Phasedown of Hydrofluorocarbons: Review and Renewal of Eligibility for Application-Specific Allowances, 75898-75943 [2024-20602]
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75898
Federal Register / Vol. 89, No. 179 / Monday, September 16, 2024 / Proposed Rules
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 84
[EPA–HQ–OAR–2024–0196; FRL–10782–01–
OAR]
RIN 2060–AV98
Phasedown of Hydrofluorocarbons:
Review and Renewal of Eligibility for
Application-Specific Allowances
Environmental Protection
Agency (EPA).
ACTION: Notice of proposed rulemaking.
AGENCY:
The U.S. Environmental
Protection Agency is undertaking this
rulemaking to assess the eligibility of six
applications to receive priority access to
allowances allocated pursuant to the
American Innovation and
Manufacturing Act of 2020. This
rulemaking proposes the framework for
how EPA will assess whether to renew
the eligibility of applications to receive
application-specific allowances;
decisions to renew or not renew each of
the six applications that currently
receive application-specific allowances;
revisions to the Technology Transitions
regulations as relevant to the specific
applications under review; a procedural
process for submitting a petition to
designate a new application as eligible
for priority access to allowances; narrow
revisions to the methodology used to
allocate allowances to applicationspecific allowance holders for calendar
years 2026 and beyond; and limited
revisions to existing regulations. EPA is
also proposing to authorize an entity to
produce regulated substances for export.
Lastly, EPA is proposing certain
confidentiality determinations for newly
reported information if this rulemaking
is finalized as proposed.
DATES: Comments must be received on
or before October 31, 2024. Any party
requesting a public hearing must notify
the contact listed below under FOR
FURTHER INFORMATION CONTACT by 5 p.m.
Eastern Daylight Time on September 23,
2024. If a virtual public hearing is held,
it will take place on or before October
1, 2024 and further information will be
provided at https://www.epa.gov/
climate-hfcs-reduction.
ADDRESSES: The U.S. Environmental
Protection Agency (EPA) has established
a docket for this action under Docket ID
No. EPA–HQ–OAR–2024–0196. All
documents in the docket are listed on
the https://www.regulations.gov
website. Although listed in the index,
some information is not publicly
available, e.g., Confidential Business
Information (CBI) or other information
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SUMMARY:
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whose disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the internet and will be publicly
available only in hard-copy form.
Publicly available docket materials are
available electronically through https://
www.regulations.gov or in hard copy at
the EPA Docket Center, Room 3334,
WJC West Building, 1301 Constitution
Avenue NW, Washington, DC. The
Public Reading Room is open from 8:30
a.m. to 4:30 p.m., Monday through
Friday, excluding legal holidays. The
telephone number for the Public
Reading Room is (202) 566–1744, and
the telephone number for the EPA
Docket Center is (202) 566–1742.
FOR FURTHER INFORMATION CONTACT:
Michelle Graff, U.S. Environmental
Protection Agency, Stratospheric
Protection Division, telephone number:
202–564–5387; or email address:
graff.michelle@epa.gov. You may also
visit EPA’s website at https://
www.epa.gov/climate-hfcs-reduction for
further information.
SUPPLEMENTARY INFORMATION:
Throughout this document, whenever
‘‘we,’’ ‘‘us,’’ ‘‘the Agency,’’ or ‘‘our’’ is
used, we mean EPA. Acronyms and
abbreviations that are used in this
rulemaking that may be helpful include:
2-BTP—2-bromo-3,3,3-trifluoropropene
AAGR—Average Annual Growth Rate
AES—Automated Export System
AIM Act—American Innovation and
Manufacturing Act of 2020
AHRI—Air-Conditioning, Heating, and
Refrigeration Institute
APU—Auxiliary Power Unit
ASHRAE—American Society for Heating,
Refrigerating, and Air-Conditioning
Engineers
ASA—Application-Specific Allowance
CAA—Clean Air Act
CBI—Confidential Business Information
CBP—U.S. Customs and Border Protection
CF3I—Trifluoroiodomethane
CFR—Code of Federal Regulations
CGMP—Current Good Manufacturing
Practice
CHIPS Act—Creating Helpful Incentives to
Produce Semiconductors Act of 2022
ClF3—Chlorine Trifluoride
CO2—Carbon Dioxide
COVID—Coronavirus Disease
CVD—Chemical Vapor Deposition
DFARS—Defense Federal Acquisition
Regulation Supplement
DOD—U.S. Department of Defense
DOJ—U.S. Department of Justice
EEI—Electronic Export Information
EV—Exchange Value
EVe—Exchange Value Equivalent
EPA—U.S. Environmental Protection Agency
FAA—Federal Aviation Administration
FAR—Federal Acquisition Regulation
FDA—U.S. Food and Drug Administration
FIFRA—Federal Insecticide, Fungicide, and
Rodenticide Act
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FSTOC—Fire Suppression Technical Options
Committee
FTOC—Flexible and Rigid Foams Technical
Options Committee
FR—Federal Register
GHG—Greenhouse Gas
GWP—Global Warming Potential
HCFO—Hydrochlorofluoroolefin
HFC—Hydrofluorocarbon
HFIB—Hexafluoroisobutylene
HFO—Hydrofluoroolefin
ICAO—International Civil Aviation
Organization
ICR—Information Collection Request
IPCC—Intergovernmental Panel on Climate
Change
ITN—Internal Transaction Number
Kg—Kilogram
MCMEU—Mission-Critical Military End Uses
MCTOC—Medical and Chemicals Technical
Options Committee
MDI—Metered Dose Inhaler
MT—Metric Ton
MTEVe—Metric Tons of Exchange Value
Equivalent
NAICS—North American Industry
Classification System
NF3—Nitrogen Trifluoride
ODP—Ozone Depletion Potential
ODS—Ozone-Depleting Substances
OMB—U.S. Office of Management and
Budget
PFC—Perfluorocarbon
PII—Personally Identifiable Information
PRA—Paperwork Reduction Act
PU—Polyurethane
RACA—Requests for Additional
Consumption Allowance
RFA—Regulatory Flexibility Act
RIA—Regulatory Impact Analysis
RSV—Respiratory Syncytial Virus
SCPPU—Structural Composite Preformed
Polyurethane
SF6—Sulfur Hexafluoride
SiN—Silicon Nitride
SiO2—Silicon Dioxide
SNAP—Significant New Alternatives Policy
SISNOSE—Significant Economic Impact on a
Substantial Number of Small Entities
TCE—Trichloroethylene
TEAP—Technology and Economic
Assessment Panel
TSCA—Toxic Substances Control Act
TSD—Technical Support Document
UMRA—Unfunded Mandates Reform Act
Table of Contents
I. Executive Summary
A. Purpose of the Proposed Regulatory
Action
B. Summary of Proposed Actions
II. General Information
A. Does this action apply to me?
B. What is EPA’s authority for taking this
action?
III. Background
IV. How is EPA assessing whether to extend
eligibility for application-specific
allowances?
A. How is EPA interpreting the ‘‘no safe or
technically achievable substitute will be
available’’ criterion?
B. How is EPA interpreting the insufficient
supply of regulated substances criterion?
C. What is EPA’s proposed framework for
renewing applications?
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V. Review of the Six Applications Listed in
the AIM Act
A. Overview of Total U.S. HFC
Consumption
B. Propellants in Metered Dose Inhalers
1. Availability of Safe and Technically
Achievable Substitutes
2. Supply
3. What is EPA proposing regarding
eligibility for application-specific
allowances?
C. Defense Sprays
1. Availability of Safe and Technically
Achievable Substitutes
2. Supply
3. What is EPA proposing regarding
eligibility for application-specific
allowances?
4. Proposed Restriction Under EPA’s
Technology Transitions Program
D. Structural Composite Preformed
Polyurethane Foam for Marine Use and
Trailer Use
1. Availability of Safe and Technically
Achievable Substitutes
2. Supply
3. What is EPA proposing regarding
eligibility for application-specific
allowances?
4. Proposed Restriction Under EPA’s
Technology Transitions Program
E. Etching of Semiconductor Material or
Wafers and the Cleaning of Chemical
Vapor Deposition Chambers Within the
Semiconductor Manufacturing Sector
1. Availability of Safe and Technically
Achievable Substitutes
2. Supply
3. What is EPA proposing regarding
eligibility for application-specific
allowances?
F. Mission-Critical Military End Uses
1. Availability of Safe and Technically
Achievable Substitutes
2. Supply
3. What is EPA proposing regarding
eligibility for application-specific
allowances?
G. Onboard Aerospace Fire Suppression
1. Availability of Safe and Technically
Achievable Substitutes
2. Supply
3. What is EPA proposing regarding
eligibility for application-specific
allowances?
VI. What are the proposed requirements
associated with a petition to be listed as
an application that will receive
application-specific allowances?
VII. Proposed Revisions to Existing
Regulations
A. Expected Total HFC Purchases
B. Unique Circumstances
C. Methodology for Entities With Irregular
Purchasing History and Very Small Users
D. Average Annual Growth Rate
Calculations
E. Inventory
F. Department of Defense Conferrals
G. Limited Set-Aside for Unique
Circumstances Related to MDIs
H. Return of Unneeded Allowances
I. Enabling Auctions of Illegally Imported
HFCs
J. Quarterly Exporter Reporting of Internal
Transaction Numbers
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K. Date of Purchase for Requests for
Additional Consumption Allowances
(RACAs)
VIII. Authorization To Produce for Export
A. To what entities is EPA proposing to
allocate production for export
allowances?
B. How many production for export
allowances is EPA proposing to issue to
Iofina on an annual basis, and for how
many years is EPA proposing to issue
these allowances?
C. Would Iofina need to expend
consumption allowances for materials
produced with production for export
allowances and subsequently exported?
D. How will this process affect the issuance
of other types of allowances?
E. What are the proposed recordkeeping
and reporting requirements for
production for export allowances?
1. Annual Certifications
2. Quarterly Export and Inventory
Reporting
3. Recordkeeping
IX. How will EPA handle confidentiality for
newly reported information?
