what 

age do sunburn episodes play a crucial role for the development of malignant melanoma,” Eur J 

Cancer 1994: 30A: 1647-54; (2) Elwood JM Japson J. “Melanoma and sun exposure: an 

overview of published studies,” Int J Cancer 1997; 73:198-203; (3) Armstrong BK, “Melanoma: 

childhood or lifelong sun exposure,” In: Grobb JJ, Stern RS Mackie RM, Weinstock WA, eds. 

“Epidemiology, causes and prevention of skin diseases,” 1st ed. London, England: Blackwell 

Science, 1997: 63-6; (4) Whiteman D., Green A. “Melanoma and Sunburn,” Cancer Causes 

Control, 1994: 5:564-72; (5) Heenan, PJ. “Does intermittent sun exposure cause basal cell 

carcinoma? A case control study in Western Australia,” Int J Cancer 1995; 60: 489-94; (6) 

Gallagher, RP, Hill, GB, Bajdik, CD, et. al. “Sunlight exposure, pigmentary factors, and risk of 

nonmelanocytic skin cancer I, Basal cell carcinoma,” Arch Dermatol 1995; 131: 157-63; (7) 

Armstrong, DK. “How sun exposure causes skin cancer: an epidemiological perspective,” 

Prevention of Skin Cancer. 2004. 89-116. 

 This action implements the U.S. commitment to reduce the total basket of HCFCs 

produced and imported to a level that is 75 percent below the respective baselines. While on an 
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ODP-weighted basis, this is not as large a step as previous actions, such as the 1996 Class I 

phaseout, it is one of the most significant remaining actions the U.S. can take to complete the 

overall phaseout of ODS and further decrease impacts on children’s health from stratospheric 

ozone depletion. 

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

Use 

 This action is not a “significant energy action” as defined in Executive Order 13211 (66 

FR 28355 (May 22, 2001)), because it is not likely to have a significant adverse effect on the 

supply, distribution, or use of energy. The rule issues allowances for the production and 

consumption of HCFCs. 

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 action does not involve technical standards. 

Therefore, EPA did not consider the use of any voluntary consensus standards. 

J. Executive Order 12898: Federal Actions to Address Environmental Justice in Minority 

Populations and Low-Income Populations 

Executive Order (EO) 12898 (59 FR 7629 (Feb. 16, 1994)) establishes federal executive 

policy on environmental justice. Its main provision directs federal agencies, to the greatest extent 

practicable and permitted by law, to make environmental justice part of their mission by 
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identifying and addressing, as appropriate, disproportionately high and adverse human health or 

environmental effects of their programs, policies, and activities on minority populations and lowincome populations in the U.S. 

 EPA has determined that this action will not have disproportionately high and adverse 

human health or environmental effects on minority or low-income populations because the 2010 

phaseout step increases the level of environmental protection for all affected populations without 

having any disproportionately high and adverse human health or environmental effects on any 

population, including any minority or low-income population. This action continues the 

implementation of the U.S. commitment to reduce the total basket of HCFCs produced and 

imported to a level that is 75 percent below the respective baselines. While on an ODP-weighted 

basis, this is not as large a step as previous actions, such as the 1996 Class I phaseout, it is one of 

the most significant remaining actions the U.S. can take to complete the overall phaseout of ODS 

and further lessen the adverse human health effects for the entire population. 

K. The Congressional Review Act 

The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the Small Business 

Regulatory Enforcement Fairness Act of 1996, generally provides that before a rule may take 

effect, the agency promulgating the rule must submit a rule report, which includes a copy of the 

rule, to each House of the Congress and to the Comptroller General of the U.S.. EPA will submit 

a report containing this rule and other required information to the U.S. Senate, the U.S. House of 

Representatives, and the Comptroller General of the U.S. prior to publication of the rule in the 

Federal Register. A major rule cannot take effect until 60 days after it is published in the Federal 

Register. This action is not a “major rule” as defined by 5 U.S.C. 804(2). This rule will be 

effective [INSERT DATE OF PUBLICATION IN THE FEDERAL REGISTER]. 

List of Subjects in 40 CFR Part 82 
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Environmental protection, Administrative practice and procedure, Air pollution control, 

Chemicals, Exports, Hydrochlorofluorocarbons, Imports 

 

DATED: ____________________________ 

___________________________________ 

Lisa P. Jackson, 

Administrator. 

40 CFR part 82 is amended to read as follows: 

PART 82-PROTECTION OF STRATOSPHERIC OZONE 

1. 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: 

Control 

Period 

Percent of 

HCFC141b 

Percent of 

HCFC-22 

Percent of 

HCFC142b 

Percent of 

HCFC-123

Percent of 

HCFC-124

Percent of 

HCFC225ca 

Percent of 

HCFC225cb 

2003 0 100 100 -- -- -- -- 

2004 0 100 100 -- -- -- -- 

2005 0 100 100 -- -- -- -- 

2006 0 100 100 -- -- -- -- 

2007 0 100 100 -- -- -- -- 

2008 0 100 100 -- -- -- -- 

2009 0 100 100 -- -- -- -- 

Protection of Stratospheric Ozone: Protection of Stratospheric Ozone: 

Adjustments to the Allowance System for Controlling HCFC Production, Import, 

and Export (Page 54 of 57) 
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2010 0 41.9 0.47 125 125 125 125 

2011 0 32.0 4.9 125 125 125 125 

2012 0 -- -- 125 125 125 125 

2013 0 -- -- 125 125 125 125 

2014 0 -- -- 125 125 125 125 

* * * * * 

2. Revise §82.17 to read as follows: 

§82.17 Apportionment of baseline production allowances for class II controlled substances. 

The following persons are apportioned baseline production allowances for HCFC-22, HCFC141b, HCFC-142b, HCFC-123, HCFC-124, HCFC-225ca, and HCFC-225cb, as set forth in the 

following table: 

Person Controlled Substance Allowances (kg) 

AGC Chemicals Americas 

HCFC-225ca 266,608

HCFC-225cb 373,952

Arkema 

HCFC-22 46,692,336

HCFC-141b 24,647,925

HCFC-142b 484,369

DuPont 

HCFC-22 42,638,049

HCFC-124 2,269,210

Honeywell 

HCFC-22 37,378,252

HCFC-141b 28,705,200

HCFC-142b 2,417,534

HCFC-124 1,759,681

MDA Manufacturing HCFC-22 2,383,835

Solvay Solexis HCFC-142b 6,541,764

3. Section 82.19 is revised to read as follows: 

§82.19 Apportionment of baseline consumption allowances for class II controlled 

substances.
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The following persons are apportioned baseline consumption allowances for HCFC-22, HCFC141b, HCFC-142b, HCFC-123, HCFC-124, HCFC-225ca, and HCFC-225cb, as set forth in the 

following table: 

Person Controlled Substance Allowances (kg) 

ABCO Refrigeration Supply HCFC-22 279,366

AGC Chemicals Americas HCFC-225ca 285,328

HCFC-225cb 286,832

Altair Partners HCFC-22 302,011

Arkema 

HCFC-22 48,637,642

HCFC-141b 25,405,570

HCFC-142b 483,827

HCFC-124 3,719

Carrier HCFC-22 54,088

Continental Industrial Group HCFC-141b 20,315

Coolgas, Inc. HCFC-141b 16,097,869

Coolgas Investment Property 

HCFC-22 1,040,458

HCFC-123 19,980

HCFC-124 3,742

Discount Refrigerants HCFC-141b 994

DuPont 

HCFC-22 38,814,862

HCFC-141b 9,049

HCFC-142b 52,797

HCFC-123 1,877,042

HCFC-124 743,312

H.G. Refrigeration Supply HCFC-22 40,068

Honeywell 

HCFC-22 35,392,492

HCFC-141b 20,749,489

HCFC-142b 1,315,819

HCFC-124 1,284,265

ICC Chemical Corp. HCFC-141b 81,225

ICOR HCFC-124 81,220

Mexichem Fluor Inc. HCFC-22 2,546,305

Kivlan & Company HCFC-22 2,081,018

MDA Manufacturing HCFC-22 2,541,545

Mondy Global HCFC-22 281,824

National Refrigerants 

HCFC-22 5,528,316

HCFC-123 72,600

HCFC-124 50,380

Perfect Technology Center, LP HCFC-123 9,100

Refricenter of Miami HCFC-22 381,293

Refricentro HCFC-22 45,979

R-Lines HCFC-22 63,172

Saez Distributors HCFC-22 37,936
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Solvay Fluorides HCFC-22 3,781,691

HCFC-141b 3,940,115

Solvay Solexis HCFC-142b 194,536

Tulstar Products 

HCFC-141b 89,913

HCFC-123 34,800

HCFC-124 229,582

USA Refrigerants HCFC-22 14,865
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EO12866_CAA Part 82A 2060 AQ82 IFR FRN_20110531 

ENVIRONMENTAL PROTECTION AGENCY 

40 CFR Part 82 

[EPA-HQ-OAR-2010-1040; FRL-xxxx-x] 

RIN 2060-AQ82 

Protection of Stratospheric Ozone: Adjustments to the Allowance System for Controlling 

HCFC Production, Import, and Export 

AGENCY: Environmental Protection Agency [EPA]. 

ACTION: Interim final rule. 

SUMMARY: EPA is adjusting the allowance system controlling U.S. consumption and 

production of hydrochlorofluorocarbons (HCFCs) as a result of a recent court decision vacating a 

portion of the rule titled “Protection of Stratospheric Ozone: Adjustments to the Allowance 

System for Controlling HCFC Production, Import, and Export; Final Rule.” EPA interprets the 

court’s vacatur as applying to the part of the rule that establishes the company-by-company 

baselines and calendar-year allowances for HCFC-22 and HCFC-142b. This action relieves the 

regulatory ban on production and consumption of these two chemicals following the court’s 

vacatur by establishing new company-by-company HCFC-22 and HCFC-142b baselines and 

allocating production and consumption allowances for 2011. 

DATES: This rule is effective [INSERT DATE OF PUBLICATION IN FEDERAL 

REGISTER]. While the urgent need for certainty regarding the consumption allowance 

allocations in the 2011 control period precludes the Agency from considering any adjustments to 

the consumption allowances allocated in this action, EPA will consider all written comments 

received by [INSERT DATE 30 DAYS AFTER PUBLICATION DATE] to determine 

whether to issue additional production allowances for the time period covered by this action. 

Commenters may also submit comments on the issues addressed in this action as they pertain to 
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future control periods. 

ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-OAR-2010-

1040, by one of the following methods: 

• www.regulations.gov: Follow the on-line instructions for submitting comments. 

 • Email: a-and-r-docket@epa.gov

 • Fax: 202-566-1741 

• Mail: Docket # EPA-HQ-OAR-2010-1040, 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-2010-1040 Air and Radiation Docket at 

EPA West, 1301 Constitution Avenue NW, Room B108, Mail Code 6102T, 

Washington, D.C. 20004. Such deliveries are only accepted during the Docket’s 

normal hours of operation, and special arrangements should be made for 

deliveries of boxed information. 

Instructions: Direct your comments to Docket ID No. EPA-HQ-OAR-2010-1040. EPA's policy 

is that all comments received will be included in the public docket without change and may be 

made available online at www.regulations.gov, including any personal information provided, 

unless the comment includes information claimed to be Confidential Business Information (CBI) 

or other information whose disclosure is restricted by statute. Do not submit information that you 

consider to be CBI or otherwise protected through www.regulations.gov or e-mail. The 

www.regulations.gov website 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 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, 
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EPA recommends that you include your name and other contact information in the body of your 

comment and with any disk or CD-ROM you submit. If EPA cannot read your comment due to 

technical difficulties and cannot contact you for clarification, EPA may not be able to consider 

your comment. Electronic files should avoid the use of special characters, any form of 

encryption, and be free of any defects or viruses. For additional information about EPA’s public 

docket, visit the EPA Docket Center homepage at www.epa.gov/epahome/dockets.htm. 

FOR FURTHER INFORMATION CONTACT: Luke H. Hall-Jordan by telephone at (202) 

343-9591, or by e-mail at hall-jordan.luke@epa.gov, or by mail at U.S. Environmental 

Protection Agency, Stratospheric Protection Division, Stratospheric Program Implementation 

Branch (6205J), 1200 Pennsylvania Avenue, NW, Washington, D.C., 20460. You may also visit 

the Ozone Protection website of EPA’s Stratospheric Protection Division at 

www.epa.gov/ozone/strathome.html for further information about EPA’s Stratospheric Ozone 

Protection regulations, the science of ozone layer depletion, and related topics. 

SUPPLEMENTARY INFORMATION: 

Acronyms and Abbreviations. The following acronyms and abbreviations are used in this 

document. 

APA – Administrative Procedure Act 

CAA – Clean Air Act 

CAAA – Clean Air Act Amendments of 1990 

CFC – Chlorofluorocarbon 

CFR – Code of Federal Regulations 

EPA – Environmental Protection Agency 

FR – Federal Register 

HCFC – Hydrochlorofluorocarbon 

HVAC – Heating, Ventilating, and Air Conditioning 
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Montreal Protocol – Montreal Protocol on Substances that Deplete the Ozone Layer 

MOP – Meeting of the Parties 

MT – Metric Ton 

ODP – Ozone Depletion Potential 

ODS – Ozone-Depleting Substances 

Party – States and regional economic integration organizations that have consented to be bound 

by the Montreal Protocol on Substances that Deplete the Ozone Layer

Organization of This Document. The following outline is provided to aid in locating 

information in this preamble. 

I. Regulated Entities 

II. Background 

A. How Does the Montreal Protocol Phase Out HCFCs? 

B. How Does the Clean Air Act Phase Out HCFCs? 

C. What Sections of the Clean Air Act Apply to This Rulemaking? 

D. How Does This Action Relate to the Recent Court Decision? 

1. Addressing 2010 Allowances 

III. Justification for this Interim Final Rule 

IV. Summary of this Interim Final Action 

V. Allocation of Allowances for the 2011 Control Period 

 A. Baselines for HCFC-22 and HCFC-142b Allowances 

 1. Adjusting the Baseline for Inter-company and Inter-pollutant 

Transfers 

B. Factors for Considering Allocation Amounts for HCFC-22 and HCFC-142b 

1. The Importance of HCFC-22 Relative to HCFC-142b Servicing Needs for 

Existing Equipment 
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2. Meeting Servicing Needs with Virgin and Recovered Material 

3. Annual Reduction in Allocated Amounts 

C. Allocations of HCFC-22 and HCFC-142b 

1. HCFC-22 Consumption Allowances for 2011 

2. HCFC-22 Production Allowances for 2011 

3. HCFC-142b Allowances for 2011 

4. How the Aggregate for HCFC-22 and HCFC-142b Translates Entity-byEntity 

D. HCFC-141b, HCFC-123, HCFC-124, HCFC-225ca, and HCFC-225cb 

Allowances 

E. Other HCFCs 

VI. Statutory and Executive Order Reviews 

 A. Executive Order 12866: Regulatory Planning and Review and Executive Order 

13563: Improving Regulation and Regulatory Review 

 B. Paperwork Reduction Act 

 C. Regulatory Flexibility Act (RFA) 

 D. Unfunded Mandates Reform Act 

 E. Executive Order 13132: Federalism 

 F. Executive Order 13175: Consultation and Coordination with Indian Tribal 

Governments 

 G. Executive Order 13045: Protection of Children from Environmental Health and 

Safety Risks 

 H. Executive Order 13211: Actions that Significantly Affect Energy Supply, 

Distribution, or Use 

 I. National Technology Transfer Advancement Act 
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 J. Executive Order 12898: Federal Actions to Address Environmental Justice in 

Minority Populations and Low-Income Populations 

 K. Congressional Review Act 

I. Regulated Entities

 This rule will affect the following categories: 

Category NAICS code SIC code Examples of regulated entities 

Industrial Gas Manufacturing 

325120 2869 

Fluorinated hydrocarbon gases 

manufacturers and reclaimers 

Other Chemical and Allied 

Products Merchant 

Wholesalers 422690 5169 

Chemical gases and compressed 

gases merchant wholesalers 

Air-Conditioning and Warm 

Air Heating Equipment and 

Commercial and Industrial 

Refrigeration Equipment 

Manufacturing 333415 3585 

Air-conditioning equipment and 

commercial and industrial 

refrigeration equipment 

manufacturers 

Air-Conditioning Equipment 

and Supplies Merchant 

Wholesalers 423730 5075 

Air-conditioning (condensing unit, 

compressors) merchant wholesalers

Electrical and Electronic 

Appliance, Television, and 

Radio Set Merchant 

Wholesalers 423620 5064 

Air-conditioning (room units) 

merchant wholesalers 

Plumbing, Heating, and AirConditioning Contractors 

238220 1711, 7623 

Central air-conditioning system and 

commercial refrigeration 

installation; HVAC contractors 

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 could 

potentially be regulated by this action. Other types of entities not listed in this table could also be 

affected. To determine whether your facility, company, business organization, or other entity is 

regulated by this action, you should carefully examine these regulations. If you have questions 

regarding the applicability of this action to a particular entity, consult the person listed in the 

“FOR FURTHER INFORMATION CONTACT” section. 
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II. Background 

EPA is undertaking this rulemaking as a result of the decision issued by the U.S. Court of 

Appeals for the District of Columbia Circuit (Court) in Arkema v. EPA (618 F.3d 1, D.C. Cir. 

2010) regarding the December 15, 2009 final rule titled “Protection of Stratospheric Ozone: 

Adjustments to the Allowance System for Controlling HCFC Production, Import, and Export,” 

published at 74 FR 66413 (2009 Final Rule). Certain allowance holders affected by the 2009 

Final Rule filed petitions for judicial review of the rule under section 307(b) of the Clean Air 

Act. Among other arguments, the petitioners contended that the rule was impermissibly 

retroactive because in setting the baselines for the new regulatory period, EPA did not take into 

account certain inter-pollutant baseline transfers that petitioners had performed during the prior 

regulatory period. 

The Court issued a decision on August 27, 2010, agreeing with petitioners that “the 

[2009] Final Rule unacceptably alters transactions the EPA approved under the 2003 Rule” 

(Arkema v. EPA, 618 F.3d at 3). The Court vacated the rule in part, “insofar as it operates 

retroactively,” and remanded to EPA “for prompt resolution,” (618 F.3d at 10). The Court 

withheld the mandate for the decision pending the disposition of any petition for rehearing. 

EPA’s petition for rehearing was denied on January 21, 2011. The mandate issued on February 4, 

2011. More detail is provided on the case and EPA’s interpretation of the Court’s decision in 

Section II.D. 

A. How Does the Montreal Protocol Phase Out HCFCs? 

The Montreal Protocol on Substances that Deplete the Ozone Layer is the international 

agreement aimed at reducing and eventually eliminating the production and consumption of 

stratospheric ozone-depleting substances (ODS). The U.S. was one of the original signatories to 

the 1987 Montreal Protocol and the U.S. ratified the Protocol on April 12, 1988. Congress then 

enacted, and President George H.W. Bush signed into law, the Clean Air Act Amendments of 
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1990 (CAAA), which included Title VI on Stratospheric Ozone Protection, codified as 42 U.S.C. 

Chapter 85, Subchapter VI, to ensure that the U.S. could satisfy its obligations under the 

Montreal Protocol. Title VI includes restrictions on production, consumption, and use of ODS 

that are subject to acceleration if “the Montreal Protocol is modified to include a schedule to 

control or reduce production, consumption, or use . . . more rapidly than the applicable schedule” 

prescribed by the statute (CAA §606). Both the Montreal Protocol and the Clean Air Act (CAA) 

define consumption as production plus imports minus exports. 

 In 1990, as part of the London Amendment to the Montreal Protocol, the Parties 

identified HCFCs as “transitional substances” to serve as temporary, lower ozone depletion 

potential (ODP) substitutes for CFCs and other ODS. EPA similarly viewed HCFCs as 

“important interim substitutes that will allow for the earliest possible phaseout of CFCs and other 

Class I substances1

” (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 U.S. 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 (MT), effective January 1, 1996. This became the U.S. 

consumption baseline for HCFCs. 

 The 1992 Copenhagen Amendment created a schedule with graduated reductions and the 

eventual phaseout of HCFC consumption (Copenhagen, 23-25 November, 1992, Decision IV/4). 

Prior to a later adjustment in 2007, the schedule initially called for a 35 percent reduction of the 

consumption cap in 2004, followed by a 65 percent reduction in 2010, a 90 percent reduction in 

 

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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2015, a 99.5 percent reduction in 2020 (restricting the remaining 0.5 percent of baseline to the 

servicing of existing refrigeration and air-conditioning equipment), with a total phaseout in 2030. 

The Copenhagen Amendment did not cap HCFC production. In 1999, the Parties created 

a cap on production for 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 ODPweighted MT, effective January 1, 2004. This became the U.S. production baseline for HCFCs. 

To further protect human health and the environment, the Parties to the Montreal Protocol 

adjusted the Montreal Protocol’s phaseout schedule for HCFCs at the 19th Meeting of the Parties 

in September 2007. In accordance with Article 2(9)(d) of the Montreal Protocol, the adjustment 

to the phaseout schedule was effective on May 14, 2008.2

 As a result of the 2007 Montreal Adjustment (reflected in Decision XIX/6), the U.S. and 

other industrialized countries are obligated to reduce HCFC production and consumption 75 

percent below the established baseline by 2010, rather than 65 percent as previously required. 

The other milestones remain the same. The adjustment also resulted in a phaseout schedule for 

HCFC production that parallels the consumption phaseout schedule. All production and 

consumption for Article 2 Parties is phased out by 2030. 

 Decision XIX/6 also adjusted the provisions for Parties operating under paragraph 1 of 

Article 5 (developing countries): (1) to set HCFC production and consumption baselines based 

on the average 2009-2010 production and consumption, respectively; (2) to freeze HCFC 

production and consumption at those baselines in 2013; and (3) to add stepwise reductions of 10 

 

2

 Under Article 2(9)(d) of the Montreal Protocol, an adjustment enters into force six months from the date the 

depositary (the Ozone Secretariat) circulates it to the Parties. The depositary accepts all notifications and documents 

related to the Protocol and examines whether all formal requirements are met. In accordance with the procedure in 

Article 2(9)(d), the depositary communicated the adjustment to all Parties on November 14, 2007. The adjustment 

entered into force and become binding for all Parties on May 14, 2008. 
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percent below baselines by 2015, 35 percent by 2020, 67.5 percent by 2025, and 97.5 percent by 

2030 – allowing, between 2030 and 2040, an annual average of no more than 2.5 percent to be 

produced or imported solely for servicing existing air-conditioning and refrigeration equipment. 

All production and consumption for Article 5 Parties will be phased out by 2040. 

 In addition, Decision XIX/6 adjusted Article 2F to allow 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 2020.3 Paragraph 14 of Decision XIX/6 notes that no later than 2015, 

the Parties would consider “further reduction of production for basic domestic needs” in 2020 

and beyond. Under paragraph 13 of Decision XIX/6, the Parties will review in 2015 and 2025, 

respectively, the need for the “servicing tails” for 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. 

B. How Does the Clean Air Act Phase Out HCFCs? 

The U.S. has chosen to implement the Montreal Protocol phaseout schedule on a 

chemical-by-chemical basis. In 1992, environmental and industry groups petitioned EPA to 

 

3

 Paragraphs 4-6 of adjusted Article 2F read as follows: 

 “4. Each Party shall ensure that for the twelve-month period commencing on 1 January 2010, and in each twelve-month period thereafter, its 

calculated level of consumption of the controlled substances in Group I of Annex C does not exceed, annually, twenty-five per cent of the 

sum referred to in paragraph 1 of this Article. Each Party producing one or more of these substances shall, for the same periods, ensure that 

its calculated level of production of the controlled substances in Group I of Annex C does not exceed, annually, twenty-five per cent of the 

calculated level referred to in paragraph 2 of this Article. However, in order to satisfy the basic domestic needs of the Parties operating under 

paragraph 1 of Article 5, its calculated level of production may exceed that limit by up to ten per cent of its calculated level of production of 

the controlled substances in Group I of Annex C as referred to in paragraph 2. 

5. Each Party shall ensure that for the twelve-month period commencing on 1 January 2015, and in each twelve-month period thereafter, its 

calculated level of consumption of the controlled substances in Group I of Annex C does not exceed, annually, ten per cent of the sum 

referred to in paragraph 1 of this Article. Each Party producing one or more of these substances shall, for the same periods, ensure that its 

calculated level of production of the controlled substances in Group I of Annex C does not exceed, annually, ten per cent of the calculated 

level referred to in paragraph 2 of this Article. However, in order to satisfy the basic domestic needs of the Parties operating under paragraph 

1 of Article 5, its calculated level of production may exceed that limit by up to ten per cent of its calculated level of production of the 

controlled substances in Group I of Annex C as referred to in paragraph 2. 

6. Each Party shall ensure that for the twelve-month period commencing on 1 January 2020, and in each twelve-month period thereafter, its 

calculated level of consumption of the controlled substances in Group I of Annex C does not exceed zero. Each Party producing one or more 

of these substances shall, for the same periods, ensure that its calculated level of production of the controlled substances in Group I of Annex 

C does not exceed zero. However: 

 i. each Party may exceed that limit on consumption by up to zero point five per cent of the sum referred to in paragraph 1 of this Article 

in any such twelve-month period ending before 1 January 2030, provided that such consumption shall be restricted to the servicing of 

refrigeration and air conditioning equipment existing on 1 January 2020; 

ii. each Party may exceed that limit on production by up to zero point five per cent of the average referred to in paragraph 2 of this 

Article in any such twelve-month period ending before 1 January 2030, provided that such production shall be restricted to the servicing of 

refrigeration and air conditioning equipment existing on 1 January 2020.”
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implement the required phaseout by eliminating the most ozone-depleting HCFCs first. Based on 

the available data at that time, EPA believed the U.S. could meet, and possibly exceed, the 

required Montreal Protocol reductions through a chemical-by-chemical phaseout that employed a 

“worst-first” approach focusing on certain chemicals earlier than others. In 1993, as authorized 

by section 606 of the CAA, the U.S. established a phaseout schedule that eliminated HCFC-141b 

first and would greatly restrict HCFC-142b and HCFC-22 next, followed by restrictions on all 

other HCFCs and ultimately a complete phaseout (58 FR 15014, March 18, 1993; 58 FR 65018, 

December 10, 1993). 

 On January 21, 2003 (68 FR 2820), EPA promulgated regulations (2003 Final Rule) to 

ensure compliance with the first reduction milestone in the HCFC phaseout: the requirement that 

by January 1, 2004, the U.S. reduce HCFC consumption by 35 percent and freeze HCFC 

production. In the 2003 Final Rule, EPA established chemical-specific consumption and 

production baselines for HCFC-141b, HCFC-22, and HCFC-142b for the initial regulatory 

period ending December 31, 2009. Section 601(2) states that EPA may select “a representative 

calendar year” to serve as the company baseline for HCFCs. In the 2003 Final Rule, EPA 

concluded that because the entities eligible for allowances had differing production and import 

histories, no single year was representative for all companies. Therefore, EPA assigned an 

individual consumption baseline year to each company by selecting its highest ODP-weighted 

consumption year from among the years 1994 through 1997. EPA assigned individual production 

baseline years in the same manner. EPA also provided an exception allowing new entrants 

provided that they began importing after the end of 1997 but before April 5, 1999, the date the 

advanced notice of proposed rulemaking was published. EPA believed that such small businesses 

might not have been aware of the impending rulemaking that would affect their ability to 

continue in the HCFC market. 
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 The 2003 Final Rule apportioned production and consumption baselines to each company 

in amounts equal to the amounts in the company’s highest “production year” or “consumption 

year,” as described above. It completely phased out the production and import of HCFC-141b by 

granting 0 percent of that substance’s baseline for production and consumption in the table at 40 

CFR 82.16. EPA did, however, create a petition process to allow applicants to request very small 

amounts of HCFC-141b beyond the phaseout. The 2003 Final Rule also granted 100 percent of 

the baselines for production and consumption of HCFC-22 and HCFC-142b for each of the years 

2003 through 2009. EPA was able to allocate allowances for HCFC-22 and HCFC-142b at 100 

percent of baseline because, in light of the concurrent complete phaseout of HCFC-141b, the 

allocations for HCFC-22 and HCFC-142b, combined with projections for consumption of all 

other HCFCs, remained below the 2004 cap of 65 percent of the U.S. baseline. 