A. Background on Determinations of
Whether Information Is Entitled to
Treatment as Confidential Information
B. Data Elements Associated With a
Petition To Be Listed as an Application
That Will Receive Application-Specific
Allowances
C. Data Elements Related to Proposed
Revisions to Existing Regulations
D. Data Elements Reported to EPA Related
to Production for Export
X. What are the costs and benefits of this
action?
XI. Statutory and Executive Order Review
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 14094: Modernizing Regulatory
Review
B. Paperwork Reduction Act (PRA)
C. Regulatory Flexibility Act (RFA)
D. Unfunded Mandates Reform Act
(UMRA)
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
Risks and Safety Risks
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution or Use
I. National Technology Transfer and
Advancement Act
J. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low-Income
Populations and Executive Order 14096:
Revitalizing Our Nation’s Commitment
to Environmental Justice for All
I. Executive Summary
A. Purpose of the Proposed Regulatory
Action
The U.S. Environmental Protection
Agency (EPA) is undertaking this action
to implement certain provisions of the
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American Innovation and
Manufacturing Act of 2020, codified at
42 U.S.C. 7675 (AIM Act or the Act).
The Act directs EPA to implement the
phasedown of hydrofluorocarbons
(HFCs) by issuing a limited quantity of
transferrable production and
consumption allowances, which entities
must expend to produce or import
HFCs. In addition, subsection (e)(4)(B)
of the Act authorizes EPA to allocate
allowances exclusively for the use in
specific applications for which there is:
(1) no safe or technically achievable
substitute and (2) an insufficient supply
of the HFCs used in the application that
can be secured from chemical
manufacturers. The Act listed six
applications that would receive priority
access to allowances for a five-year
period beginning on December 27, 2020:
propellants in metered dose inhalers
(MDIs), defense sprays, structural
composite preformed polyurethane
(SCPPU) foam for marine use and trailer
use (hereafter referred to as SCPPU foam
for marine and trailer uses), the etching
of semiconductor material or wafers and
the cleaning of chemical vapor
deposition (CVD) chambers within the
semiconductor manufacturing sector,
mission-critical military end uses
(MCMEU), and onboard aerospace fire
suppression. EPA intends to finalize
this proposed rule ahead of the
allocation of calendar year 2026
allowances. Without finalization of this
proposed rule, all applications would be
ineligible for allowances for calendar
year 2026.1 EPA has created a category
of allowances to provide this priority
access, which EPA refers to as
application-specific allowances (ASAs).
ASAs are allocated ahead of general
pool allowances based on a
methodology intended to determine
eligible entities’ needs for regulated
substances (see Section VII of this
preamble and the Allocation Framework
Rule (86 FR 55116, October 5, 2021) for
more information). After the total ASA
quantity is determined, the remaining
allowances are distributed to general
pool allowance recipients using a
different methodology.
1 EPA first codified the allocation methodology
for general pool and ASA holders in ‘‘Phasedown
of Hydrofluorocarbons: Establishing the Allowance
Allocation and Trading Program Under the
American Innovation and Manufacturing Act’’
(hereafter referred to as the ‘‘Allocation Framework
Rule’’) (86 FR 55116, October 5, 2021). The
methodology for general pool allowance holders
was subsequently updated in ‘‘Phasedown of
Hydrofluorocarbons: Allowance Allocation
Methodology for 2024 and Later Years’’ (hereafter
referred to as the ‘‘2024 Allocation Rule’’ (88 FR
46836, July 20, 2023); the ASA methodology was
not updated in the 2024 Allocation Rule.
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Subsection (e)(4)(B)(v) of the AIM Act
directs EPA to review applications
receiving priority access to allowances
not less frequently than once every five
years, and, if the application meets the
criteria above, authorize the eligibility
of the application to receive priority
access to allowances for a period of not
more than five years. EPA is proposing
how the Agency will interpret these two
criteria to review applications receiving
ASAs. EPA is also proposing decisions
to renew or not renew each of the six
applications that currently receive
ASAs.
Separately, subsection (i) of the Act
authorizes EPA, by rulemaking, to
restrict the use of HFCs in sectors or
subsectors where the regulated
substances are used. Under the
authority of this provision, EPA
finalized the rule ‘‘Phasedown of
Hydrofluorocarbons: Restrictions on the
Use of Certain Hydrofluorocarbons
Under the American Innovation and
Manufacturing Act of 2020’’ (hereafter
referred to as the ‘‘2023 Technology
Transitions Rule’’; 88 FR 73098, October
24, 2023), which established restrictions
for three sectors and 39 subsectors. The
rule exempted applications with a
current qualification for ASAs. As such,
if an application is no longer eligible to
receive ASAs, it would become subject
to the restrictions established in the
2023 Technology Transitions Rule. EPA
is therefore proposing how the
Technology Transitions regulations
would apply to applications if EPA were
to determine that those applications are
not eligible for renewal for the full fiveyear period.
The Act also includes a provision for
the public to petition EPA to designate
an application as eligible for priority
access to allowances. EPA is proposing
a procedural process for submitting a
petition under this provision and to
define minimum required elements of
such a petition. In addition, this
rulemaking proposes narrow revisions
to the methodology used to allocate
allowances to ASA holders for calendar
years 2026 and beyond as well as other
limited revisions to the existing 40 CFR
part 84 regulations. EPA is also
proposing to authorize an entity to
produce regulated substances for export
for application-specific uses pursuant to
subsection (e)(5). Lastly, EPA is
proposing certain confidentiality
determinations for newly reported
information if this rulemaking is
finalized as proposed.
B. Summary of Proposed Actions
Application-specific allowance holder
review: EPA is describing how it
proposes to interpret the criteria under
subsection (e)(4)(B) of the AIM Act and
evaluate the six categories of ASA
holders listed in subsection (e)(4)(B)(v)
of the Act. EPA is proposing to renew
the following applications for the full
five-year period from 2026–2030:
propellants in MDIs, the etching of
semiconductor material or wafers and
the cleaning of CVD chambers within
the semiconductor manufacturing
sector, MCMEU, and onboard aerospace
fire suppression. EPA is co-proposing
two options for defense sprays: do not
renew or renew for a two-year period
through 2027. EPA is co-proposing three
options for SCPPU foams for marine and
trailer uses: do not renew, renew for a
two-year period through 2027, or renew
for the full five-year period from 2026–
2030 with allowance amounts
determined based on the exchange value
(EV) of a substitute HFC. In cases where
EPA is proposing to change the status of
ASA holders, this proposal also details
how the Technology Transitions
regulations would apply to those
applications.
Application-specific allowance holder
petitions: EPA is proposing the process
and information requirements for
submitting petitions under subsection
(e)(4)(B) of the AIM Act which seek the
designation of an application as an
essential use.
Application-specific allowance
methodology: EPA is proposing targeted
revisions to the existing ASA
methodology: to require companies to
provide a total request for allowances
for the calendar year, to expand
permissible scenarios that could qualify
as unique circumstances, to use a
different allocation methodology for
certain very small users of HFCs and
entities with irregular purchasing
history, how to account for inventory in
allocation decisions, to establish a setaside of allowances for situations that
meet the criteria for unique
circumstances related to medical
conditions treated by MDIs, and to
allow ASA holders to return a portion
of their allowances voluntarily if they
do not intend to use them. EPA is also
proposing new requirements for
conferrals of MCMEU allowances and
an opportunity to return unneeded
ASAs.
Other regulatory revisions: EPA is
proposing other specific regulatory
changes to: clarify the ability of the
Federal government to pursue, if
appropriate, auctioning illegally
imported HFCs that are seized by
enforcement officials, require exporting
companies to report ‘‘Internal
Transaction Numbers’’ (ITNs) quarterly,
and simplify the reporting on ‘‘date of
purchase’’ for a Request for Additional
Consumption Allowances (RACA).
Authorization of production for
export: EPA is proposing to authorize an
entity to produce for export for
application-specific uses abroad.
Handling of confidentiality for newly
reported information: EPA is proposing
certain confidentiality determinations
for newly reported information if this
rulemaking is finalized as proposed.
II. General Information
A. Does this action apply to me?
You may be potentially affected by
this proposal if you use HFCs in one of
the six applications eligible for an
allocation under section (e)(4)(B)(iv) of
the AIM Act. You may also potentially
be affected if you produce, import,
export, purify, destroy, reclaim,
package, or otherwise distribute HFCs
for end users in one of these six
applications or are a current HFC
allowance holder. Potentially affected
categories, North American Industry
Classification System (NAICS) codes,
and examples of potentially affected
entities are included in Table 1.
TABLE 1—NAICS CLASSIFICATION OF POTENTIALLY AFFECTED ENTITIES
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NAICS code
325120
325199
325211
325412
325414
325998
326220
326150
326299
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NAICS industry description
Industrial Gas Manufacturing.
All Other Basic Organic Chemical Manufacturing.
Plastics Material and Resin Manufacturing.
Pharmaceutical Preparation Manufacturing.
Biological Product (except Diagnostic) Manufacturing.
All Other Miscellaneous Chemical Product and Preparation Manufacturing.
Rubber and Plastics Hoses and Belting Manufacturing.
Urethane and Other Foam Product.
All Other Rubber Product Manufacturing.
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TABLE 1—NAICS CLASSIFICATION OF POTENTIALLY AFFECTED ENTITIES—Continued
NAICS code
NAICS industry description
333415 .................................
Air-Conditioning and Warm Air Heating Equipment and Commercial and Industrial Refrigeration Equipment Manufacturing.
Industrial Mold Manufacturing.
Semiconductor and Related Device Manufacturing.
Other Electronic Component Manufacturing.
Electromedical and Electrotherapeutic Apparatus Manufacturing.
Truck Trailer Manufacturing.
Travel Trailer and Camper Manufacturing.
Aircraft Manufacturing.
Ship Building and Repairing.
Boat Building.
Military Armored Vehicle, Tank, and Tank Component Manufacturing.
Military Ships, Building, and Repairing.
Surgical and Medical Instrument Manufacturing.