 EPA allocates allowances for specific years; they are valid between January 1 and 

December 31 of a given control period (i.e., calendar year). Prior to December 15, 2009, EPA 

had not allocated any HCFC allowances for year 2010 or beyond. The regulations at section 

82.15(a) and (b) only addressed the production and import of HCFC-22 and HCFC-142b for the 

years 2003-2009. Through the 2009 Final Rule (74 FR 66412), EPA addressed the production 

and import of HCFC-22 and HCFC-142b for the 2010-2014 control periods. Absent the granting 

of calendar-year allowances, section 82.15 would have prohibited the production and import of 

HCFC-22 and HCFC-142b after December 31, 2009. The 2009 Final Rule allowed for continued 

production and consumption, at specified amounts, of HCFC-142b, HCFC-22, and other HCFCs 

not previously included in the allowance system, for the 2010-2014 control periods. 

 In the U.S., an allowance is the unit of measure that controls production and consumption 

of ODS. EPA establishes company-by-company baselines (also known as “baseline allowances”) 

and allocates calendar-year allowances equal to a percentage of the baseline for specified control 

periods. A calendar-year allowance represents the privilege granted to a company to produce or 
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import one kilogram (not ODP-weighted) of the specific substance. EPA allocates two types of 

calendar-year allowances – production allowances and consumption allowances. “Production 

allowance” and “consumption allowance” are defined at section 82.3. To produce an HCFC for 

which allowances have been allocated, an allowance holder must expend both production and 

consumption allowances. To import an HCFC for which allowances have been allocated, an 

allowance holder must expend consumption allowances. An allowance holder exporting HCFCs 

for which it has expended consumption allowances may obtain a refund of those consumption 

allowances upon submittal of proper documentation to EPA. 

 Since EPA is implementing the phaseout on a chemical-by-chemical basis, it allocates 

and tracks production and consumption allowances on an absolute kilogram basis for each 

chemical. Upon EPA approval, an allowance holder may transfer calendar-year allowances of 

one type of HCFC for calendar-year allowances of another type of HCFC, with transactions 

weighted according to the ODP of the chemicals involved. Pursuant to section 607 of the CAA, 

EPA applies an offset to each HCFC transfer by deducting 0.1 percent from the transferor’s 

allowance balance. The offset benefits the ozone layer since it “results in greater total reductions 

in the production in each year of . . . class II substances than would occur in that year in the 

absence of such transactions” (42 U.S.C. 7671f). 

The U.S. remained comfortably below the aggregate HCFC cap through 2009. The 2003 

Final Rule announced that EPA would allocate allowances for 2010-2014 in a subsequent action 

and that those allowances would be lower in aggregate than for 2003-2009, consistent with the 

next stepwise reduction for HCFCs under the Montreal Protocol. EPA stated its intention to 

determine the number of allowances that would be needed for HCFC-22 and HCFC-142b, 

bearing in mind that other HCFCs would also contribute to total HCFC consumption. EPA noted 

that it would likely achieve the 2010 reduction step by applying a percentage reduction to the 

HCFC-22 and HCFC-142b baselines. EPA subsequently monitored the market to estimate 
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servicing needs and market adjustments in the use of HCFCs, including HCFCs for which EPA 

did not establish baselines in the 2003 Final Rule. 

In the 2009 Final Rule, EPA determined both the estimated demand for HCFC-22 during 

the 2010-2014 regulatory period and the percentage of that estimated demand for which it was 

appropriate to allocate allowances. As described in Section V.B. of this action, EPA determined 

that the percentage of the estimated demand allocated in the form of allowances should not 

remain constant from year to year but rather should decline on an annual basis. For 2010, EPA 

allocated allowances equal to 80 percent of the estimated demand for HCFC-22, concluding that 

reused, recycled, and reclaimed material could meet the remaining 20 percent. Under the 2009 

Final Rule, the percentage of estimated demand for which there was no allocation, and therefore 

would need to be met through recycling and reclamation, rose from 20 percent in 2010 to 29 

percent in 2014 to ensure the U.S. market would have a viable reclamation industry and could 

meet the 2015 stepwise reduction under the Montreal Protocol. The determinations EPA made in 

the 2009 Final Rule regarding (1) the total estimated demand for HCFC-22 in 2010-2014 and (2) 

the percentage of that estimated demand that EPA would address through an allowance 

allocation were not at issue in the litigation and are unaffected by the Court’s decision. EPA is 

not revisiting either determination with respect to 2011 in this interim final action, but rather is 

relying on the existing record for the 2009 Final Rule. However, EPA welcomes comment on 

whether it should revisit these determinations in the future. EPA is also interested in comments 

on whether it could and should allocate a different percentage of baseline for calendar-year 

production than for calendar-year consumption, while still meeting U.S. obligations under the 

Montreal Protocol and complying with the CAA. 

C. What Sections of the Clean Air Act Apply to This Rulemaking? 

 Several sections of the CAA apply to this rulemaking. Section 605 of the CAA phases out 

production and consumption and restricts the use of HCFCs in accordance with the schedule set 
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forth in that section. As discussed in the 2009 Final Rule (74 FR 66416), section 606 provides 

EPA authority to set a more stringent phaseout schedule for acceleration ofthan the schedule in 

section 605 based on an EPA determination regarding current scientific information or the 

availability of substitutes, or to conform to any acceleration under the Montreal Protocol. EPA 

previously accelerated set a more stringent schedule than the section 605 schedule through a rule 

published December 10, 1993 (58 FR 65018). Through the 2009 Final Rule, EPA made a further 

accelerated adjustment to the section 605 schedule based on the acceleration under the Montreal 

Protocol as agreed to at the Meeting of the Parties in September 2007. Those accelerations more 

stringent schedule established in that rule areis unaffected by the recent Court decision and are is 

therefore still in effect. 

Section 606 provides authority for EPA to promulgate regulations that establish a 

schedule for production and consumption that is more stringent than what is set forth in section 

605 if: “(1) based on an assessment of credible current scientific information (including any 

assessment under the Montreal Protocol) regarding harmful effects on the stratospheric ozone 

layer associated with a class I or class II substance, the Administrator determines that such more 

stringent schedule may be necessary to protect human health and the environment against such 

effects, (2) based on the availability of substitutes for listed substances, the Administrator 

determines that such more stringent schedule is practicable, taking into account technological 

achievability, safety, and other relevant factors, or (3) the Montreal Protocol is modified to 

include a schedule to control or reduce production, consumption, or use of any substance more 

rapidly than the applicable schedule under this title.” It is only necessary to meet one of the three 

criteria. In the 2009 Final Rule, EPA determined that all three criteria had been met with respect 

to the schedule for phasing out production and consumption of HCFC-22 and HCFC-142b. 

As noted in the 2009 Final Rule, while section 606 is sufficient authority for accelerating 

establishing a more stringent schedule than the section 605 phaseout schedule, section 614(b) of 
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the CAA provides that in the case of a conflict between the CAA and the Montreal Protocol, the 

more stringent provision shall govern. Thus, section 614(b) requires the Agency to establish 

phaseout schedules at least as stringent as the schedules contained in the Montreal Protocol. To 

meet the 2010 stepdown requirement, EPA is continuing to allocate HCFC allowances at a level 

that will ensure the aggregate HCFC production and consumption will not exceed 25 percent of 

the U.S. baselines. For more discussion of this point, see 74 FR 66416. 

Finally, section 607 addresses transfers of allowances both between companies and 

chemicals. EPA is further clarifying its policy on inter-pollutant transfers in this action. 

D. How Does This Action Relate to the Recent Court Decision?

 Certain allowance holders affected by the 2009 Final Rule filed petitions for review in the 

U.S. Court of Appeals for the District of Columbia Circuit. Among other arguments, the 

petitioners, Arkema Inc., Solvay Fluorides, LLC, and Solvay Solexis, Inc., contended that the 

rule was impermissibly retroactive because in setting the baselines for the new regulatory period, 

EPA did not take into account certain inter-pollutant baseline transfers that petitioners had 

performed during the prior regulatory period. The transfers at issue occurred in 2008. Solvay 

Solexis, Inc. submitted two Class II Controlled Substance Transfer Forms for consumption 

allowance transfers to Solvay Fluorides, LLC on February 15, 2008, and March 4, 2008. 

Arkema, Inc. submitted two Class II Controlled Substance Transfer Forms for consumption and 

production allowance transfers on April 18, 2008. Each company requested EPA’s approval to 

convert HCFC-142b allowances to HCFC-22 allowances, and checked a box on the EPA transfer 

form indicating that “baseline” allowances would be transferred. EPA sent non-objection notices 

to both Solvay Solexis and Solvay Fluorides on February 21, 2008 and March 20, 2008 and to 

Arkema, Inc. in April 2008. The transfer requests and EPA’s approvals were attached to 

petitioners’ court filings and are available in the docket for this action. 
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 In the Notice of Proposed Rulemaking titled “Protection of Stratospheric Ozone: 

Adjustments to the Allowance System for Controlling HCFC Production, Import, and Export,” 

published in the Federal Register at 73 FR 78680 on December 23, 2008 (2008 Proposed Rule), 

EPA requested comments on establishing baselines for the 2010-2014 regulatory period “with or 

without” taking into account baseline inter-pollutant transfers made during the 2003-2009 

regulatory period (73 FR 78687). The proposed regulatory text accounted for the inter-pollutant 

transfers discussed above. The increase in HCFC-22 baseline allowances for Arkema, Inc. and 

Solvay Fluorides, LLC presented in the 2008 Proposed Rule resulted in a larger amount of 

HCFC-22 baseline allowances overall and therefore a lower percentage of HCFC-22 baselines 

allocated across the board in each control period. Specifically, the proposed shift resulted in a 16 

percent decrease in market share for all other allowance holders, and increases for the 

petitioners: Arkema and Solvay. For more detail on the impact of these transfers, see Section 

V.C. of this preamble. 

In the 2009 Final Rule, after considering comments, EPA determined that allowing interpollutant transfers to carry forward from one regulatory period to the next could undermine the 

Agency’s chemical-by-chemical phaseout approach and could encourage market manipulation. 

For a more detailed discussion, see Section V.A.1. EPA also concluded that section 607 of the 

CAA was best read as limiting inter-pollutant transfers to those conducted on an annual basis. 

For these reasons, EPA did not take the 2008 inter-pollutant transfers into account in establishing 

the baselines for the 2009 Final Rule covering 2010-2014. 

The Court issued a decision on August 27, 2010, agreeing with petitioners that “the 

[2009] Final Rule unacceptably alters transactions the EPA approved under the 2003 Rule” 

(Arkema v. EPA, 618 F.3d at 3). The Court vacated the rule in part, “insofar as it operates 

retroactively,” and remanded to EPA “for prompt resolution,” (618 F.3d at 10). The Court 

withheld the mandate for the decision pending the disposition of any petition for rehearing. On 
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November 12, 2010, EPA filed a petition for rehearing, which was denied on January 21, 2011. 

The mandate issued on February 4, 2011. 

Because the Court vacated the rule only in part, without specifying which part or parts 

were vacated, EPA may adopt a reasonable interpretation of the vacatur’s extent. In doing so, 

EPA is relying on its expertise in administering the HCFC phaseout regulations under Title VI of 

the CAA. First, EPA notes that the rule contains elements that were not at issue in the litigation. 

EPA concludes that the vacatur has no effect on allowances for any substances other than HCFC142b and HCFC-22, since the petitioners’ claims and the opinion itself discuss only those two 

substances. Similarly, EPA concludes that other discrete portions of the rule, such as the 

provisions on use and introduction into interstate commerce, are unaffected by the vacatur. 

The baselines for HCFC-142b and HCFC-22 were clearly at issue in the litigation and 

indeed are the focus of the Court’s opinion. The Court found that “the Agency’s refusal to 

account for the Petitioners’ baseline transfers of inter-pollutant allowances in the Final Rule is 

impermissibly retroactive,” (618 F.3d at 9). Because baseline and calendar year allowances are 

inextricably linked4

, EPA has determined that the Court’s vacatur voids the HCFC-22 and 

HCFC-142b baselines in 40 CFR 82.17 and 82.19 as well as the percentage of baseline allocated 

for those specific substances in 40 CFR 82.16 for all companies listed in those sections.5

 This 

means that until EPA establishes new baselines and allocates new calendar-year allowances, 

production and import of these two substances is prohibited under 40 CFR 82.15. Recognizing 

 

4

 The reason baseline and calendar-year allocations are inextricable is because calendar-year allocations are 

expressed as a percentage of baseline, and the percentage of baseline allocated for a specific substance varies 

depending on the sum of all company baselines for that substance. The process works as follows for each specific 

HCFC: First, all the company-specific baselines listed in the tables at 40 CFR 82.17 and 82.19 are added to 

determine the aggregate amount of baseline production and consumption, respectively. Second, EPA determines 

how many consumption allowances the market needs for a given year, taking into account recycled, reused, and 

reclaimed material, and divides that amount by the aggregate amount of baseline allowances. The resulting 

percentage listed in the table at section 82.16 becomes what each company is allowed to consume in a given control 

period. For example, a company with 100,000 kg of HCFC-22 baseline allowances would multiply that number by 

the percentage allowed for 2011 (for example, 32 percent) to determine its calendar-year allowance is 32,000 kg. 