Plumbing and Heating Equipment and Supplies (Hydronics) Merchant Wholesalers.
Warm Air Heating and Air-Conditioning Equipment and Supplies Merchant Wholesalers.
Refrigeration Equipment and Supplies Merchant Wholesalers.
Industrial Machinery and Equipment Merchant Wholesalers.
Industrial Supplies Merchant Wholesalers.
Transportation Equipment and Supplies (except Motor Vehicle) Merchant Wholesalers.
Other Chemical and Allied Products Merchant Wholesalers.
Freight Transportation Arrangement.
Testing Laboratories.
Research and Technology in Biotechnology (except Nanobiotechnology).
Solid Waste Collection.
Hazardous Waste Treatment and Disposal.
Materials Recovery Facilities.
Fire Protection.
333511 .................................
334413 .................................
334419 .................................
334510 .................................
336212 .................................
336214 .................................
336411 .................................
336611 .................................
336612 .................................
336992 .................................
SIC 373102 ..........................
339112 .................................
423720 .................................
423730 .................................
423740 .................................
423830 .................................
423840 .................................
423860 .................................
424690 .................................
488510 .................................
541380 .................................
541714 .................................
562111 .................................
562211 .................................
562920 .................................
922160 .................................
This table is not intended to be
exhaustive, but rather provide a guide
for readers regarding entities likely to be
affected by this action. Other types of
entities not listed in this section could
also be affected. If you have any
questions regarding the applicability of
this action to a particular entity, consult
the person listed under FOR FURTHER
INFORMATION CONTACT.
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B. What is EPA’s authority for taking
this action?
On December 27, 2020, the AIM Act
was enacted as section 103 in Division
S, Innovation for the Environment, of
the Consolidated Appropriations Act,
2021 (codified at 42 U.S.C. 7675). In
subsection (k)(1)(A), the AIM Act
provides EPA with the authority to
promulgate necessary regulations to
carry out EPA’s functions under the Act,
including its obligations to ensure that
the Act’s requirements are satisfied (42
U.S.C. 7675(k)(1)(A)). Subsection
(k)(1)(C) of the Act also provides that
Clean Air Act (CAA) sections 113, 114,
304, and 307 apply to the AIM Act and
any regulations EPA promulgates under
the AIM Act as though the AIM Act
were part of title VI of the CAA.
Accordingly, this rulemaking is subject
to CAA section 307(d) (see 42 U.S.C.
7607(d)(1)(I)) (CAA section 307(d)
applies to ‘‘promulgation or revision of
regulations under subchapter VI of this
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chapter (relating to stratosphere and
ozone protection)’’).
The AIM Act authorizes EPA to
address HFCs in three main ways:
phasing down HFC production and
consumption through an allowance
allocation program, facilitating the
transition to next-generation
technologies by restricting use of these
HFCs in the sector or subsectors in
which they are used, and promulgating
certain regulations for purposes of
maximizing reclaiming and minimizing
releases of HFCs from equipment and
ensuring the safety of technicians and
consumers. This proposal relates to the
first area and addresses restrictions in
the second area for impacted subsectors.
The Act required EPA, for the fiveyear period beginning on December 27,
2020, to allocate the full quantity of
allowances necessary, based on
projected, current, and historical trends,
for the production or consumption of
regulated substances for the exclusive
use in six applications: propellants in
MDIs, defense sprays, SCPPU foam for
marine and trailer uses, the etching of
semiconductor material or wafers and
the cleaning of CVD chambers within
the semiconductor manufacturing
sector, MCMEU, and onboard aerospace
fire suppression (42 U.S.C.
7675(e)(4)(B)(iv)(I)). EPA has defined
these allowances as ASAs. EPA intends
to finalize this rulemaking ahead of the
allocation of calendar year 2026
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allowances. Without finalization of this
rulemaking, all applications would be
ineligible for application-specific
allowances for calendar year 2026.
Subsection (e)(4)(B)(v) of the AIM Act
requires EPA to review applications
receiving allocations pursuant to
subsection (e)(4)(B)(iv) at least every
five years. If pursuant to this review
EPA determines that the requirements of
two statutory criteria are met, EPA shall
authorize production or consumption,
as applicable, of the exclusive use of
regulated substances in the application
for renewable periods of not more than
five years. Specifically, EPA must
determine whether: (1) no safe or
technically achievable substitute will be
available during the applicable period
for the application; and (2) the supply
of the regulated substance that
manufacturers or users of the regulated
substance for that application are
capable of securing from chemical
manufacturers is insufficient to
accommodate the application.
Separately, an entity may file a
petition for an application to receive
ASAs. The AIM Act outlines timeframes
and deadlines for EPA to act on such a
petition and how the Agency should
assess such a petition (42 U.S.C.
7675(e)(4)(B)(ii)). Specifically, not later
than 180 days after receiving a petition,
EPA must propose and seek public
comment on whether to provide ASAs
for the application. Not later than 270
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days after EPA receives a petition, the
Agency must take final action on the
petition. Any application determined to
be eligible for ASAs would also be
subject to the review requirements in
subsection (e)(4)(B)(v).
Subsection (i) of the AIM Act,
‘‘Technology Transitions,’’ provides that
‘‘the Administrator may by rule restrict,
fully, partially, or on a graduated
schedule, the use of a regulated
substance in the sector or subsector in
which the regulated substance is used’’
(42 U.S.C. 7675(i)(1)). However, rules
promulgated under subsection (i) ‘‘shall
not apply to . . . an essential use under
clause (i) or (iv) of subsection (e)(4)(B),
including any use for which the
production or consumption of the
regulated substance is extended under
clause (v)(II) of that subsection’’ (42
U.S.C. 7675(i)(7)(B)(i)). Therefore, per
subsection (i)(7)(B)(i), the restrictions
promulgated under the Technology
Transitions Program are not currently
applicable to any application receiving
an ASA (40 CFR 84.56(a)(2)). To the
extent that this proposal would result in
an application no longer receiving an
ASA, this action also proposes the
Technology Transitions Program
restrictions that would apply to that
application, if any, based on EPA’s
consideration of the factors listed in
subsection (i)(4) of the AIM Act, should
EPA finalize a determination that an
application can no longer receive an
ASA.
Prior to proposing a rule, subsection
(i)(2)(A) of the Act directs EPA to
consider negotiating with stakeholders
in the sector or subsector subject to the
potential rule in accordance with
negotiated rulemaking procedures
established under subchapter III of
chapter 5 of title 5, United States Code
(commonly known as the ‘‘Negotiated
Rulemaking Act of 1990’’). If EPA makes
a determination to use the negotiated
rulemaking procedures, subsection
(i)(2)(B) requires that EPA, to the extent
practicable, give priority to completing
that rulemaking over completing
rulemakings under subsection (i) that
are not using that procedure. If EPA
does not use the negotiated rulemaking
process, subsection (i)(2)(C) requires the
Agency to publish an explanation of the
decision not to use that procedure
before commencement of the
rulemaking process. The Negotiated
Rulemaking Act of 1990 (5 U.S.C. 563)
provides seven criteria that the head of
an agency should consider when
determining whether a negotiated
rulemaking is in the public interest,
namely, whether: (1) there is a need for
a rule; (2) there are a limited number of
identifiable interests that will be
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significantly affected by the rule; (3)
there is a reasonable likelihood that a
committee can be convened with a
balanced representation of persons who
can adequately represent the identified
interests and are willing to negotiate in
good faith to reach a consensus on the
proposed rule; (4) there is a reasonable
likelihood that a committee will reach a
consensus on the proposed rule within
a fixed period of time; (5) the negotiated
rulemaking procedure will not
unreasonably delay the notice of
proposed rulemaking and the issuance
of the final rule; (6) the agency has
adequate resources and is willing to
commit such resources, including
technical assistance, to the committee;
and (7) the agency, to the maximum
extent possible consistent with the legal
obligations of the agency, will use the
consensus of the committee with respect
to the proposed rule as the basis for the
action proposed by the agency for notice
and comment.
If a head of agency determines that
the use of the negotiated rulemaking
procedure is in the public interest, an
agency may convene a federally
chartered advisory committee, and may
rely on an appointed convener under 5
U.S.C. 563(b) to assist with ascertaining
the names of persons who are willing
and qualified to represent interests that
will be significantly affected by the
proposed rule. If the agency decides to
establish a negotiated rulemaking
committee, the agency must publish in
the Federal Register and in relevant
publications a notice announcing the
agency’s intention to establish a
negotiated rulemaking committee, a
description of the subject and scope of
the rule, a list of the interests which are
likely to be significantly affected by the
rule, a list of the persons proposed to
represent such interests and the
proposed agency representatives, a
proposed agenda and schedule for
completing the committee’s work, a
description of the administrative and
technical support to be provided to the
committee by the agency, a solicitation
for comments on the proposal to
establish the committee and on the
proposed membership of the committee,
and an explanation of how a person may
apply or nominate another person for
membership on the committee. The
agency must provide at least 30 calendar
days for the submission of comments
and applications related to the
membership of the committee. In
establishing and administering such a
committee, the agency shall comply
with the Federal Advisory Committee
Act, unless an exception applies. If the
committee reaches consensus on a
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proposed rule, the committee shall
transmit a report containing the
proposed rule to the Federal agency. If
the committee does not reach a
consensus on a proposed rule, the
committee may transmit a report
specifying any areas upon which
consensus was reached. The proposed
rule is still subject to public comment,
and for purposes of a rulemaking
developed under the AIM Act, the
requirements of CAA section 307(d).
Before proposing the 2023
Technology Transitions Rule, consistent
with AIM Act subsection (i)(2)(A) and
(C), EPA considered whether to
negotiate with stakeholders using the
negotiated rulemaking procedure
provided for in the Negotiated
Rulemaking Act of 1990, decided not to
use such procedures, and published its
explanation of that decision in the
Federal Register (86 FR 74080,
December 29, 2021).