Historically and in this interim final rule, EPA has allocated the same percentage of baseline allowances for 

production as it does for consumption. 

5

 The companies’ allocations are inter-related because, as noted in footnote 4, the percentage of baseline allocated 

varies according to the sum of the company-specific baselines. 
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this scenario, on January 28, 2011, EPA sent letters to affected stakeholders informing them that 

the Agency would exercise enforcement discretion for a limited period provided their production 

and import did not exceed specified levels and provided that they adhered to additional 

conditions. 

In determining the meaning of the Court’s vacatur, EPA considered whether this 

interpretation was consistent with what the Court intended and a good fit for the specific 

circumstances, which include the goals and design of the HCFC allowance program and the 

basic structure of the 2009 Final Rule. While this interpretation is appropriate in this instance, it 

is possible that another interpretation would be more appropriate in a case involving a program 

with different goals, design, or structure. 

In the 2009 Final Rule, EPA relied on its assessment of the amount of virgin and 

recovered HCFC-22 and HCFC-142b needed to service existing equipment and transition to the 

2015 stepdown under the Montreal Protocol. The Court did not take issue with this assessment. 

At this time, EPA has not received information indicating that demand will be higher than the 

Agency’s assessment predicted. On the contrary, EPA has heard from several anecdotal sources 

that the amount of actual market demand for HCFC-22 may in fact be lower than the amount 

identified in the Servicing Tail Report. However, since EPA does not have sufficient data to 

support this conclusion at this time, and recognizes the urgent need to act quickly to establish 

allowances for the 2011 control period, the Agency is relying on the record for the 2009 Final 

Rule, which includes the Agency’s prior assessment of demand for HCFC-22 and HCFC-142b in 

2011. Therefore, through this action, EPA is establishing new baselines for 2011 reflecting the 

court’s decision and allocating the percentage of baseline needed to ensure that the total 

allocation for 2011 remains the same as in the 2009 Final Rule. If sufficient information becomes 

available in future, EPA may adjust the aggregate allocation level for future control periods. 

1. Addressing 2010 Allowances 
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 EPA interprets the Court’s decision as applying, at a minimum, to the HCFC-22 and 

HCFC-142b baseline and calendar-year allowances for 2011-2014. EPA is not addressing 2010 

allowances in this action. The Agency plans to take comment in a future notice-and-comment 

rulemaking on whether the vacatur and remand should be interpreted as applying to the 2010 

allocations, and if so, how allowances in future control periods might be adjusted to reflect this. 

The 2011 control period is already well underway, and as discussed in the good cause finding in 

Section III, it is important that EPA establish a definitive 2011 allocation now to dispel 

confusion and allow normal business activities to proceed. In particular, EPA believes the urgent 

need for certainty regarding the consumption allowance allocations in the 2011 control period 

precludes the Agency from considering any adjustments during 2011. However, EPA intends to 

address this issue in detail in a separate notice-and-comment rulemaking with respect to future 

control periods. 

III. Justification for this Interim Final Rule 

 EPA is taking this action as an interim final rule without prior proposal and public 

comment because EPA finds that the good cause exemption from the notice-and-comment 

rulemaking requirement of the Administrative Procedure Act (APA), 5 U.S.C. 551 et seq., 

applies here. Section 307(d) of the CAA states that in the case of any rule to which section 

307(d) applies, notice of proposed rulemaking must be published in the Federal Register (CAA 

§307(d)(3)). The promulgation or revision of regulations under Title VI of the CAA is generally 

subject to section 307(d). However, section 307(d) does not apply to any rule referred to in 

subparagraphs (A) or (B) of section 553(b) of the APA. Section 553(b)(B) of the APA, 5 U.S.C. 

553(b)(B), provides that, when an agency for good cause finds that notice-and-comment public 

procedures are impracticable, unnecessary, or contrary to the public interest, the agency may 

issue a rule without providing notice and an opportunity for public comment. 
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EPA has determined that there is good cause for making today's rule final without prior 

proposal and opportunity for comment because such notice and opportunity for comment is 

unnecessary, impracticable, and contrary to the public interest. In reaching this determination, 

EPA considered several factors: (1) taking interim final action for 2011 avoids regulatory 

confusion, disruption of normal business activities, and effects on consumers pending 

development of a notice-and-comment rulemaking (see, e.g., Brae Corp. v. United States, 740 

F.2d 1023 (D.C. Cir. 1984)); (2) the Agency is relying on the existing record from the 2009 Final 

Rule for this action (see, e.g., Chamber of Commerce v. SEC, 443 F.3d 890 (D.C. Cir. 2006)); 

and (3) the rule’s duration is limited (see, e.g., Small Refiner Lead Phase-Down Task Force v. 

EPA, 705 F.2d 506 (D.C. Cir. 1983)). 

First, it is in the public interest to dispel confusion, allow normal business activities to 

proceed, and avoid adverse effects on consumers. EPA has received numerous questions from 

industry about what, if any, allowances companies currently hold in light of the Court’s decision. 

The primary purpose of this interim final rule is to dispel confusion and provide regulatory 

certainty for the near term. EPA interprets the vacatur as voiding company baselines and 

calendar-year allowances for HCFC-22 and HCFC-142b, and because entities are prohibited 

from producing or importing HCFCs without allowances, quick action is necessary to ensure the 

continued production and import of those two HCFCs. This interim final action will provide 

industry with certainty for 2011, and allow normal business operations to continue. It also gives 

EPA time to develop notice-and-comment rules that will cover subsequent control periods. 

This action will also avoid unintended consequences for consumers and businesses who 

own appliances containing HCFC-22 and/or HCFC-142b (e.g., refrigerators and air 

conditioners), as well as the businesses that service these appliances. Absent this rulemaking, 

there could be a shortage of these HCFCs. Consumers and businesses unable to service their 

existing HCFC-22 equipment with HCFCs would instead have to retrofit their existing 
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appliances before the end of their useful life to use a refrigerant other than that which was 

intended for the appliance, or purchase new equipment to replace existing appliances. Not only 

would this be expensive and unexpected, especially for those who bought a new unit shortly 

before January 1, 2010, but the shortage could lead to improper retrofits that decrease a unit’s 

effectiveness and energy efficiency, cost the consumer more to operate, and result in further 

refrigerant emissions to the atmosphere. Considering the current state of the economy, shortages 

of HCFC-22 could lead appliance owners, who likely do not have the same level of experience 

as a licensed professional, to recharge their units on their own. Improper retrofits and recharging 

could raise the potential for mixing refrigerants, which could damage systems and increase the 

likelihood of mixed refrigerants being vented into the atmosphere, since mixtures may not work 

properly and likely could not be reclaimed. 

At worst, ll of these scenarios could lead to an unanticipated abrupt changeover of large 

significant quantities of equipment, which would be at odds with EPA’s goal of minimizing 

impacts to business and consumers by supporting a gradual turnover of the installed base of 

equipment as individual equipment reaches the end of its useful life, allowing existing equipment 

to continue to operate properly. In the preamble to the 2009 Final Rule, EPA stated: “Congress 

intended to permit the continued use of previously-manufactured appliances” (74 FR 66438). 

EPA discussed this issue in detail at that time, in the context of the section 605(a) ban on the 

“use” of HCFCs (74 FR 66437-66438). In this action, the Agency is not revisiting its analysis or 

conclusions with respect to this issue. Accordingly, EPA is allocating production and 

consumption allowances for HCFC-22 and HCFC-142b in a way that avoids shortening the 

useful lifetime of appliances that were manufactured prior to the effective date of the use ban 

(January 1, 2010). 

Furthermore, a supply shortage could raise the price of affected gases, thereby increasing 

incentives for entities to illegally smuggle HCFC-22 into the country to meet the demand of 
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consumers and businesses. There are numerous cases cited on the EPA website 

(www.epa.gov/ozone/enforce/index.html) documenting the smuggling of CFCs and HCFCs. Not 

only would this hurt entities that are abiding by the law, it could even hurt consumers and 

businesses that unknowingly receive inferior material. For all these reasons, it is important that 

EPA take action quickly. Since it is impracticable to complete a notice-and-comment rulemaking 

prior to the 2011 summer season, when working air conditioners are most important, and delay 

would be contrary to the public interest, interim final action is necessary. 

The second reason for invoking the good cause exemption is that EPA is relying on the 

existing record for the 2009 Final Rule, which is still applicable and sufficiently current for the 

purposes of this action. In this interim final rule, EPA is not revisiting the determination made in 

the 2009 Final Rule regarding the total amount of HCFC production and import that the Agency 

will allow for 2011. EPA is simply addressing what share of that total amount should be 

allocated to particular companies. The 2008 Proposed Rule (73 FR 78680) provided all interested 

parties an opportunity to comment on the total HCFC production and import amount for 2011. 

Thus, it is unnecessary to provide a second opportunity to comment on that amount prior to 

issuing this interim final rule. 

Third, this interim final rule only addresses 2011—the current control period—and is 

thus limited in duration. The specific duration is defined by the structure of the stratospheric 

ozone protection program, which operates in control periods that correspond to calendar years. 

Allowances are allocated for a specific control period. EPA intends to initiate a notice-andcomment rulemaking or rulemakings as soon as possible to address subsequent control periods. 

For the reasons explained above, and given the Court’s statement that it was remanding 

to EPA “for prompt resolution,” notice and public procedure are impracticable, unnecessary, and 

contrary to the public interest. EPA finds that this constitutes good cause under 5 U.S.C. 

553(b)(B). Nonetheless, EPA is providing 30 days for submission of public comments following 
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this action. EPA will consider all written comments submitted in the allotted time period to 

determine whether to issue additional production allowances for 2011. In addition, EPA will 

review comments on other aspects of this rulemaking as they relate to 2012 and beyond, and will 

provide an opportunity for public comment on specific proposals for future control periods. 

Section 553(d) of the Administrative Procedure Act (APA), 5 U.S.C. Chapter 5, generally 

provides that rules may not take effect earlier than 30 days after they are published in the Federal 

Register. APA section 553(d) excepts from this provision any action that grants or recognizes an 

exemption or relieves a restriction. Since today's action relieves a restriction from the regulatory 

ban on the production and consumption of HCFC-22 and HCFC-142b in the U.S., EPA is 

making this action effective immediately upon publication to ensure the availability of these 

HCFCs for servicing air conditioning and refrigeration equipment in 2011. 

IV. Summary of this Final Action 

In response to the Court’s decision, EPA is (1) establishing 2011 company-by-company 

consumption and production baselines for HCFC-22 and HCFC-142b in the tables at 40 CFR 

82.17 and 82.19 in a manner that reflects the 2008 inter-pollutant baseline transfers and (2) 

allocating company-by-company production and consumption allowances for these substances 

for 2011 by establishing percentages of baseline in the table at section 82.16. EPA is also 

updating the tables at sections 82.17 and 82.19 to reflect 2010 inter-company, single-pollutant 

baseline transfers and revising the list of allowance holders to update company names. These 

actions are consistent with actions taken in the 2009 Final Rule. To reflect the court’s vacatur, 

EPA is removing the allocation percentages from the table at section 82.16 for the years 2011-

2014. In this rulemaking, EPA is adding an allocation percentage for 2011. In a separate noticeand-comment rulemaking or rulemakings, EPA will address the allocations for the control 

periods 2012-2014. All aspects of the 2009 Final Rule promulgated on December 15, 2009 (74 

FR 66412) that are not addressed in this interim final rule are unchanged. 
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As a Party to the Montreal Protocol, and having ratified the Montreal Protocol and all of 

its amendments, the U.S. was required to decrease its amount of HCFC consumption and 

production to 25 percent of the U.S. baseline in 2010. The cap is the same for the years 2010-

2014 before it drops down to 10 percent of baseline in 2015. Under the cap, the aggregate 

allowances for all U.S. HCFC consumption in 2011 cannot exceed 3,810 ODP-weighted MT (25 

percent of the aggregate U.S. consumption baseline) annually, and the aggregate allowances for 

all U.S. HCFC production in 2011 cannot exceed 3,884.25 ODP-weighted MT (25 percent of the 

aggregate U.S. production baseline) annually. 

 To stay below the cap set by the Montreal Protocol for the 2011 control period addressed 

in this rulemaking, EPA is using the historical production and consumption baselines as adjusted 

in the 2009 Final Rule, with further adjustments to reflect the 2008 inter-pollutant baseline 

transfers and inter-company, single-pollutant baseline transfers that occurred after issuance of the 

2009 Final Rule. EPA is considering other methods for distributing allowances in the future that 

do not make use of the baselines established in this interim final rule for 2011. The Agency 

welcomes comment on whether and when it would be appropriate to establish a new method for 

distributing allowances. EPA also welcomes comment on what allocation methods it should 

consider in a future proposed rulemaking.

 EPA determined in the 2009 Final Rule that for HCFC-22, it was necessary to allocate a 

percentage of baseline that would decrease on an annual basis to reflect a projected decrease in 

demand as well as to promote recycling and reclamation. EPA is not revisiting that determination 

in this rulemaking. EPA concluded in the 2009 Final Rule that this approach would help prevent 

shortages that might otherwise occur upon the stepdown in 2015. In this action, EPA is 

allocating 32.0 percent of baseline for HCFC-22 in 2011, which reflects an annual decline from 

the 2010 amount. EPA is allocating 4.9 percent of baseline for HCFC-142b in 2011. The HCFC142b number relates solely to the aggregate baselines for this substance and does not reflect an 
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annual decline. The reasons for establishing these allocation percentages for 2011 are discussed 

in Section V. 

 EPA’s allocations for both HCFC-22 and HCFC-142b meet U.S. obligations under the 

Montreal Protocol and reflect the use restrictions under section 605(a) of the CAA while 

providing for servicing needs consistent with those restrictions. The allocations for HCFC-22 

and HCFC-142b reflect EPA’s analysis of market data for these chemicals, as prepared in 

advance of the 2009 Final Rule. The allocation levels for these HCFCs meet the demand for 

virgin material and avoid shortages during 2011. 

 In this action, EPA is not changing the methodology used in the 2009 Final Rule to 

calculate the total number of calendar-year consumption and production allowances. While the 

number of total calendar-year consumption allowances is unchanged, the number of production 

allowances is slightly lower (less than two percent lower) than in the 2009 Final Rule due to the 

changes in aggregate baseline allowances. This is explained in more detail in Section V.C. The 

only other difference is in the distribution of those allowances. 

 At this time, EPA is allocating a total of 2,504 ODP-weighted MT of HCFC-22 and 

HCFC-142b calendar-year consumption allowances and 2,302 ODP-weighted MT of HCFC-22 

and HCFC-142b calendar-year production allowances for 2011. Both allocations remain below 

the limit established by the Montreal Protocol for the 2010-2014 phasedown step of 75 percent 

below baseline. The difference between the cap and the total allocation reflects EPA’s estimate 

(developed for the 2009 Final Rule) of the demand for HCFCs during these control periods. It 

also will accommodate minor adjustments in the market, particularly to allow potential market 

growth for other allowed HCFCs. As discussed in more detail in Section V.B.3. and in the 

preamble to the 2009 Final Rule, it will also encourage greater reclamation of recovered 

refrigerant and thus facilitate preparation for the 2015 step down in the consumption cap to 10 

percent of baseline. 
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 This action also clarifies EPA’s policy on inter-pollutant transfers for 2011 and all future 

control periods in Section V.A.1. and asks for comment on allocation approaches in future 

control periods. 

V. Allocation of Allowances for the 2011 Control Period 

A. Baselines for HCFC-22 and HCFC-142b Allowances 

In the 2009 Final Rule, EPA presented the allocation structure for HCFC-22 and HCFC142b for the control periods 2010-2014: allocating a percentage of the baseline production and 

consumption allowances. The rationale for this system is discussed further at 74 FR 66412. The 

Court found no fault with EPA’s framework for allocating HCFCs in the 2009 Final Rule, except 

the aspects of the rule they deemed to be retroactive, i.e., not taking into account inter-pollutant 

baseline transfers that occurred in the prior regulatory period in establishing company-specific 

baseline allowances. To address this, EPA is establishing HCFC-22 and HCFC-142b baseline 

allowances for 2011 that reflect past inter-pollutant baseline transfers deemed permanent by the 

Court. 

1. Adjusting the Baseline for Inter-company and Inter-pollutant Transfers

Sections 607(b) and (c) of the CAA address inter-pollutant and inter-company transfers 

of allowances, respectively. Inter-pollutant transfers are the transfer of an allowance of one 

substance to an allowance of another substance on an ODP-weighted basis. Inter-company 

transfers are transfers of allowances for the same ODS from one company to another company. 

Section 607(c) also authorizes inter-company transfers combined with inter-pollutant transfers, 

so long as the requirements of both are met. The corresponding regulatory provisions for HCFCs 

appear at 40 CFR 82.23. 

The 2009 Final Rule updated the baselines for HCFC-22 and HCFC-142b to reflect name 

changes and inter-company baseline transfers, i.e., transfers of baseline for a specific type of 

HCFC from one company to another. Doing so reflected the changes in the marketplace that had 
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occurred since EPA promulgated the 2003 Final Rule. Inter-company baseline transfers provide 

a mechanism for new entrants to join the HCFC market and for other companies to expand their 

business. EPA recognizes that in some cases, entities are no longer actively involved in HCFC 

production, import, and/or export activities. EPA retained the baseline for such entities, noting 

that this had been a mechanism by which new entrants had entered the HCFC allowance system 

in the past. 

 The 2009 Final Rule also addressed four inter-pollutant baseline transfers made during 

the prior regulatory period (see Section II.D. of this action for more detail). EPA had proposed to 

adjust the company baselines to reflect these four inter-pollutant baseline transfers in the 2008 

Proposed Rule. Eight commenters opposed, and two commenters supported, these proposed 

adjustments. At issue was whether the inter-pollutant baseline transfers should carry forward as 

part of the companies’ baseline allowances in the next regulatory period. 

 After reviewing the comments, EPA concluded that adjusting the baselines to reflect 

inter-pollutant baseline transfers could create incentives for future manipulation of the allocation 

system in anticipation of future control periods. EPA remains concerned about the potential for 

such future manipulation if inter-pollutant baseline transfers during the current regulatory period 

are carried forward as a change in a company’s baseline for future regulatory periods. For 

example, in 2020 EPA will no longer be issuing HCFC-22 production or consumption 

allowances (see section 82.16(e)). EPA expects that companies with HCFC-22 allowances would 

no longer be in the HCFC market at that date if they did not hold allowances for other HCFCs 

that may still be produced after 2020. If EPA were to allow inter-pollutant baseline transfers that 

carried forward into the new regulatory period, companies with HCFC-22 baselines in 2019 

could convert them all to baselines for HCFC-123. Perpetuating the HCFC-22 baselines in a new 

form would be counter to the design of the chemical-by-chemical phaseout, under which the 

baseline allowances for a particular chemical are intended to drop out of the system upon the 
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phase-out of that chemical. As another example, in 2015, a producer or importer that previously 

had not participated in the HCFC-123 market could dominate that market by converting its 

HCFC-22 baseline in 2014 to HCFC-123 baseline. Given the different ODPs of HCFC-22 and 

HCFC-123 (0.055 and 0.02, respectively), converting one baseline allowance of HCFC-22 would 

result in 2.75 baseline allowances of HCFC-123. Also, since companies hold many more HCFC22 baseline allowances than HCFC-123 baseline allowances, converting those HCFC-22 baseline 

allowances would have an overwhelming effect on the current HCFC-123 baseline allowance 

holders and the overall market. EPA agrees with commenters on the 2008 Proposed Rule that 

taking inter-pollutant baseline transfers into account in setting baselines could have the effect of 

moving the U.S. HCFC phasedown from a chemical-by-chemical phaseout, as established under 

the “worst-first” approach in the 1993 Final Rule, towards an ODP-weighted phasedown. Thus, 

there are important policy reasons going forward for not taking inter-pollutant transfers into 

account in establishing baselines for new regulatory periods. 

 Some commenters on the 2008 Proposed Rule stated that modifying the baselines by 

taking into account inter-pollutant transfers would be contrary to the CAA. One commenter 

argued that section 607 of the CAA allows EPA to approve inter-pollutant transfers of 

allowances only on a year-to-year basis. That commenter pointed to language in section 607(b) 

stating that EPA regulations are to permit “a production allowance for a substance for any year to 

be transferred for a production allowance for another substance for the same year on an ozone 

depletion weighted basis.” The commenter also discussed the legislative history of the 1990 

CAA Amendments. 

 EPA does not agree with the commenter that the language of section 607(b) is clear on its 

face. However, where the statutory language is ambiguous, EPA has discretion to choose a 

reasonable interpretation of that language. EPA determined in the 2009 Final Rule that section 

607(b) is best read as permitting only year-by-year inter-pollutant transfers. EPA continues to 
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believe that this is the best interpretation of the statutory language. Section 607(b) states that 

EPA’s rules are to permit “a production allowance for a substance for any year to be transferred 

for a production allowance for another substance for the same year.” This language emphasizes 

the year-by-year nature of such transactions. No parallel language appears in section 607(c). That 

section does, however, provide that any inter-pollutant transfers between two or more persons 

must meet the requirements of section 607(b). 

 As the Court noted, “the Agency is certainly entitled to . . . institute a program that 

forbids baseline inter-pollutant transfers in the future,” (Arkema v. EPA, 618 F.3d at 9). Hence, 

EPA concludes that requiring all inter-pollutant transfers to be conducted on a yearly – and thus 

temporary – basis going forward is the approach most consistent with the wording of section 

607(b). Further discussion of the reasons for limiting inter-pollutant transfers to those conducted 

on a calendar-year basis is available in the Response to Comments on the 2008 Proposed Rule 

(included in the docket for this rulemaking). 

 Consistent with the Court’s decision regarding past inter-pollutant transfers (those 

conducted during the prior regulatory period), the baselines established in this action for 2011 

take into account the 2008 inter-pollutant baseline transfers discussed earlier in this notice. EPA 

is clarifying, however, that it has not approved any inter-pollutant transfers of baseline 

allowances in the current regulatory period, and for the reasons given in the 2009 Final Rule and 

in this action, in future EPA intends to approve inter-pollutant transfers only on a year-by-year 

basis. Thus, in the context of the protection of stratospheric ozone allowance system, companies 

should not expect that any inter-pollutant transfers they conduct will affect their baselines either 

in the current regulatory period or any future regulatory period. 

 As it did in the 2009 Final Rule, EPA is adjusting baseline allowances to reflect intercompany, single-pollutant baseline transfers that occurred since the last final rule was signed. 
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 In summary, this interim final rule reflects the changes in consumption and production 

baseline allowances from (1) the 2008 inter-pollutant transfers deemed permanent by the Court 

and (2) inter-company, single-pollutant baseline transfers that have occurred since the 2009 Final 

Rule was signed, and (3) clarifies the types of inter-pollutant transfers that will be permitted in 

the future. The consumption and production baseline amounts for HCFC-22 and HCFC-142b for 

2011 are shown below in Table 3. 

B. Factors for Considering Allocation Amounts for HCFC-22 and HCFC-142b 

In the 2009 Final Rule, EPA decided to allocate HCFC-22 and HCFC-142b allowances 

based on the projected servicing needs for those compounds, taking into account the amount of 

those needs that can be met through recycling and reclamation. EPA is not changing that 

approach in this interim final rule. However, the specific amounts allocated per company are 

different due to the changed baselines and the need to apply a different allocation percentage to 

company baselines in order to keep the aggregate amount allocated the same. Because it is 

necessary to promote use of reused, recycled, and reclaimed material in anticipation of the 2015 

phasedown step, EPA does not intend to allocate the difference between the consumption 

allocation authorized by the Parties to the Montreal Protocol and the consumption allocation 

authorized by this rule except under unforeseen extenuating circumstances. 

1. The Importance of HCFC-22 Relative to HCFC-142b Servicing Needs for Existing 

Equipment 

HCFC-22 is the most widely-used HCFC. The demand for its use in servicing existing 

equipment was the primary factor affecting EPA’s allocation of production and consumption 

allowances of HCFCs for the current regulatory period. Prior to issuing the 2009 Final Rule, 

EPA issued and sought comment on three versions of a draft report analyzing servicing demand 

for the HCFC appliances in the U.S. refrigeration and air-conditioning sector projected to be in 

service from 2010-2019 (all versions available at Docket EPA-HQ-OAR-2008-0496: published 
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November 4, 2005 at 70 FR 67172; released at a stakeholder meeting on September 29, 2006; 

published December 23, 2008, with 2008 Proposed Rule). The Servicing Tail Report focuses on 

air-conditioning and refrigeration appliances because such equipment represents the bulk of the 

servicing need. In addition, the servicing exception to the use ban for HCFC-22 and HCFC-142b 

pertains only to use as a refrigerant in such equipment. Under section 605(a) of the CAA and 

EPA’s implementing regulations, nearly all other uses of these two HCFCs were banned 

effective January 1, 2010. The projected servicing need for HCFC-22 in 2011 is approximately 

57,900 MT (3,185 ODP-weighted MT), or approximately 84 percent of the consumption cap for 

all HCFCs in 2011 under the Montreal Protocol, which is 3,810 ODP-weighted MT. HCFC-142b 

has primarily been used as a foam blowing agent, a use that was phased out in 2010. The 

projected servicing demand for existing refrigeration equipment containing HCFC-142b is 

extremely low: approximately 100 MT (7 ODP-weighted MT). EPA therefore focused the 

analysis on HCFC-22 because that compound is the predominant HCFC in the installed base of 

air-conditioning and refrigerant equipment for which servicing in the U.S. will likely continue. 

As discussed in the 2009 Final Rule, the majority of HCFC-22 equipment that is 

projected to be in use from this point onward will be air-conditioning applications, including 

window units, packaged terminal units, unitary air-conditioning, chillers, dehumidifiers, water 

and ground source heat pumps, and motor vehicle air-conditioning in buses and trains. The report 

projected that approximately 145.6 million units of all such types of HCFC-22 air-conditioning 

equipment were in use in 2010, decreasing by about 41 percent in 2015 and 86 percent in 2020. 

In addition, approximately 3.8 million units of HCFC-22 refrigeration equipment were in use in 

2010. The installed base of HCFC-22 refrigeration equipment is projected to decrease from 2010 

levels by about 44 percent in 2015 and 75 percent in 2020. For more on the Servicing Tail Report

and the Vintaging Model, which was used to develop the report, see 74 FR 66424 and the 

Servicing Tail Report included in the docket. 
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 EPA estimates that the servicing need for HCFC-22 will continue to decrease each year, 

and consistent with the 2009 Final Rule, this interim final rule accounts for this by allocating a 

smaller amount for 2011 than was allocated for 2010. This approach is described in Section 

V.B.3. In this interim final action, EPA is maintaining the overall HCFC-22 allocation levels for 

2011 that the Agency determined were appropriate in the 2009 Final Rule. EPA’s decision not to 

allocate above the need projected in the Servicing Tail Report is discussed in the preamble to the 

2009 Final Rule. 

2. Meeting Servicing Needs with Virgin and Recovered Material 

In the 2009 Final Rule, the Agency recognized that servicing demand can be met with a 

combination of newly-manufactured or imported HCFCs (virgin HCFCs) and HCFCs that have 

been recovered and either reused, recycled or reclaimed. Therefore, EPA did not anticipate that 

virgin HCFC-22 would need to be produced or imported to meet the entire HCFC-22 servicing 

demand (estimated to be 3,185 ODP-weighted MT in 2011). The Servicing Tail Report analyzes 

various scenarios regarding reclamation. EPA continues to believe that reused, recycled, and 

reclaimed material can help meet HCFC-22 servicing needs and is therefore not changing course 

at this time. Should new data be presented, EPA reserves the option of increasing the amount of 

demand for servicing existing equipment that should be met by reused, recycled, and reclaimed 

material in future control periods. 