EPA noted in the final 2023
Technology Transitions Rule that,
where appropriate, EPA will consider
recent Agency actions and decisions
related to restrictions on the use of
HFCs in sectors and subsectors for its
consideration on using negotiated
rulemaking procedures. EPA did not, for
example, separately consider using
negotiated rulemaking for four petitions
that were received after a rulemaking
process had already been commenced
regarding the same sectors and
subsectors, nor did EPA consider anew
whether or not to use negotiated
rulemaking in an interim final rule (88
FR 88825, December 26, 2023) that
amended one provision of the 2023
Technology Transitions Rule for one
subsector.
Similarly, the proposed changes to the
Technology Transitions regulations
contemplated in this action would be
targeted at a subset of applications
within a subsector subject to those
restrictions. EPA is not addressing a
new subsector in this proposal, nor even
proposing a different level of stringency
from already promulgated restrictions;
rather, this action proposes only to
establish deadlines by which
applications would need to comply with
Technology Transitions regulations in
the event that those applications no
longer receive ASAs. EPA does not
believe that the public interest would be
served by using the negotiated
rulemaking procedure for this limited
adjustment to the Technology
Transitions regulations, especially
because timeliness is a concern.
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III. Background
fluorinated
HFCs are
chemicals that have no known natural
sources. HFCs are used in a variety of
applications such as refrigeration and
air conditioning, foam blowing agents,
solvents, aerosols, and fire suppression.
HFCs are potent greenhouse gases
(GHGs) with 100-year global warming
potentials (GWPs) (a measure of the
relative climatic impact of a GHG) that
can be hundreds to thousands of times
that of carbon dioxide (CO2).
HFC use and emissions have been
growing worldwide due to the global
phaseout of ozone-depleting substances
(ODS) under the Montreal Protocol on
Substances that Deplete the Ozone
Layer (Montreal Protocol), and the
increasing use of refrigeration and airconditioning equipment globally. HFC
emissions had previously been
projected to increase substantially over
the next several decades. In 2016, in
Kigali, Rwanda, countries agreed to
adopt an amendment to the Montreal
Protocol, known as the Kigali
Amendment, which provides for a
global phasedown of the production and
consumption of HFCs. The United
States ratified the Kigali Amendment on
October 31, 2022. Global adherence to
the Kigali Amendment would
substantially reduce future emissions,
leading to a peaking of HFC emissions
before 2040.
There are hundreds of possible HFC
compounds. The 18 HFCs listed as
regulated substances by the AIM Act are
some of the most commonly used HFCs
(neat and in blends) and have high
impacts as measured by the quantity of
each substance emitted multiplied by
their respective GWPs. These 18 HFCs
are all saturated, meaning they have
only single bonds between their atoms,
and therefore have longer atmospheric
lifetimes than fluorinated compounds
that are unsaturated. More detailed
information on HFCs, their uses, and
their impacts is available in the
Allocation Framework Rule (86 FR
55116, October 5, 2021).
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IV. How is EPA assessing whether to
extend eligibility for applicationspecific allowances?
As noted in Section II.B of this
preamble, the AIM Act directs EPA to
undertake a review of applications
receiving allowances pursuant to
subsection (e)(4)(B)(iv) at least every
2 While the overwhelming majority of HFC
production is intentional, EPA is aware that HFC–
23 can be a byproduct associated with the
production of other chemicals, including but not
limited to hydrochlorofluorocarbon (HCFC)–22 and
other fluorinated gases.
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five years. The statute says that access
to ASAs shall be authorized for a
renewed period if two statutory criteria
are met. Specifically: (1) ‘‘no safe or
technically achievable substitute will be
available during the applicable period
for that application; and’’ (2) ‘‘the
supply of the regulated substance that
manufacturers or users of the regulated
substance for that application are
capable of securing from chemical
manufacturers . . . including any
quantities of a regulated substance
available from production or import, is
insufficient to accommodate the
application’’ (42 U.S.C.
7675(e)(4)(B)(1)). In this section, we
outline how EPA interprets these
criteria, what information the Agency
will consider in assessing these criteria,
and a proposed framework for
evaluating if an application is eligible
for renewal for up to five years. EPA
notes that under the statute, these
criteria also apply to new applications
that may be listed, but, aside from
Section VI addressing the petition
process, this proposed rulemaking is
primarily focused on the renewal of
existing applications. However, EPA’s
interpretations of the criteria discussed
in this section would apply to future
actions to add new applications. The
AIM Act includes additional evaluation
considerations for new applications in
subsection (e)(4)(B)(i), but the Agency is
not addressing their interpretation in
this rulemaking.
A. How is EPA interpreting the ‘‘no safe
or technically achievable substitute will
be available’’ criterion?
In order for an application to continue
to be eligible to receive ASAs, EPA must
determine ‘‘no safe or technically
achievable substitute will be available’’
for the application during the time
period under review (42 U.S.C.
7675(e)(4)(B)(i)(I)). EPA is proposing
that the best interpretation of this
criterion is that if there is an available
substitute that is both safe and
technically achievable, an application
would not meet this criterion for
renewal. EPA acknowledges that the
statutory language could be ambiguous
as to whether a substitute must be both
safe and technically achievable.
However, reading the statutory language
differently than proposed would seem
to create a perverse outcome. In such a
scenario, an application would become
ineligible for ASAs if EPA identified a
substitute that was technically
achievable, but not safe. EPA reads the
context of subsection (e)(4) as indicating
that Congress intended that listed
applications continue to receive priority
access to allowances as long as the
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application needed to use regulated
substances. In a situation where an
identified substitute is not safe, EPA
believes that it would be Congress’s
intent to continue to provide priority
access to allowances such that the
application was not prematurely forced
to transition to an unsafe substitute.
Similarly, it does not seem reasonable to
take away access to ASAs when an
identified substitute is safe, but not
technically achievable. If the
application cannot technically
implement the transition to a substitute,
it seems unrealistic to think that there
could be a transition away from
regulated substances. Accordingly, EPA
proposes to interpret the statutory text
and surrounding framework such that if
EPA determines there is no safe
substitute that is technically achievable
for an application, or a technically
achievable substitute is not safe, the
application would meet the first
criterion for renewal.
In looking at potential substitutes for
an application under subsection
(e)(4)(B)(i)(I), EPA is proposing to
consider regulated substances (i.e., other
HFCs), alternative substances (e.g.,
hydrofluoroolefins (HFOs),
hydrocarbons), and blends of HFCs and/
or HFC alternatives that can perform the
same general function as the current
HFC in use. EPA is proposing that such
an interpretation of the term
‘‘substitute’’ is most consistent with the
statutory language of subsection
(e)(4)(B) as a whole. Specifically, in its
direction to EPA to review applications
receiving ASAs every five years,
Congress directed EPA to ‘‘review the
availability of substitutes, including any
quantities of the regulated substance
available.’’ This sentence structure,
indicating that examination of
quantities of regulated substances
available would be included as part of
analyzing what substitutes are available,
suggests that regulated substances are
part of the universe of substitutes that
Congress intended EPA to include in its
review. In addition to EPA’s
determination that such an approach is
more consistent with the statutory
language than an approach of only
looking at non-regulated substances as
substitutes, EPA has also identified
other benefits of this interpretation. For
example, it would seem to be a perverse
outcome if EPA renewed an
application’s eligibility for ASAs at
historic quantities where there was an
available substitute that did not require
any or required fewer allowances to
procure. Non-HFCs may be able to fill
the same role as the HFC, often
functioning as a chemical-for-chemical
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replacement or requiring limited design
changes.
EPA is proposing, as part of its
assessment of what chemicals may be
determined to be safe as a substitute for
applications under review, to only
include substances, including blends of
substances, with a lower GWP than the
regulated substance currently in use. As
explained in the Allocation Framework
Rule (86 FR 55116, October 5, 2021), the
HFC phasedown’s significant benefits
are derived from the reduction of
production and consumption of certain
chemicals on a GWP-weighted basis.3
Considering higher-GWP substances or
blends of substances would run against
this overall objective and could reduce
the benefits of the HFC phasedown,
especially if this rulemaking led to the
uptake of higher-GWP non-HFC
technologies (e.g., semiconductor
manufacturers transitioning back to
using higher-GWP perfluorocarbons
(PFCs)). In addition, this proposed
interpretation aligns with the approach
under the 2023 Technology Transitions
Rule (88 FR 73098, October 24, 2023),
which established GWP limits for
subsectors and considered substitutes as
only those with lower GWPs. Further
discussion regarding the sources EPA is
relying on to determine if a substitute is
safe (e.g., listed by EPA’s Significant
New Alternatives Policy (SNAP)
Program) can be found below.
In addition to looking at chemicals
that could serve as substitutes, EPA is
also including in its analysis any
potentially available not-in-kind
technologies (e.g., finger-pump bottles
that would not use any chemical
propellant in lieu of aerosol cans) for
purposes of subsection (e)(4)(B)(i)(I).
Such an approach is consistent with the
common understanding of the plain
language definition of ‘‘substitute.’’ For
example, Merriam Webster defines
substitute as a thing that ‘‘takes the
place of function of another’’ and the
Oxford dictionary similarly notes a
substitute is a ‘‘thing acting or serving
in place of another.’’ In general, not-inkind technologies can serve the need of
some applications, so it is appropriate to
include them within the scope of
assessing safe and technically
achievable substitutes. It would be
unnecessarily limiting to exclude from
the scope of the analysis a technology
that performs the same general function
for the application as the current HFC
in use does. EPA also acknowledges that
3 While the AIM Act calls for reduction of HFC
production and consumption on an EV-weighted
basis, EV and GWP are numerically equal. Lower
GWP is an important consideration for whether a
substitute is safe, so EPA is using GWP instead of
EV in the discussion in this section of the rule.
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market pressure from the HFC
phasedown may encourage a transition
into not-in-kind technologies (and nonHFCs) by limiting the supply of HFCs
on a GWP-weighted basis, while the
Technology Transitions Program
prohibits the use of certain HFCs in
certain sectors and subsectors. There is
also precedent for considering not-inkind technologies under CAA Title VI,
such as the SNAP Program and
Nonessential Product Bans, and the AIM
Act Technology Transitions Program, all
of which also evaluate not-in-kind
substitutes as possible alternatives to
ODS and HFCs, respectively.
EPA is aware that a transition to
certain substitutes will require changes
to how the HFCs are used in the
application (e.g., accommodating a
flammable HFC in the manufacturing
process). Shifts to not-in-kind
technologies will inherently require a
change in manufacturing and/or the
product, so it would be a consistent
approach to also not outright exclude
substitute chemicals that would
similarly require a change in
manufacturing process or the product.
EPA does not want to unnecessarily
limit the scope of the substitute analysis
at this point in time, and therefore is
considering a wide range of possible
safe and technically achievable
substitutes. The phasedown of HFCs is
still nascent, and, at this point, we
cannot know the full breadth of
technologies that will be developed as
replacements for the current HFCs in
use.
The Agency is proposing to assess this
criterion, specifically that a substitute is
safe, technically achievable, and
available, on an application-wide basis.
For applications that use multiple HFCs,
a substitute would need to be able to
replace all HFCs used (or multiple
substitutes that replace all individual
HFCs would need to be available). For
applications that have sub-applications
(e.g., defense sprays include those
intended for humans and those
intended for animals), there would need
to be a viable substitute for known subapplications. EPA’s interpretation is that
it would be unreasonable to consider an
application as having met this criterion
and thereby ineligible for renewal
unless all known sub-applications can
successfully transition away from their
currently used HFC(s).
EPA’s evaluation of each application
is not intended to be a company-specific
review; the commercialization 4 of a
substitute by one sub-application
suggests the substitute is safe or
technically achievable for the entire
application barring evidence, such as
testing data, to the contrary. However,
there are additional barriers to
commercialization, which are
considered when assessing if the
identified substitute is available for an
entire application. In addition, EPA’s
interpretation of the statutory language
is that applications are intended to be
viewed as a whole and not necessarily
renewed by sub-application.
Specifically, the listing of the
applications in subsection (e)(4)(B)(iv)(I)
does not break down the application
into sub-applications (e.g., ‘‘defense
sprays’’ is not listed as multiple separate
applications, e.g., ‘‘personal defense
sprays,’’ ‘‘law enforcement defense
sprays,’’ and ‘‘bear defense sprays’’).
Similarly, for applications that use
multiple HFCs and have specific uses
for the individual HFCs, it would not be
reasonable to assess this criterion as
being met if an application does not
have an available safe and technically
achievable substitute for each HFC. It is
EPA’s opinion that Congress did not
intend for an application to lose its
eligibility for ASAs if it could only
transition some, but not all, of the HFCs
currently used in the application.
EPA reviewed a range of sources in
developing its assessment of the
availability of safe, technically
achievable substitutes for each
application at issue here. Sources
include, but are not limited to:
manufacturer announcements;
information provided by stakeholders
under part 84 reporting requirements
and other communications; relevant
Federal and State regulations;
evaluations carried out under the 2023
Technology Transitions Rule (88 FR
73098, October 24, 2023) and the SNAP
Program; standards from industry,
standard-setting bodies (e.g., American
Society for Heating, Refrigerating, and
Air-Conditioning Engineers (ASHRAE)),
and the U.S. Government (e.g., the U.S.
Food and Drug Administration’s (FDA)
standards for MDIs); and peer-reviewed
technical reports. The Technical
Support Document (TSD) ‘‘Draft Review
of Applications in the American
Innovation and Manufacturing (AIM)
Act Section (e)(4)(B)(4)’’ contains a
comprehensive array of sources we
looked at for each application, and EPA
is taking comment on other relevant
sources that should be considered.
4 EPA is using the term ‘‘commercialization’’ to
mean that the substitute is commercially available
and actively being used in an application’s
equipment or sold on the market (domestically or
internationally) for use in the application.
‘‘Commercialization’’ is not intended to be equated
with ‘‘available,’’ as explained in more detail in the
main text.
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As noted, EPA is considering the
listings under the SNAP Program as part
of its assessment. The SNAP Program
has an established history evaluating
substitutes for ODS, many of which are
also possible substitutes for HFCs.
Where relevant, in its assessment of the
availability of safe substitutes, EPA
considered information from the SNAP
Program, including the listings
themselves and the information
underlying SNAP Program decisions.
The SNAP Program does not evaluate
substitutes for semiconductor etching
and cleaning of CVD chambers. Some
military applications are covered under
the SNAP Program. In other cases, such
as MDIs and SCPPU foams, while these
applications are within the scope of the
SNAP Program, there may be other
sources of information (e.g., the FDA,
company information) that may be more
appropriate.
In its evaluation of substitutes and
related decisions (e.g., to list as
acceptable or unacceptable), the SNAP
Program carries out a comparative risk
evaluation and considers whether a
substitute to an ozone-depleting
substance presents human health and
environmental risks that are lower than
or comparable to such risks from other
substitutes that are currently or
potentially available for the same uses.
The human health risks analyzed
include safety, and in particular,
flammability, toxicity, and exposure (of
workers, consumers, and the general
population) to chemicals with direct
toxicity; environmental risks include
ozone depletion potential (ODP) and
GWP. Information and data relied upon
in the SNAP Program are directly
relevant to EPA’s assessment of
substitutes in this rulemaking, and
therefore EPA has pulled from and
relied upon SNAP Program assessments
as appropriate.
EPA evaluates substitutes under the
SNAP Program on an ongoing basis and
over time has listed numerous
substances as ‘‘acceptable,’’ ‘‘acceptable,
subject to use conditions,’’ or
‘‘acceptable, subject to narrowed use
limits.’’ ‘‘Acceptable subject to use
conditions’’ indicates that a substitute is
acceptable only if used in a certain way.
Use conditions can include, but are not
limited to, warning labels, compliance
with relevant safety standards, and
restrictions on where a substitute is
used (e.g., HFC–134a is acceptable for
FDA-approved MDIs for medical
purposes but is not acceptable for a
majority of aerosol uses, and some fire
suppression substitutes may only be
used in typically unoccupied spaces).
EPA can also list substitutes as
‘‘acceptable subject to narrowed use
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limits’’ under SNAP, indicating that a
substitute may be used only within
certain specialized applications within
an end use and may not be used for
other applications within that end use
(e.g., SNAP has previously listed some
substitutes as acceptable for only
narrowed use limits for military or
space- and aeronautics-related
applications). In listing of a chemical as
acceptable or acceptable subject to use
conditions directly relevant to the
application, the SNAP Program makes
an assessment that the benefits
outweigh the risks relative to other
alternatives; these listings are relevant
data to support EPA’s determination
under AIM Act subsection (e)(4)(B) on
whether a substitute is ‘‘safe’’ under the
interpretation proposed in this
rulemaking.
EPA lists substitutes as
‘‘unacceptable’’ under SNAP if the
Agency determines that they may
increase overall risk to human health
and the environment, compared to other
alternatives that are available or
potentially available for the same use.
EPA has listed substitutes as
unacceptable considering the human
health criteria described above, as well
as the environmental factors considered
under SNAP. For example, SNAP has
listed certain substitutes as
unacceptable due to unusually high
ODP, GWP, toxicity and exposure, and
flammability (where it is not clear how
to mitigate risks sufficiently).
Substitutes listed as unacceptable in an
end use are prohibited for that use and
therefore would not be an available safe
or technically achievable substitute for
an application under our proposed
interpretation of this criterion.
The Agency is also reviewing the
evaluations carried out for the 2023
Technology Transitions Rule (88 FR
73098, October 24, 2023) and relying on
information and assessments done in
that rulemaking, as appropriate. In
establishing restrictions, the Technology
Transitions Program factored in the
availability of substitutes, considering
both safety and technological
achievability, among other factors. The
Technology Transitions Program relied
on information from a wide range of
sources when assessing availability,
including but not limited to, SNAP, the
Montreal Protocol’s Technology and
Economic Assessment Panel (TEAP),
standards bodies, and information
provided by industry, States, and
environmental non-governmental
organizations. Though the Technology
Transitions Program looked subsectorwide, not at specific end uses, and did
not specifically analyze the applications
currently receiving ASAs under
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subsection (e)(4)(B)(iv), some of these
applications (e.g., defense sprays and
SCPPU foams for marine and trailer
uses) have similarities with the
subsectors currently subject to
restrictions. As a result, in carrying out
the assessments undertaken in this
rulemaking, EPA is considering relevant
information from the Technology
Transition Program’s evaluations.
In the assessment undertaken in this
rulemaking, EPA is also taking into
account other Federal standards and
regulations, both within EPA and from
other U.S. Government agencies. For
many applications under review in this
rulemaking, there are applicable
regulations and standards that outline
requirements related to the chemicals or
technologies used within an
application. In these situations, such
standards and regulations may in some
instances limit use of possible
substitutes. In some instances, it may
not be possible for a substitute to ever
be used. In other instances, applicable
regulations may require entities to go
through a regulatory approval process
that would affect when an application
can transition to a substitute. Some
examples of regulations and standards
we are considering as part of our
proposed evaluations include EPA’s
regulations covering pesticides such as
bear spays and dog sprays (subapplications of defense sprays) under
the Federal Insecticide, Fungicide, and
Rodenticide Act (FIFRA; 7 U.S.C. 136–
136y), the FDA’s requirements for MDIs,
and the U.S. Federal Aviation
Administration’s (FAA) requirements
for onboard aerospace fire suppression.
Additional standards and regulations for
each application are discussed further
in the relevant chapter of the TSD. EPA
invites comment on any other standards
or regulations that entities think EPA
should consider in determining an
application’s ability to transition to a
substitute.
EPA also considered the work
undertaken by the Montreal Protocol’s
TEAP in the proposed application
assessment given the TEAP’s analytical
work on substitutes and alternative
technologies to substances controlled
under the Montreal Protocol, including
HFCs. TEAP assesses technical and
economic information that serves as the
basis for parties’ assessment of control
measures of substances under the
purview of the Montreal Protocol. Such
information is related to substitutes that
may replace the substances controlled
under the Montreal Protocol and
alternative technologies that may be
used without adverse impact on the
ozone layer and climate, production and
consumption of controlled substances,
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emissions of controlled substances,
potential alternatives for exempted uses
and others, as mandated by the parties.