3. Annual Reduction in Allocated Amounts

As explained in the preamble to the 2009 Final Rule, without year-to-year reductions in 

the allocations for virgin HCFC-22, the HCFC-22 market could be oversaturated, and the 

contribution of reused, recycled, and reclaimed refrigerant would decrease, both in the total 

number of kilograms and as the proportion of overall need. 

EPA is particularly concerned with encouraging a smooth transition to the 2015 

stepdown. At that date, the U.S. must meet a 90 percent reduction below the baseline for all 
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HCFCs, which is equivalent to 1,524 ODP-weighted MT. EPA’s Servicing Tail Report shows 

that even a 20 percent recovery rate would be insufficient to meet the demand for HCFC-22 in 

2015. As shown in Table 4-5 in the report, demand for HCFC-22 in 2015 is projected to be 

38,800 MT while the cap for all HCFCs equates to 27,709 MT of HCFC-22 (assuming no 

allocation for any other HCFCs). A 20 percent recovery rate would allow for the additional use 

of 8,800 MT but would still leave a shortfall of 2,291 MT in 2015. In developing the 2009 Final 

Rule, EPA calculated that to meet the total demand in 2015, the recovery rate would have to 

increase to 26 percent (representing 29 percent of total servicing demand). 

In the 2009 Final Rule, EPA determined that it was desirable to institute a year-by-year 

reduction for the period 2010-2014. The Agency is maintaining that policy in this interim final 

action for 2011. A smooth transition for stakeholders – including continued availability of 

needed material for approved uses – has historically been an essential aspect of U.S. success in 

implementing the Montreal Protocol and CAA requirements. To ease the transition to 2015 and 

avoid disruptions to the market and shortages in HCFC-22 at that date, it is necessary to take 

steps now to foster the development of a robust recovery and recycling industry in the U.S. 

 EPA determined in the 2009 Final Rule the level of allocation that would meet the 

servicing demand over 2010-2014. In this interim final action, EPA is maintaining the overall 

HCFC-22 allocation levels for 2011 that the Agency determined were appropriate in the 2009 

Final Rule. Since EPA is not banning the use of existing HCFC-22 appliances manufactured 

prior to January 1, 2010, reused, recycled, and reclaimed HCFC-22 will become more valuable 

as the phaseout progresses. The demand for HCFC-22 to service existing equipment will provide 

an economic incentive to increase the quantities of recovered HCFC-22 available for reuse, 

recycling, and reclamation. The docket for the 2009 Final Rule (EPA-HQ-OAR-2008-0496) 

provides further information on EPA’s assumptions regarding the availability of reused, recycled 

and reclaimed HCFC-22 to meet servicing demand. 
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Because the primary benefit of annually reducing the allocation is to ensure demand in 

2015 is met through greater recovery and reclamation, EPA continues to believe that it is 

appropriate to base the allocation on that goal. In developing the 2009 Final Rule, EPA estimated 

demand in 2015 for HCFC-22 would be 38,800 MT. Were the allocations to consist entirely of 

HCFC-22, the cap would limit the 2015 HCFC-22 allocation to only 27,709 MT, a difference of 

11,091 MT that would have to be made up with recovered material. Furthermore, it is likely that 

the allocation in 2015 will not consist entirely of HCFC-22, as EPA will need to reserve room 

under the cap for other HCFCs. In the 2009 Final Rule, EPA determined it was appropriate to 

establish an annual step-down such that the amount of total demand to be met from recovered 

HCFC-22 would equal 12,500 MT each year. This is approximately the amount EPA projected 

would be needed to meet the servicing demand in 2015. EPA is retaining this approach for 2011 

in the interim final rule. Under this approach, the allocations equal approximately 45,400 MT in 

2011. These values, shown in the table below, are derived by subtracting 12,500 MT from the 

estimated demand each year. EPA will not issue HCFC-22 and HCFC-142b allowances for 2012 

or later until a future rulemaking. Consistent with the 2009 Final Rule, EPA plans to reduce the 

allocation amount annually in future rulemakings to reflect the declining servicing demand. 

2010 2011 

Estimated Demand (MT) 62,500 57,900 

Total Allocation (MT) 50,000 45,400 

Recovered Amount (MT) 12,500 12,500 

As the total demand decreases, maintaining the supply of recovered HCFCs at a constant 

level results in recovered material comprising a greater proportion of the total demand each year. 

Under this approach, the percentage of the total demand to be met with recovered material will 

rise from 20 percent of total demand in 2010 to 21.6 percent in 2011, though the total amount of 

recovered material needed remains at 12,500 MT for both years. EPA still believes this is 

appropriate as it facilitates meeting the demand in 2015, of which at least 29 percent must be met 
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with recovered material, but takes comment on whether demand for HCFC-22 has changed since 

the 2009 Final Rule was published. Additionally, EPA is taking comment on whether there is 

surplus HCFC-22 on the U.S. market. In particular, EPA is interested in learning more about (1) 

the current amount of recovered HCFC-22 that is available for reclamation or reuse in another 

HCFC-22 system; (2) the amount of surplus HCFC-22 (virgin and reclaimed) in inventory; and 

(3) the amount of recovered HCFC-22 abroad awaiting import into the U.S. for reclamation 

and/or reuse. If new information shows a different amount of HCFC-22 should be allocated in 

future control periods to encourage reclamation and ensure a smooth transition in 2015, EPA will 

explore options to address this in a later proposed rule. 

C. Allocations of HCFC-22 and HCFC-142b 

 EPA is revising the tables in 40 CFR 82 that together specify the production and 

consumption allowances available to allowance holders during specified control periods. The 

tables at sections 82.17 and 82.19 apportion baseline production allowances and baseline 

consumption allowances, respectively, to individual companies for individual HCFCs during a 

particular regulatory period. Complementing these tables, the table at section 82.16 lists the 

percentage of baseline allocated to allowance holders for specific control periods. In the interim 

final rule, EPA is retaining this framework of complementary tables, revising them to reflect the 

Court’s vacatur, responding to the Court’s remand by making adjustments to the previous 

baselines consistent with the Court’s ruling, and granting percentages of baselines in a manner 

that achieves the 2010 phaseout step and lays the groundwork for the next phaseout step in 2015. 

 In the 2009 Final Rule, the percent allocation for HCFC-22 for 2011 was 38.0 percent of 

baseline. In the interim final rule, the value is 32.0 percent. The percent allocation for HCFC142b for 2011 was 0.47 percent of baseline in the 2009 Final Rule and is 4.9 percent of baseline 

in this interim final rule. These changes do not reflect a change in the total consumption 

allocation amounts for each substance, as the total allocation for HCFC-22 in 2011 remains 
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approximately 45,400 MT (the same as the 2009 Final Rule), and the total allocation for HCFC142b in 2011 remains at approximately 100 MT. Using the same percentage of baseline to 

allocate production allowances as consumption allowances, the total HCFC-22 production 

allocation is smaller than in the 2009 final rule by less than two percent. The lower amount is 

due to the change in company baselines to reflect the Court’s decision on the 2008 inter-pollutant 

baseline transfers, and not a change in the methodology used to determine allowances. More 

information is available on this subject in Section V.C.2. 

 The 2009 Final Rule, which did not treat the 2008 transfers of HCFC-142b to HCFC-22 

baseline allowances as carrying forward into the next regulatory period, had a total HCFC-22 

consumption baseline of 119,384 MT. In this interim final rule, EPA is reflecting the baseline 

transfers in section 82.19 in accordance with the Court’s decision. As a result, the aggregate 

HCFC-22 consumption baseline has increased to 141,865 MT. Since the aggregate HCFC-22 

baseline is now higher due to the increase in the number of HCFC-22 baseline allowances for 

Arkema, Inc. and Solvay Fluorides, LLC, EPA is allocating a smaller percentage of the 

company-specific baselines than in the 2009 Final Rule to achieve the same total number of 

allowances. Thus, 45,400 MT of HCFC-22 consumption (the aggregate allocation amount in 

2011) is equal to 38.0 percent of 119,384 MT (baseline) of HCFC-22 in the 2009 Final Rule, and 

32.0 percent of 141,865 MT (baseline) in this interim final rule. The aggregate HCFC-22 

production baseline is also increasing from 110,619 MT in the 2009 Final Rule to 129,093 MT in 

this interim final rule to reflect Arkema, Inc.’s transfer of HCFC-142b baseline production 

allowances to HCFC-22 baseline production allowances. 

 The opposite is true for HCFC-142b, which had a larger aggregate consumption baseline 

in the proposed rule (21,089 MT), but now has a smaller baseline (2,047 MT) since EPA is 

accounting for inter-pollutant transfers from HCFC-142b to HCFC-22. Thus, 100 MT of HCFC142b consumption allowances (the aggregate allocation amount in 2011) are equal to 0.47 
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percent of 21,089 MT of HCFC-142b in the 2009 Final Rule, and 4.9 percent of 2,047 MT in this 

interim final rule. Aggregate HCFC-142b baseline production allowances are decreasing from 

25,090 MT in the 2009 Final Rule to 9,444 MT in this interim final rule to reflect Arkema, Inc.’s 

transfer of HCFC-142b baseline production allowances. 

 EPA is removing the vacated text relating to HCFC-22 and HCFC-142b from the tables 

in sections 82.16, 82.17, and 82.19; adding new production and consumption baselines for those 

substances for 2011 to the tables at sections 82.17 and 82.19; and adding new specified 

percentages of baseline for those substances to the table in section 82.16 for the 2011 control 

period. 

Table 1- Phaseout Schedule for Class II Controlled Substances in 40 CFR 82.16 

Control 

Period 

Percent of 

HCFC141b 

Percent of 

HCFC-22 

Percent of 

HCFC142b 

Percent of 

HCFC-123

Percent of 

HCFC-124

Percent of 

HCFC225ca 

Percent of 

HCFC225cb 

2003 0 100 100 -- -- -- -- 

2004 0 100 100 -- -- -- -- 

2005 0 100 100 -- -- -- -- 

2006 0 100 100 -- -- -- -- 

2007 0 100 100 -- -- -- -- 

2008 0 100 100 -- -- -- -- 

2009 0 100 100 -- -- -- -- 

2010 0 41.9 0.47 125 125 125 125 

2011 0 32.0 4.9 125 125 125 125 

2012 0 -- -- 125 125 125 125 

2013 0 -- -- 125 125 125 125 

2014 0 -- -- 125 125 125 125 

 Consistent with the 2009 Final Rule, EPA is allocating different baseline percentages for 

HCFC-22 and HCFC-142b because EPA projects that the needs will differ for servicing airconditioning and refrigeration appliances during the 2011 control period. As discussed in Section 

V.B.1., the analysis prepared for the 2009 Final Rule showed there will be a significantly greater 

need for HCFC-22 than for HCFC-142b during 2011. Based on the Servicing Tail Report and 
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reporting information already required by EPA regulations, the needs for individual HCFCs are 

not uniform. EPA determined in the 2009 Final Rule 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. While annual inter-pollutant transfers in accordance with 

section 82.23(b) could be used to transfer allowances of one HCFC for another on a temporary 

basis, EPA continues to believe it is not appropriate to rely on such transfers as a mechanism for 

large-scale corrections. Instead, EPA anticipates that the continued availability of annual, 

temporary inter-pollutant transfers will permit the market to self-correct for unforeseen changes 

in demand and allow entities to consider a range of options for their allowances. EPA seeks to 

avoid unnecessary disruptions in the marketplace and to promote a smooth transition for society. 

1. HCFC-22 Consumption Allowances for 2011 

For 2011, EPA is allocating HCFC-22 consumption allowances to meet about 78 percent 

of the servicing need, assuming the remainder will be met by recovered HCFC-22 that is either 

reused, recycled, or reclaimed. This translates into approximately 45,400 MT (2,497 ODPweighted MT), or 66 percent of the total HCFC consumption cap for the 2011 control period. 

2. HCFC-22 Production Allowances for 2011 

For purposes of the 2011 interim final rule, EPA is not revisiting its determination in the 

2009 Final Rule to use the same percentages for production and consumption allocations – 

deriving the percentages based on estimated need for each individual HCFC. Therefore, this rule 

allocates 41,310 MT (2,272 ODP-weighted MT of the 3,884.25 ODP-weighted metric ton 

production cap) to HCFC-22 production in 2011. The 2011 aggregate allocation is 1.7 percent 

lower than the amount allocated in the 2009 Final Rule (41,310 MT in this Interim Final Rule vs. 

42,035 MT in the 2009 Final Rule) because the aggregate amount of baseline production 

allowances in this rulemaking did not increase by the same relative amount as aggregate baseline 

consumption allowances. Because Solvay did not transfer its HCFC-142b production allowances 
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to HCFC-22 production allowances, consumption allowances are 18.8 percent higher in this rule, 

while production allowances are only 16.7 percent higher. The memo to the docket for this 

rulemaking (EPA-HQ-OAR-2010-1040) titled “HCFC-22 and HCFC- 142b Allocation 

Adjustments: 2009 Final Rule vs. 2011 Interim Final Rule,” discusses the slight differences in 

allocation amounts in more detail. 