This assessment includes applications
listed in AIM subsection (e)(4)(B)(iv). In
addition, TEAP develops assessments in
response to decisions taken by the
parties to the Montreal Protocol,
including but not limited to Decision
XXVIII/2, which call for an assessment
of alternatives to HFCs every five years.
EPA particularly looked at the 2022
Assessment Reports by the Medical and
Chemical Technical Options Committee,
concerning semiconductors, aerosols,
and MDIs; the Flexible and Rigid Foams
Technical Options Committee (FTOC);
and the Fire Suppression Technical
Options Committee (FSTOC). TEAP
reports have included information on
technical achievability and safety. TEAP
reports are developed by experts around
the world and provide insight into the
HFC substitutes currently in use and
under development in the United States
and globally. As such, EPA is
considering relevant information from
these reports when carrying out the
assessment of available safe or
technically achievable substitutes
undertaken in this rulemaking.
As described throughout this section,
EPA is considering information from a
wide range of sources in its assessment
of the availability of safe or technically
achievable substitutes for the
applications receiving ASAs under
subsection (e)(4)(B)(iv)(I), and no one
source will be determinative for this
criterion. Further information about
sources consulted for each application
can be found in Section V of this
preamble and the TSD. EPA invites
comment on its interpretation of ‘‘no
safe or technically achievable substitute
will be available’’ and the sources it is
considering in its assessment of this
criterion.
B. How is EPA interpreting the
insufficient supply of regulated
substances criterion?
Under the second criterion for
renewal of an application’s eligibility to
receive ASAs, EPA must determine that
‘‘the supply of the regulated substance
that manufacturers or users of the
regulated substance for that application
are capable of securing from chemical
manufacturers . . . , including any
quantities of a regulated substance
available from production or import, is
insufficient to accommodate the
application’’ (42 U.S.C.
7675(e)(4)(B)(i)(II)). As described here
and in the sections of the proposed rule
discussing each of the six applications,
a determination that there is insufficient
supply could be based on a number of
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different factors, including the available
domestic supply of the HFC(s) at issue,
demand for said HFC(s), and supply
chain constraints particular to a given
application (e.g., federally required
purity specifications). Priority access to
allowances through ASAs has the
potential to address insufficient supply
of HFCs by allowing entities that use
HFCs in an eligible application to more
easily procure HFCs from a domestic
supplier by conferring allowances to
authorize production or import or to
import the HFCs themselves.
In this proposed rulemaking, EPA is
interpreting this criterion as requiring
an assessment related to the supply of
the HFC(s) currently used in an
application’s equipment or to
manufacture the application’s products
for use. Under this proposed
interpretation, EPA would not evaluate
HFC(s) currently used exclusively for
research and development in assessing
whether there is insufficient supply.
EPA recognizes that the research and
development process may find various
alternatives to be unsuitable for an
application. Therefore, it would be
premature to consider supply of
potentially unsuitable HFC alternatives
until such time as they have been
commercialized or are close to
commercialization. Further, it could
also have the perverse effect of limiting
research into alternatives if an
application’s initial research could
prematurely contribute to removal from
eligibility for ASAs.
EPA is proposing to consider
regulated substances supplied by
chemical manufacturers in its
assessment of supply. EPA interprets
the reference to regulated substances
‘‘from chemical manufacturers’’ in 42
U.S.C. 7675(e)(4)(B)(i)(II) as direction
from Congress to assess supply from
chemical manufacturers only, and that
this direction could cover both virgin
and recovered and reprocessed HFCs.
EPA is proposing to include HFCs
produced domestically and those that
are produced abroad and imported in its
assessment of supply under this
criterion. Congress directed EPA to
consider regulated substances ‘‘from
chemical manufacturers . . . ,
including any quantities of a regulated
substance available from production or
import’’ in its assessment under 42
U.S.C. 7675(e)(4)(B)(i)(II). Because of
Congress’s reference to production and
import of regulated substances, and the
lack of any language suggesting that
chemical manufacturers should be read
as limited to only U.S. producers, EPA
intends to consider imported material
from foreign HFC producers in addition
to regulated substances from domestic
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producers. As a result, EPA is proposing
not to consider HFC supply held by and
available to entities that do not produce
or import HFCs in its assessment of this
criterion. This would exclude quantities
of HFCs held by entities that do not
produce or import HFCs with
allowances, potentially including
reclaimers, distributors, HFC blenders,5
and HFC repackagers. EPA considers
this proposed interpretation to be most
consistent with the statutory language in
42 U.S.C. 7675(e)(4)(B)(i)(II).
The Agency is proposing to consider
multiple sources of data in its
evaluation of whether supply of a
regulated substance is insufficient to
accommodate an application.
Specifically, in developing the analysis
for each application, EPA has drawn
information regarding the total expected
HFC consumption in the United States,
global production of individual HFCs
used in the applications, manufacturer
announcements regarding production of
specific HFCs, past and projected
market trends for an application that
can inform projected demand for the
HFC(s) it uses, and allowance usage by
application to date, including
conferrals, imports, and open market
purchases by ASA holders, as well as
expenditures of conferred allowances by
suppliers to ASA holders. EPA is
intending to consider data from all of
these sources collectively in order to
gain a more complete picture of
projected supply for the relevant
individual HFC(s), rather than relying
on one data point. EPA is taking
comment on these and any other
sources the agency should consider
when assessing insufficient supply.
EPA is proposing to assess
insufficient supply on an applicationwide basis. If an application uses
multiple HFCs, and the supply of at
least one of those HFCs is insufficient to
accommodate the application, EPA
would consider the criterion met for the
application. EPA interprets 42 U.S.C.
7675(e)(4)(B)(i)(II) to require the Agency
to review the supply of the regulated
substance for each regulated substance
an application uses. If there is an
insufficient supply for one HFC, EPA
would determine that this criterion is
met, and the application would
continue to be eligible for ASAs,
assuming the first criterion regarding
substitutes is also met. EPA is proposing
5 For a discussion on the difference between
producing HFCs consistent with the AIM Act and
blending HFCs to make various refrigerant blends,
see ‘‘Response to Comments’’, pg. 193, Docket ID
No. EPA–HQ–OAR–2021–0044, associated with the
Allocation Framework Rule (86 FR 55116) and the
discussion in the 2024 Allocation Rule (88 FR
46863).
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that such an approach is the best
interpretation of the AIM Act direction
in 42 U.S.C. 7675(e)(4)(B)(i)(II) that if
both criteria are met, ‘‘the Administrator
shall authorize the production or
consumption, as applicable, of any
regulated substance used in the
application.’’ A converse approach
would result in EPA not renewing the
ASA eligibility of an application that
has no available substitutes and there is
an insufficient supply available of a
regulated substance used by that
application. EPA is interpreting the AIM
Act to provide ASAs to an application
where at least one regulated substance
that manufacturers are capable of
securing is insufficient to accommodate
the application, even if the supply of a
different regulated substance is not
insufficient.
In addition to looking generally at the
supply of HFCs, EPA is also considering
relevant restrictions, if any, on the type
of HFC or supplier of HFCs that would
further limit supply to a particular
application. For example, FDA
regulations govern use of
pharmaceutical-grade HFCs by MDI
manufacturers. Facilities manufacturing
the regulated substances must comply
with FDA regulations, and there are a
limited number of purifiers. EPA is
considering any applicable relevant
Federal regulations and standards
(examples listed above in Section IV.A.),
including required regulatory approvals
and purity levels, that could limit the
supply of the HFC(s) used within an
application.
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C. What is EPA’s proposed framework
for renewing applications?
In outlining the requirement that EPA
review the applications eligible for
ASAs at least every five years, the AIM
Act states that if EPA determines ‘‘that
the requirements described in
subclauses (I) and (II) of clause (i) are
met’’ then the EPA will renew the
application’s eligibility to continue to
receive ASAs (42 U.S.C.
7675(e)(4)(B)(v)(II)) (emphasis added).
Accordingly, EPA interprets the
statutory language to mean that both
criterion (I) of clause (i) (that a
substitute is not available) and criterion
(II) (that supply is insufficient) must be
met for an application to be renewed as
eligible for ASAs. If either or both
criteria are not met as of January 1,
2026, EPA proposes to not renew an
application’s eligibility to receive ASAs.
Put another way, if EPA determines, for
example, that supply is not insufficient
to accommodate an application as of
January 1, 2026, EPA would propose to
not renew that application’s eligibility
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for ASAs, regardless of whether a
substitute is available.
If both statutory criteria are met as of
January 1, 2026, EPA intends to assess
whether an application’s fulfillment of a
criterion may change over the following
five-year period. The outcome of this
assessment would be determinative of
how long EPA will deem an application
eligible to receive ASAs. For example, if
EPA determines that there is no
substitute available as of January 1,
2026, but a substitute will be available
by January 1, 2028, EPA would renew
the application’s eligibility to receive
ASAs for only two years (i.e., calendar
years 2026 and 2027). Similarly, if
supply is deemed insufficient to
accommodate the application as of
January 1, 2026, but the market will
change such that supply will not be
insufficient to accommodate the
application as of January 1, 2028, EPA
would renew the application’s
eligibility to receive ASAs for only two
years (i.e., calendar years 2026 and
2027).
If EPA determines that an application
has a safe or technically achievable
substitute available that is a regulated
substance, EPA proposes to evaluate the
supply of the substitute HFC and assess
if supply of the substitute HFC is
insufficient to accommodate the
application. If the Agency did not do
this, the application would not be
eligible for renewal because it had met
the substitute criterion, regardless of the
supply of this substitute HFC; EPA sees
this as counter to Congress’s intent
when it established priority access to
allowances for these applications.
Further, it is EPA’s assessment that it
would be counterproductive to an
application’s efforts to transition away
from the currently used HFC(s) if EPA
did not consider the supply of the HFC
substitute when assessing eligibility for
renewal for ASAs (i.e., if an application
had insufficient supply of the substitute
HFC, an entity may be forced to return
to using its original HFC). Under the
framework proposed in this rulemaking,
if EPA determines there is an HFC
substitute, but there is insufficient
supply of that HFC substitute, EPA
would continue to list the application as
eligible for ASAs. This approach would
allow an entity transitioning to a lowerGWP HFC to remain eligible to receive
allowances until supply of that lowerGWP HFC is no longer insufficient (or
a non-HFC substitute is identified).
EPA is also proposing that if an
application is eligible to be renewed for
ASAs for less than five years, the
application will not be reviewed for
eligibility for ASAs ahead of the next
five-year renewal period. The direction
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in the statute under AIM subsection
(e)(4)(B)(v) is to review each
‘‘application receiving an allocation of
allowances under clause (i) or (iv) . . .
not less frequently than once every 5
years,’’ and, if the criteria are met, EPA
shall renew the application ‘‘for
renewable periods of not more than 5
years.’’ EPA interprets this language,
coupled with the lack of language in the
statute directing EPA to do another
review of an application that is no
longer eligible for allowances at the end
of its renewal period, as direction that
EPA is not required to re-review this
application for eligibility for ASAs
ahead of the next five-year period.
Congress’s direction to undertake a
renewal is specific to applications
receiving ASAs under 42 U.S.C.
7675(e)(4)(B)(i) and (iv). If an
application is renewed for only two of
five years at this stage, when the next
renewal period arises, it would not be
receiving ASAs under 42 U.S.C.
7675(e)(4)(B)(i) or (iv). Therefore, EPA is
proposing that the best interpretation of
the AIM Act language is that once EPA
determines that an application is no
longer eligible for ASAs, EPA would not
re-review that application at any future
time. If an application is determined to
no longer be eligible for ASAs and an
entity is interested in being considered
for eligibility for ASAs again, the entity
would need to petition the Agency to be
evaluated for eligibility, and the Agency
would then undertake the relevant
petition review process; see Section VI
of this preamble for further discussion
of the petition process requirements.
V. Review of the Six Applications
Listed in the AIM Act
EPA reviewed the six applications
listed in AIM Act subsection
(e)(4)(B)(iv)(I)—propellant in MDIs;
defense sprays; SCPPU foam for marine
use and trailer use; the etching of
semiconductor material or wafers and
the cleaning of CVD chambers within
the semiconductor manufacturing
sector; MCMEU; and onboard aerospace
fire suppression—as required under 42
U.S.C. (e)(4)(B)(v)(I). Pursuant to that
review, in this rulemaking EPA is
proposing and seeking comment on
whether the criteria for renewal
described in Section IV of this preamble
are met for any part, or the entirety, of
the 2026–2030 time period. This section
begins with an overview of total
projected U.S. HFC consumption and
then proceeds into EPA’s assessment of
the criteria for each application and
proposed decision regarding whether to
renew each application’s eligibility to
receive ASAs. EPA provides additional
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information in the TSD available in the
docket for this rulemaking.
A. Overview of Total U.S. HFC
Consumption
This section contains a summary of
total projected U.S. HFC consumption.
We assess specific HFC supply
considerations on an application-byapplication basis below. EPA provides
additional information regarding this
analysis in the TSD.
The global and domestic HFC markets
have been rapidly changing since
agreement to the Kigali Amendment to
the Montreal Protocol in 2016.6 The
domestic HFC market has been further
changing since the passage of the AIM
Act in 2020 and the subsequent
promulgation of domestic regulations.
In 2021, EPA promulgated regulations to
implement the required phasedown of
HFC production and consumption in
the United States. Additional
regulations coming into effect, as early
as January 1, 2025, will also further alter
this overall market and impact demand
for certain HFCs. EPA anticipates the
market will be dynamic as it responds
to these additional regulations and
continues adapting to the global
phasedown of HFCs.
In the addendum to the HFC
Phasedown Regulatory Impact Analysis
(RIA) updated for the 2023 Technology
Transitions Rule (88 FR 73098, October
24, 2023), EPA modeled total HFC
consumption to be significantly lower
than the limit established by the
statutory phasedown cap for all years of
the phasedown, assuming compliance
with the restrictions. The 2023
Technology Transitions Rule
established subsector-level GWP limits
and restrictions on the use of certain
regulated substances. These
requirements take effect as early as
January 1, 2025, and as late as January
1, 2028. While some subsectors already
use either HFCs that are below the GWP
limit or non-HFC substitutes, other
subsectors will need to transition away
from their currently used HFC to
comply with these regulations. In
addition, the proposed rulemaking
‘‘Phasedown of Hydrofluorocarbons:
Management of Certain
Hydrofluorocarbons and Substitutes
Under Subsection (h) of the American
Innovation and Manufacturing Act of
2020’’ (88 FR 72216, October 19, 2023)
(hereafter ‘‘Emissions Reduction and
Reclamation Rule’’) has proposed
requirements that reclaimed and
recycled HFCs be used for certain
equipment in the refrigeration, air6 The United States ratified the Kigali
Amendment in October 2022.
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conditioning, and heat pump sector and
fire suppression sector (onboard
aerospace fire suppression, as an
application eligible for ASAs, is
currently exempt) as early as early as
January 1, 2028. If finalized as
proposed, these requirements are also
expected to limit use of virgin HFCs for
specific activities (e.g., servicing for
certain refrigeration and air
conditioning subsectors).7 In general,
there is uncertainty associated with
these estimates, as they are based on
expected industry transitions in
response to AIM Act rulemakings and
predicted market dynamics. If HFC
consumption is lower than the amount
allowed under the AIM Act in a given
year, the result may be that there are
more allowances than are needed to
meet market demand in that year.8 If
demand for HFCs is lower than the cap,
it is possible that general pool
consumption and production
allowances, which are currently used to
produce or import HFCs for entities that
do not hold allowances and entities that
use HFCs in an application-specific use,
would be available to allow for the
production or import of HFCs for use by
entities that historically have relied
upon ASAs. While current ASA holders
can access material produced using
general pool allowances or purchase
HFCs on the open market, if demand by
non-ASA entities is lower than the cap,
it is possible that the ‘‘leftover’’
allowances could be used to supply
ASA holders and therefore decrease the
need for ASAs. It is also possible that all
allowances are used, and the HFCs that
are not sold in that year are stockpiled
in anticipation of future needs.
The Agency cannot fully predict shifts
in chemical production, domestically
and internationally, that may occur. As
the HFC phasedown progresses, EPA
anticipates suppliers may focus their
business on supplying lower-GWP
HFCs, since production and
consumption of these lower-GWP HFCs
requires the expenditure of fewer
allowances for the same volume of
7 See Emissions Reduction and Reclamation Rule
(88 FR 72216, 72292, October 19, 2023).
8 The actions taken pursuant to subsection (h) and
(i) of the AIM Act did not propose to and did not
accelerate the HFC phasedown. The RIAs associated
with those actions did not analyze an acceleration
of the HFC phasedown. Rather, HFCs will continue
to be available consistent with the phasedown
codified at 40 CFR part 84, subpart A, and this
action does not propose to change that phasedown
schedule. Even if the requirements finalized
pursuant to subsections (h) and (i) in effect reduce
the production or consumption of HFCs used in
particular sectors or subsectors faster than the
scheduled reductions under the AIM Act, that does
not make those rules an acceleration under
subsection (f).
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substance.9 At the same time, sectors
that are not yet ready to transition and
are not covered by the 2023 Technology
Transitions Rule (88 FR 73098, October
24, 2023) may continue to use higherGWP HFCs and could grow in size.
EPA also does not yet have data on
how the market is reacting to the 2024
stepdown in HFC allowances (from 90
percent of the HFC consumption
baseline to 60 percent of baseline); at
the time of this proposal the market is
only a few months into adjusting to the
2024 HFC stepdown, and EPA has
received only one set of quarterly
reports. Among other things, data on
market reactions could inform how the
market will react to the next large
stepdown in 2029 (from 60 percent of
baseline to 30 percent of baseline). For
example, the decrease in available
consumption allowances could
encourage users of HFCs to transition
faster than projected. However, given
the significant amount of HFCs in
inventory at the end of 2022, the
transition away from HFCs could also be
slower than projected. Though it seems
likely that demand could be below the
cap for the 2025–2028 period based on
existing regulations, it is uncertain if
2029 (the fourth year of the five-year
renewal period) will see similar space
between consumption and allowed
consumption under the cap. EPA also
notes the 2024 stepdown in permissible
production and consumption is unique
given its scale and that it is occurring
early in the overall AIM Act
implementation. There will be
significantly more information regarding
the state of the HFC market after the
January 1, 2024, stepdown at the time
EPA is finalizing this proposal, and EPA
intends to analyze available data to
inform its decisions regarding whether
supply of individual HFCs is
insufficient to accommodate the
individual applications.
In addition, there are also other
constraints on supply of specific HFCs
used in the six applications that EPA is
taking into consideration (e.g., purity
specifications required by Federal
standards and regulations and limited
number of producers), as explained in
more detail in Sections V.B through
V.G. of this preamble. Supply chain
dynamics for each of the six
9 In the Allocation Framework Rule, EPA
established a system whereby allowances are
measured on an EV equivalent basis. 86 FR at
55142. To determine the total number of allowances
needed, producers and importers multiply the
quantity of the HFC they seek to produce or import
by its EV. For example, an importer would need to
expend 143 consumption allowances to import 100
kilograms (kg) of HFC–134a. Given the variation in
EVs, one would need to expend 5.3 allowances to
import 100 kg of HFC–152a.
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applications could affect whether
general pool allowances would be able
to be used to provide HFCs for each
application.
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B. Propellants in Metered Dose Inhalers
EPA has been allocating ASAs for
regulated substances used for
propellants in MDIs in accordance with
subsection (e)(4)(B)(iv)(I)(ff) of the AIM
Act. In the Allocation Framework Rule,
EPA defined a ‘‘metered dose inhaler’’
as ‘‘a handheld pressurized inhalation
system that delivers small, precisely
measured therapeutic doses of
medication directly to the airways of a
patient. MDIs treat health conditions
such as asthma and chronic obstructive
pulmonary disease and are approved for
such use by the U.S. Food and Drug
Administration (FDA)’’ (40 CFR 84.3).