While some allowance holders have encouraged EPA to increase the number of 

production allowances allocated in 2011, EPA is not allocating additional production allowances 

in this interim final rule for several reasons. First, EPA is relying on the existing record for the 

2009 Final Rule, in which the Agency determined it was appropriate to allocate production and 

consumption allowances at the same percentage of baseline. EPA believes it is important to 

obtain public comment on this issue before changing course. Second, in the 2009 Final Rule, 

EPA stated that allocating the same percentage of baseline for production and consumption was 

“consistent with section 605(c) of the Clean Air Act, which requires that the phaseout schedule 

for HCFC consumption be the same as that for HCFC production” (74 FR 66429). EPA has 

given further thought to this provision and is seeking public comment on its interpretation before 

any changes in policy. Third, EPA has not previously taken comment on whether there would be 

environmental implications associated with such a change. Given these three considerations, 

EPA believes it would not be appropriate to increase the production amount without providing 

notice and an opportunity to comment. 

While this interim final rule contains the same allocation percentages for production and 

consumption, EPA welcomes comment on whether it should use different percentages to allocate 

HCFC-22 production and consumption allowances in 2011 and/or future control periods. From a 

policy perspective, EPA is interested in comments on whether an increase in the total number of 

HCFC-22 production allowances would result in greater total HCFC production, either in the 

U.S. or globally. EPA notes that production of 1 kilogram of an HCFC requires both a 
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production allowance and a consumption allowance (82.15(a)(1),(2)). Thus, an increase in 

production allowances without a corresponding increase in consumption allowances does not 

automatically result in greater production. The most likely scenario is that an increase in 

production allowances would result in greater U.S. production for export. This is because as 

stated in 82.20(a), “A person may obtain at any time during the control period...consumption 

allowances equivalent to the quantity of class II controlled substances that the person exported 

from the U.S. and its territories to a foreign state...when that quantity of class II controlled 

substance was produced in the U.S. ...with expended consumption allowances.” In effect, 

current EPA regulations allow exporters to receive a refund of one consumption allowance for 

each kilogram they export if they show one consumption and one production allowance were 

expended for the material exported. Therefore, EPA would not expect an increase in production 

allowances to result in greater amounts of HCFCs being used in the U.S. EPA welcomes 

comment on whether an increase in the level of production allowances would result in more U.S. 

production, either for domestic use or for export, and whether any additional U.S. production for 

export would result in greater worldwide production of HCFCs. 

From a legal perspective, EPA is interested in comments on whether section 605(c) 

would preclude allocating a different percentage of baseline for production than for 

consumption. Section 605(c) states that EPA must “promulgate regulations phasing out the 

production . . . of class II substances in accordance with [section 605],” subject to any 

acceleration under section 606. It further states that EPA must “promulgate regulations to insure 

that the consumption of class II substances in the United States is phased out and terminated in 

accordance with the same schedule . . . as is applicable to the phase-out and termination of 

production of class II substances under [Title VI].” EPA is considering three possible 

interpretations of the term “schedule” as referenced in section 605(c): (1) the schedule that 

appears on the face of section 605, which contains no deadlines until 2015; (2) the schedule that 
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appears on the face of section 605, as accelerated under section 606; and (3) the specific 

allocation percentages or amounts established by EPA through rulemaking for each control 

period. EPA believes that the second interpretation is the most consistent with the statutory 

language and purpose. 

In past actions, the Agency has accelerated the initial schedule in section 605 to reflect 

modifications to the Montreal Protocol phaseout schedule for HCFCs. Under the 2007 Montreal 

Adjustment (reflected in Decision XIX/6), the U.S. is obligated to reduce HCFC production and 

consumption 75 percent below its aggregate baseline by 2010. EPA is not proposing to increase 

production to an amount that would be inconsistent with that obligation. Instead, EPA is taking 

comment on whether to allow production to increase relative to consumption, without 

encroaching on the cap. Specifically, EPA is taking comment on whether to issue additional 

production allowances in the amount of 7,746 MT when compared to this interim final rule. 

If EPA were to decide to increase production allowances in 2011, its preferred approach 

would be to decouple the percentage of baseline allocated for production from the percentage of 

baseline allocated for consumption. EPA would effectuate this change in its regulations by 

replacing the table at 40 CFR 82.16 with two tables. One would allocate 32 percent of baseline 

for consumption allowances in 2011. The other would allocate 38 percent of baseline for 

production allowances in 2011. This approach would still provide the petitioners in Arkema v. 

EPA the benefit of their 2008 baseline transfers while giving other companies with production 

baselines approximately the same number of production allowances as they received in the 2009 

Final Rule. Compared to the 2009 Final Rule, the net result would be 7,020 MT (386 ODPweighted MT) additional HCFC-22 production allowed in 2011 for a total of 49,055 MT (2,698 

ODP-weighted MT). Under this scenario, the U.S. would be 1,021 ODP-weighted MT below the 

production cap and in compliance with its obligations under the Montreal Protocol. EPA is 

seeking comment on whether this increase would hinder the transition to the 2015 phaseout step, 
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under which the U.S. is obligated to reduce HCFC production and consumption 90 percent below 

its aggregate baseline. EPA’s preference is to continue to use the same percentages for 

production and consumption allocations. This is because EPA is concerned this action could 

increase U.S. production of HCFCs, might decrease the U.S.’s ability to transition to the 2015 

stepdown under the Montreal Protocol, and potentially increase global production of HCFCs. 

Nevertheless, the Agency welcomes comment on this option for increasing 2011 and/or future 

HCFC-22 production allowances. After reviewing comments, EPA may either issue a 

supplemental allocation of production allowances for 2011 or leave the 2011 production 

allocation in this interim final rule unchanged. 

3. HCFC-142b Allowances for 2011

 Establishing HCFC-142b baseline allowances that take into account the 2008 interpollutant transfers discussed in Section II.D. results in 2,047 MT of aggregate baseline 

consumption allowances and 9,444 MT of aggregate baseline production allowances. Consistent 

with the 2009 Final Rule, EPA is allocating 100 percent of the projected servicing need for 

HCFC-142b identified in that rule: 100 MT (7 ODP-weighted MT) of consumption. To get to 

that level of consumption, EPA is allocating 4.9 percent of the aggregate consumption baseline, 

as reflected in the table at section 82.16. The aggregate allocation number for consumption is the 

same as in the 2009 Final Rule. 

 Using the same percentage (4.9 percent), EPA is allocating 463 MT (30.1 ODP-weighted 

MT) of HCFC-142b production allowances for 2011. The 2011 aggregate allocation for 

production is higher than the amount allocated in the 2009 Final Rule (463 MT in this interim 

final rule vs. 118 MT in the 2009 Final Rule). The allocated amount is 292 percent higher than in 

the 2009 Final Rule because the aggregate amount of baseline HCFC-142b consumption 

allowances in this rulemaking decreased by a significantly larger amount than aggregate baseline 

HCFC-142b production allowances. Baseline Cconsumption allowances are 90.3 percent lower 
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in this rule, while baseline production allowances are only 62.4 percent lower. This occurred 

because Solvay did not transfer its HCFC-142b production allowances to HCFC-22 production 

allowances. This higher amount of calendar-year production does not affect the U.S.’s ability to 

meet its obligations under the Montreal Protocol. The memo to the docket for this rulemaking 

(EPA-HQ-OAR-2010-1040) titled “HCFC-22 and HCFC- 142b Allocation Adjustments: 2009 

Final Rule vs. 2011 Interim Final Rule,” discusses the differences in exact allocation amounts in 

more detail. 

34. How the Aggregate for HCFC-22 and HCFC-142b Translates Entity-by-Entity

 EPA is allocating (1) approximately 45,400 MT of HCFC-22 consumption allowances, 

(2) 41,310 MT of HCFC-22 production allowances, (3) approximately 100 MT of HCFC-142b 

consumption allowances, and (4) 463 MT of HCFC-142b production allowances for 2011. 

However, EPA actually allocates allowances to individual companies (i.e., legal entities).

 Company-specific production and consumption baselines (also referred to as “baseline 

allowances”) for HCFC-142b and HCFC-22 are listed at sections 82.17 and 82.19, respectively. 

The percentage of baseline each entity will receive in 2011 appears at section 82.16(a), as shown 

in Table 1 above. 

 Allowances allocated for individual control periods are called “calendar-year allowances” 

to distinguish them from the baseline production or consumption. For 2011, EPA is apportioning 

production and consumption baselines for HCFC-22 and HCFC-142b on the same basis as in the 

2009 Final Rule, except that EPA is making adjustments to reflect (1) the 2008 inter-pollutant 

transfers of baseline allowances deemed permanent by the Court, (2) inter-company, singlepollutant transfers of baseline allowances that occurred in 2010, and (3) changes in company 

names that occurred after the 2009 Final Rule was signed. Applying the approach described 

above, EPA is apportioning production and consumption baselines for HCFC-22 and HCFC142b to the following entities in the following amounts: 
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Table 2: Baseline Production Allowances of HCFC-22 and HCFC-142b in 40 CFR 82.17 

Person Controlled Substance Allowances (kg) 

Arkema 

HCFC-22 46,692,336

HCFC-142b 484,369

DuPont HCFC-22 42,638,049

Honeywell 

HCFC-22 37,378,252

HCFC-142b 2,417,534

MDA Manufacturing HCFC-22 2,383,835

Solvay Solexis HCFC-142b 6,541,764

Table 3: Baseline Consumption Allowances of HCFC-22 and HCFC-142b in 40 CFR 82.19 

Person Controlled Substance Allowances (kg) 

ABCO Refrigeration Supply HCFC-22 279,366

Altair Partners HCFC-22 302,011

Arkema HCFC-22 48,637,642

HCFC-142b 483,827

Carrier Corporation HCFC-22 54,088

Coolgas Investment Property HCFC-22 1,040,458

DuPont HCFC-22 38,814,862

HCFC-142b 52,797

H.G. Refrigeration Supply HCFC-22 40,068

Honeywell HCFC-22 35,392,492

HCFC-142b 1,315,819

Mexichem Fluor Inc. HCFC-22 2,546,305

Kivlan & Company HCFC-22 2,081,018

MDA Manufacturing HCFC-22 2,541,545

Mondy Global HCFC-22 281,824

National Refrigerants HCFC-22 5,528,316

Refricenter of Miami HCFC-22 381,293

Refricentro HCFC-22 45,979

R-Lines HCFC-22 63,172

Saez Distributors HCFC-22 37,936

Solvay Fluorides HCFC-22 3,781,691

Solvay Solexis HCFC-142b 194,536

USA Refrigerants HCFC-22 14,865

D. HCFC-141b, HCFC-123, HCFC-124, HCFC-225ca, and HCFC-225cb Allowances 

Other than adjustments for inter-company, single-pollutant transfers of baseline 

allowances, baselines and percentages of baseline allocated as calendar-year allowances for 

HCFC-141b, HCFC-123, HCFC-124, HCFC-225ca, and HCFC-225cb are unchanged from the 
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2009 Final Rule. In the case of HCFC-141b, EPA is continuing to allocate 0 percent of baseline 

for U.S. consumption and production, consistent with 40 CFR 82.16(b). 

E. Other HCFCs 

 As a result of EPA’s allocation process, which is largely based on projected demand for 

HCFC-22 and HCFC-142b, minus an amount of HCFC-22 that is assumed to be reused, 

recycled, or reclaimed, the total allocation is lower than the aggregate HCFC cap under the 

Montreal Protocol. EPA recognizes that there could be some additional need for HCFCs not 

specifically included in this rule. While some niche applications in the U.S. use other HCFCs, 

such as HCFC-21, EPA is not aware of additional need for production or import of these 

substances at this time, as adequate amounts appear to be in inventory. However, EPA is not 

foreclosing the possibility of additional production or import for these niche uses. Also, some 

amount of HCFC-141b will likely continue to be produced or imported via the petition process 

during 2011. EPA believes there is sufficient room under the cap for such continued production 

and import. The current regulations at 40 CFR 82.15 ban the production and import of class II 

substances for which EPA has apportioned baseline production and consumption allowances in 

excess of allowances held by the producer or importer, but do not ban the production and import 

of class II substances for which EPA has not apportioned baseline production and consumption 

allowances. This rule does not alter the current regulations in that respect. The producer or 

importer of an HCFC that is not subject to the allowance system would be required to report to 

EPA consistent with the existing recordkeeping and reporting requirements. If necessary, EPA 

could amend the regulations to set and apportion baselines and issue allowances for these 

HCFCs. Therefore, retaining room under the cap provides the benefit of accounting for 

unanticipated growth in HCFCs that do not have allocations or other unforeseen events. 

However, EPA is not reserving room under the cap for the above-described reasons. EPA is 
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allocating allowances based on modeled demand for virgin and recovered material in preparation 

for the next major stepdown period under the Montreal Protocol in 2015. 

VI. Statutory and Executive Order Reviews 

A. Executive Order 12866: Regulatory Planning and Review and Executive Order 13563: 

Improving Regulation and Regulatory Review 

 Under Executive Order (EO) 12866 (58 FR 51735, October 4, 1993), this action is a 

"significant regulatory action” since it raises “novel legal or policy issues.” Accordingly, EPA 

submitted this action to the Office of Management and Budget (OMB) for review under 

Executive Orders 12866 and 13563 (76 FR 3821, January 21, 2011) and any changes made in 

response to OMB recommendations have been documented in the docket for this action. 

 EPA did not conduct a specific analysis of the benefits and costs associated with this 

action. Many previous analyses provide a wealth of information on the costs and benefits of the 

U.S. HCFC phaseout including: 

• The 1993 Addendum to the 1992 Phaseout Regulatory Impact Analysis: Accelerating the 

Phaseout of CFCs, Halons, Methyl Chloroform, Carbon Tetrachloride, and HCFCs. 

• The 1999 Report Costs and Benefits of the HCFC Allowance Allocation System. 

• The 2000 Memorandum Cost/Benefit Comparison of the HCFC Allowance Allocation 

System. 

• The 2005 Memorandum Recommended Scenarios for HCFC Phaseout Costs Estimation. 

• The 2006 ICR Reporting and Recordkeeping Requirements of the HCFC Allowance 

System. 

• The 2007 Memorandum Preliminary Estimates of the Incremental Cost of the HCFC 

Phaseout in Article 5 Countries. 
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• The 2007 Memorandum Revised Ozone and Climate Benefits Associated with the 2010 

HCFC Production and Consumption Stepwise Reductions and a Ban on HCFC Precharged Imports. 

A memorandum summarizing these analyses is available in the docket. 

B. Paperwork Reduction Act 

 This action does not impose any new information collection burden. EPA already 

requires recordkeeping and reporting for HCFCs, and this action does not amend those 

provisions. The Office of Management and Budget (OMB) has previously approved the 

information collection requirements contained in the existing regulations at 40 CFR part 82, 

subpart A under the provisions of the Paperwork Reduction Act, 44 U.S.C. 3501 et seq. and has 

assigned OMB control number 2060-0498. The OMB control numbers for EPA's regulations in 

40 CFR are listed in 40 CFR part 9. 

C. Regulatory Flexibility Act (RFA) 

The Regulatory Flexibility Act (RFA) generally requires an agency to prepare a 

regulatory flexibility analysis of any rule subject to notice-and-comment rulemaking 

requirements under the Administrative Procedure Act or any other statute, unless the agency 

certifies that the rule will not have a significant economic impact on a substantial number of 

small entities. Small entities include small businesses, small organizations, and small 

governmental jurisdictions. Because this rule is not subject to notice-and-comment rulemaking 

requirements, the RFA does not apply and the Agency is not required to conduct a regulatory 

flexibility analysis. 

Nevertheless, in the spirit of the RFA, we have considered the economic impacts of this 

interim final rule on small entities. For purposes of assessing the impacts of this rule on small 

entities, a small entity is defined as: (1) a small business as defined by the Small Business 
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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 action will affect the following categories: 

Category NAICS code SIC code Examples of regulated entities 

Industrial Gas Manufacturing 

325120 2869 

Fluorinated hydrocarbon gases 

manufacturers and reclaimers 

Other Chemical and Allied 

Products Merchant 

Wholesalers 422690 5169 

Chemical gases and compressed 

gases merchant wholesalers 

Air-Conditioning and Warm 

Air Heating Equipment and 

Commercial and Industrial 

Refrigeration Equipment 

Manufacturing 333415 3585 

Air-conditioning equipment and 

commercial and industrial 

refrigeration equipment 

manufacturers 

Air-Conditioning Equipment 

and Supplies Merchant 

Wholesalers 423730 5075 

Air-conditioning (condensing unit, 

compressors) merchant wholesalers

Electrical and Electronic 

Appliance, Television, and 

Radio Set Merchant 

Wholesalers 423620 5064 

Air-conditioning (room units) 

merchant wholesalers 

Plumbing, Heating, and AirConditioning Contractors 

238220 1711, 7623 

Central air-conditioning system and 

commercial refrigeration 

installation; HVAC contractors 

 After considering the economic impacts of this interim final rule on small entities, I 

certify this action will not have a significant economic impact on a substantial number of small 

entities as it relieves a regulatory ban on production and consumption that would otherwise apply 

in the wake of the Court’s vacatur. EPA is continuing to allocate production and consumption 

allowances using the same approach described in the 2009 Final Rule with adjustments to reflect 

(1) 2008 inter-pollutant transfers of baseline allowances deemed permanent by the Court, (2) 

inter-company, single-pollutant transfers of baseline allowances that occurred in 2010, and (3) 
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changes in company names that occurred after the 2009 Final Rule was signed. EPA is not 

modifying the recordkeeping or reporting provisions and thus is not increasing the burden to 

small businesses. 

D. Unfunded Mandates Reform Act 

 This action contains no Federal mandates under the provisions of Title II of the Unfunded 

Mandates Reform Act of 1995 (UMRA), 2 U.S.C. 1531-1538 for State, local, or tribal 

governments or the private sector. First, UMRA does not apply to rules that are necessary for the 

implementation of international treaty obligations. This rule implements the 2010 milestone for 

the phaseout of HCFCs under the Montreal Protocol. Second, this action relieves the regulatory 

ban on production and consumption that would otherwise apply. This action will not have any 

significant direct impacts or State, local and tribal governments or private sector entities. 

Therefore, 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 action apportions production and consumption allowances and establishes 

baselines for private entities, not small governments. 

E. Executive Order 13132: Federalism 

 Executive Order 13132, titled “Federalism” (64 FR 43255, August 10, 1999), requires 

EPA to develop an accountable process to ensure “meaningful and timely input by State and 

local officials in the development of regulatory policies that have federalism implications.” 

“Policies that have federalism implications” is defined in the Executive Order to include 

regulations that have “substantial direct effects on the States, on the relationship between the 

national government and the States, or on the distribution of power and responsibilities among 

the various levels of government.” 
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 This action does not have federalism implications. It does not have substantial direct 

effects on the States, on the relationship between the national government and the States, or on 

the distribution of power and responsibilities among the various levels of government, as 

specified in Executive Order 13132. This action is expected to primarily affect producers, 

importers, and exporters of HCFCs. Thus, the requirements of section 6 of the Executive Order 

do not apply. 

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

 This action does not have tribal implications, as specified in Executive Order 13175 (65 

FR 67249, November 9, 2000). This action does not significantly or uniquely affect the 

communities of Indian tribal governments. It does not impose any enforceable duties on 

communities of Indian tribal governments. Thus, Executive Order 13175 does not apply to this 

action. 

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

Risks 

 This action is not subject to EO 13045 (62 F.R. 19885, April 23, 1997) because it is not 

economically significant as 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 
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Science, 1997: 63-6; (4) Whiteman D., Green A. “Melanoma and Sunburn,” Cancer Causes 

Control, 1994: 5:564-72; (5) Heenan, PJ. “Does intermittent sun exposure cause basal cell 

carcinoma? A case control study in Western Australia,” Int J Cancer 1995; 60: 489-94; (6) 

Gallagher, RP, Hill, GB, Bajdik, CD, et. al. “Sunlight exposure, pigmentary factors, and risk of 

nonmelanocytic skin cancer I, Basal cell carcinoma,” Arch Dermatol 1995; 131: 157-63; (7) 

Armstrong, DK. “How sun exposure causes skin cancer: an epidemiological perspective,” 

Prevention of Skin Cancer. 2004. 89-116. 

 This action implements the U.S. commitment to reduce the total basket of HCFCs 

produced and imported to a level that is 75 percent below the respective baselines. While on an 

ODP-weighted basis, this is not as large a step as previous actions, such as the 1996 Class I 

phaseout, it is one of the most significant remaining actions the U.S. can take to complete the 

overall phaseout of ODS and further decrease impacts on children’s health from stratospheric 

ozone depletion. 

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

Use 

 This action is not a “significant energy action” as defined in Executive Order 13211 (66 

FR 28355 (May 22, 2001)), because it is not likely to have a significant adverse effect on the 

supply, distribution, or use of energy. The rule issues allowances for the production and 

consumption of HCFCs. 

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 
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developed or adopted by voluntary consensus standards bodies. The NTTAA directs EPA to 

provide Congress, through OMB, explanations when the Agency decides not to use available and 

applicable voluntary consensus standards. This action does not involve technical standards. 

Therefore, EPA did not consider the use of any voluntary consensus standards. 

J. Executive Order 12898: Federal Actions to Address Environmental Justice in Minority 

Populations and Low-Income Populations 

Executive Order (EO) 12898 (59 FR 7629 (Feb. 16, 1994)) establishes federal executive 

policy on environmental justice. Its main provision directs federal agencies, to the greatest extent 

practicable and permitted by law, to make environmental justice part of their mission by 

identifying and addressing, as appropriate, disproportionately high and adverse human health or 

environmental effects of their programs, policies, and activities on minority populations and lowincome populations in the U.S. 

 EPA has determined that this action will not have disproportionately high and adverse 

human health or environmental effects on minority or low-income populations because the 2010 

phaseout step increases the level of environmental protection for all affected populations without 

having any disproportionately high and adverse human health or environmental effects on any 

population, including any minority or low-income population. This action continues the 

implementation of the U.S. commitment to reduce the total basket of HCFCs produced and 

imported to a level that is 75 percent below the respective baselines. While on an ODP-weighted 

basis, this is not as large a step as previous actions, such as the 1996 Class I phaseout, it is one of 

the most significant remaining actions the U.S. can take to complete the overall phaseout of ODS 

and further lessen the adverse human health effects for the entire population. 

K. The Congressional Review Act 

The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the Small Business 

Regulatory Enforcement Fairness Act of 1996, generally provides that before a rule may take 
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effect, the agency promulgating the rule must submit a rule report, which includes a copy of the 

rule, to each House of the Congress and to the Comptroller General of the U.S.. EPA will submit 

a report containing this rule and other required information to the U.S. Senate, the U.S. House of 

Representatives, and the Comptroller General of the U.S. prior to publication of the rule in the 

Federal Register. A major rule cannot take effect until 60 days after it is published in the Federal 

Register. This action is not a “major rule” as defined by 5 U.S.C. 804(2). This rule will be 

effective [INSERT DATE OF PUBLICATION IN THE FEDERAL REGISTER]. 

List of Subjects in 40 CFR Part 82 

Environmental protection, Administrative practice and procedure, Air pollution control, 

Chemicals, Exports, Hydrochlorofluorocarbons, Imports 

 

DATED: ____________________________ 

___________________________________ 

Lisa P. Jackson, 

Administrator. 

40 CFR part 82 is amended to read as follows: 

PART 82-PROTECTION OF STRATOSPHERIC OZONE 

1. Revise §82.16(a) to read as follows: 

§82.16 Phaseout schedule of class II controlled substances. 

Protection of Stratospheric Ozone: Protection of Stratospheric Ozone: 

Adjustments to the Allowance System for Controlling HCFC Production, Import, 

and Export (Page 54 of 57) 
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(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: 

Control 

Period 

Percent of 

HCFC141b 

Percent of 

HCFC-22 

Percent of 

HCFC142b 

Percent of 

HCFC-123

Percent of 

HCFC-124

Percent of 

HCFC225ca 

Percent of 

HCFC225cb 

2003 0 100 100 -- -- -- -- 

2004 0 100 100 -- -- -- -- 

2005 0 100 100 -- -- -- -- 

2006 0 100 100 -- -- -- -- 

2007 0 100 100 -- -- -- -- 

2008 0 100 100 -- -- -- -- 

2009 0 100 100 -- -- -- -- 

2010 0 41.9 0.47 125 125 125 125 

2011 0 32.0 4.9 125 125 125 125 

2012 0 -- -- 125 125 125 125 

2013 0 -- -- 125 125 125 125 

2014 0 -- -- 125 125 125 125 

* * * * * 

2. Revise §82.17 to read as follows: 

§82.17 Apportionment of baseline production allowances for class II controlled substances. 

The following persons are apportioned baseline production allowances for HCFC-22, HCFC141b, HCFC-142b, HCFC-123, HCFC-124, HCFC-225ca, and HCFC-225cb, as set forth in the 

following table: 

Person Controlled Substance Allowances (kg) 

AGC Chemicals Americas 

HCFC-225ca 266,608

HCFC-225cb 373,952

Arkema 

HCFC-22 46,692,336

HCFC-141b 24,647,925

HCFC-142b 484,369

DuPont HCFC-22 42,638,049
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HCFC-124 2,269,210

Honeywell 

HCFC-22 37,378,252

HCFC-141b 28,705,200

HCFC-142b 2,417,534

HCFC-124 1,759,681

MDA Manufacturing HCFC-22 2,383,835

Solvay Solexis HCFC-142b 6,541,764

3. Section 82.19 is revised to read as follows: 

§82.19 Apportionment of baseline consumption allowances for class II controlled 

substances.

The following persons are apportioned baseline consumption allowances for HCFC-22, HCFC141b, HCFC-142b, HCFC-123, HCFC-124, HCFC-225ca, and HCFC-225cb, as set forth in the 

following table: 

Person Controlled Substance Allowances (kg) 

ABCO Refrigeration Supply HCFC-22 279,366

AGC Chemicals Americas HCFC-225ca 285,328

HCFC-225cb 286,832

Altair Partners HCFC-22 302,011

Arkema 

HCFC-22 48,637,642

HCFC-141b 25,405,570

HCFC-142b 483,827

HCFC-124 3,719

Carrier HCFC-22 54,088

Continental Industrial Group HCFC-141b 20,315

Coolgas, Inc. HCFC-141b 16,097,869

Coolgas Investment Property 

HCFC-22 1,040,458

HCFC-123 19,980

HCFC-124 3,742

Discount Refrigerants HCFC-141b 994

DuPont 

HCFC-22 38,814,862

HCFC-141b 9,049

HCFC-142b 52,797

HCFC-123 1,877,042

HCFC-124 743,312

H.G. Refrigeration Supply HCFC-22 40,068

Honeywell HCFC-22 35,392,492

HCFC-141b 20,749,489
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HCFC-142b 1,315,819

HCFC-124 1,284,265

ICC Chemical Corp. HCFC-141b 81,225

ICOR HCFC-124 81,220

Mexichem Fluor Inc. HCFC-22 2,546,305

Kivlan & Company HCFC-22 2,081,018

MDA Manufacturing HCFC-22 2,541,545

Mondy Global HCFC-22 281,824

National Refrigerants 

HCFC-22 5,528,316

HCFC-123 72,600

HCFC-124 50,380

Perfect Technology Center, LP HCFC-123 9,100

Refricenter of Miami HCFC-22 381,293

Refricentro HCFC-22 45,979

R-Lines HCFC-22 63,172

Saez Distributors HCFC-22 37,936

Solvay Fluorides HCFC-22 3,781,691

HCFC-141b 3,940,115

Solvay Solexis HCFC-142b 194,536

Tulstar Products 

HCFC-141b 89,913

HCFC-123 34,800

HCFC-124 229,582

USA Refrigerants HCFC-22 14,865