Patients using MDIs to treat pulmonary
conditions work closely with their
healthcare provider to identify the right
treatment for their condition.
Pharmaceutical grade HFC–227ea and
HFC–134a, purified from technical
grade HFC–227ea and HFC–134a,
respectively, are both used in MDIs as
a propellant.
EPA is proposing to determine that no
safe or technically achievable substitute
will be available for propellants in MDIs
and that supply of the regulated
substance that manufacturers and users
are capable of securing from chemical
manufacturers is insufficient to
accommodate this application through
calendar year 2030. Therefore, EPA
proposes to renew the eligibility of
entities using regulated substances for
propellants in MDIs to receive ASAs for
the five-year period of calendar years
2026 through 2030.
1. Availability of Safe and Technically
Achievable Substitutes
EPA has not identified substitutes that
it would propose to deem safe and
technically achievable that are available
for propellants in the metered-dose
inhalers application at this time. In
assessing the availability of substitutes
for MDIs, EPA reviewed information
from sources such as the FDA, the EPA
SNAP Program, the TEAP’s Medical and
Chemicals Technical Options
Committee (MCTOC), industry,
scientific journal articles, and more,
which is described in greater detail in
the TSD included in the docket for this
proposed action. After reviewing
relevant information and analyses, EPA
is aware of two potential replacements
for HFC–134a and HFC–227ea as
propellants in MDIs, specifically HFO–
1234ze(E) and HFC–152a.
MDIs, including those containing an
alternative propellant other than HFC–
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134a or HFC–227ea, are subject to the
approval requirements under section
505 of the Federal Food, Drug and
Cosmetic Act. The process to develop an
MDI with a new propellant is complex
and will take time. A sponsor (i.e., MDI
manufacturer) will need to reformulate
the MDI product to use the new
alternative propellant and conduct a
development program to obtain data,
including clinical data, with the new
MDI product. If the development
program is successful, a sponsor will
then need to submit an application to
the FDA for approval; the review
timeline for a new drug application is
10 to 12 months. The overall process to
develop an MDI product containing a
new alternative propellant is expected
to take years.
EPA regularly consulted with the FDA
throughout development of this
proposed rule, and the reformulation of
the majority of MDIs with an alternative
propellant may extend beyond the end
of the renewal period of 2030. EPA is
aware that a few MDI manufacturers
have begun the development process,
some of whom are expecting to soon
begin Phase 3 trials and FDA has stated
that it is possible that they may receive
new drug applications for a small
number of MDI products with
alternative propellants by 2030.
However, these new drug applications
will need to undergo FDA review. For
new drug applications that receive FDA
approval, the commercialization plans
for new MDIs are unknown but is
anticipated to take additional time.
Unlike for some of the other uses
receiving ASAs where
commercialization of substitutes across
the entire application after those
products are first available on the
market may take a few years, for MDIs,
EPA anticipates that it will take many
years before alternatives are available
across the application. That is, it will
take time for reformulation, approval,
and commercialization to occur for each
of the individual MDI products used to
treat pulmonary disease. For example,
manufacturers of generic MDIs may face
delay in transitioning to alternative
propellants, as generic drug products
must be shown to be a duplicate of, and
bioequivalent to, a previously approved
drug product and rely on FDA’s finding
that the previously approved product is
safe and effective. Applicants request
approval for generic drug products,
including MDIs, in Abbreviated New
Drug Applications (ANDAs). FDA
provides its recommendations for
establishing bioequivalence in its
product-specific guidances, which for
orally inhaled products like MDIs, have
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generally included some combination of
in vitro and in vivo studies, along with
recommendations related to the
formulation and device. FDA committed
to review 90% of standard original
ANDAs within 10 months from the date
of submission, but often multiple review
cycles are necessitated by application
quality. This review time can be
extended if a site/facility is not ready for
inspection. The timing of ANDA
approval also depends on, among other
things, the patent and exclusivity
protections for the previously approved
product.
According to the MCTOC 2022
Assessment Report, the transition from
HFC–134a and HFC–227ea to HFC–152a
and HFO–1234ze(E) in MDIs is expected
to begin in non-Article 5 countries 10 in
2025 and continue through at least
2032, and no other feasible, lower-GWP
MDI propellants have been identified in
the United States and abroad.11 HFO–
1234ze(E) and HFC–152a, along with
other aerosol propellants, are listed as
acceptable by EPA’s SNAP Program and
are commercially available and
currently used in commercial and/or
technical aerosol products.
Furthermore, they also have most of the
requisite physical properties to function
as a propellant in MDIs with
significantly lower GWPs than the
current HFCs in use; however, neither
propellant has significant use in
pharmaceuticals today and will require
extensive clinical research and FDA
approval before they could replace the
current HFCs.
In light of the above analysis, it is
EPA’s assessment that there is no
information before the Agency at the
time of this proposal to suggest that
there would be a safe and technically
achievable substitute available prior to
the next five-year review.
2. Supply
As previously mentioned,
pharmaceutical-grade HFC–134a and
HFC–227ea (also known as HFA–134a
and HFA–227ea) are currently used as
propellants in MDIs.
As part of the manufacturing process
for MDIs, technical grade HFC–134a and
HFC–227ea are purified into
pharmaceutical-grade HFC–134a and
HFC–227ea. Documents the FDA
requires as part of the drug approval
process must specify the facility
manufacturing the HFC propellant. The
supply of pharmaceutical-grade HFC–
10 Non-Article 5 countries are defined as
developed countries under the Montreal Protocol.
For a list of Article 5 and non-Article 5 countries
see https://ozone.unep.org/classification-parties.
11 See https://ozone.unep.org/system/files/
documents/MCTOC-Assessment-Report-2022.pdf.
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134a comes from technical grade HFC–
134a that is produced at a limited
number of production facilities in other
countries, including a single plant in the
United States, and then purified at a
single facility in the United Kingdom
and reimported to the United States for
consumption in MDIs. In its analysis of
other applications, EPA has noted that
HFC–134a is the most widely available
HFC. However, this fact does not equate
to a sizeable supply for the MDI
application because MDI manufacturers
are not easily able to switch suppliers of
pharmaceutical-grade HFCs. Unlike
other applications, where EPA has
discussed the diverse number of
chemical suppliers for HFC–134a
globally, in this instance the options are
constrained.
As components of drug products, the
use of HFCs in MDIs are subject to
certain FDA requirements. FDA’s
Current Good Manufacturing Practice
(CGMP) requirements under the statute
(21 U.S.C. 351(a)) apply to drugs,
including their components (21 U.S.C.
321(g)(1)), and include requirements
related to methods, facilities, controls,
manufacturing, processing, packing, and
holding to assure that drugs meet
requirements for safety, identity,
strength, and quality and purity. FDA
has also promulgated CGMP regulations
for finished pharmaceuticals in 21 CFR
210 and 211. These CGMP regulations
also contain requirements for
manufacturers in their handling,
control, storage, and testing of
components used in manufacture of
drug products. HFC purification occurs
in dedicated facilities that are subject to
FDA CGMP requirements for drugs and
devices, as well as other international
quality standards, as MDI manufacturers
may serve markets in addition to that of
the United States. If an MDI
manufacturer wanted to change their
supplier of pharmaceutical grade HFC,
this would trigger FDA review. MDI
manufacturers who change suppliers of
pharmaceutical grade HFCs would need
to provide data to ensure the safety and
quality of the new propellant and
submit the data to the FDA for review
and approval. This data may include
pharmacology/toxicology data, product
quality data of the new propellant
source, and a comparison of the current
and proposed new propellant sources,
and quality data that demonstrates the
drug made with the new propellant
meets all applicable quality
requirements. Depending upon the
comparability of the HFA sources,
additional data may be requested by the
FDA (21 CFR 314.70).
There are three suppliers of
pharmaceutical-grade HFC–227ea for
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use in the United States. One of the
suppliers is a producer that purifies the
technical grade HFC–227ea at one of
their facilities in the United States. The
second produces and purifies the
pharmaceutical-grade HFC–227ea at
their facility in Germany, which is then
imported by that producer for
distribution to domestic MDI
manufacturers. The third supplies
pharmaceutical-grade HFC–227ea to the
United States from their facility in the
United Kingdom. At least two of these
facilities also supply pharmaceuticalgrade HFC–227ea globally for MDI
manufacture. Producers of
pharmaceutical-grade HFC–227ea must
also comply with FDA requirements as
described above, which limits their
ability to switch to other suppliers of
HFC–227ea.
3. What is EPA proposing regarding
eligibility for application-specific
allowances?
EPA is proposing to renew the
eligibility of entities using regulated
substances for propellants in MDIs to
receive ASAs for the five-year period of
calendar years 2026 through 2030. EPA
is proposing to determine ‘‘that the
requirements described in subclauses (I)
and (II) of clause (i) are met’’ in
accordance with the requirements of 42
U.S.C. 7675(e)(4)(B)(v)(II). Specifically,
for the reasons outlined earlier in this
section, EPA is proposing to determine
that no safe or technically achievable
substitute will be available for
propellants in MDIs and that supply of
the regulated substance that
manufacturers and users are capable of
securing from chemical manufacturers
is insufficient to accommodate
propellants in MDIs through calendar
year 2030. EPA is proposing to
determine that the supply of both HFC–
134a and HFC–227ea is insufficient to
accommodate the propellants in MDIs
application.
C. Defense Sprays
Per subsection (e)(4)(B)(iv)(I)(bb) of
the AIM Act, EPA has been allocating
ASAs for defense sprays since 2021.
EPA defined a ‘‘defense spray’’ as ‘‘an
aerosol-based spray used for selfdefense, including pepper spray and
animal sprays, and containing the
irritant capsaicin and related
capsaicinoids (derived from oleoresin
capsicum), an emulsifier, and an aerosol
propellant,’’ (40 CFR 84.3). Within this
application, there are four primary uses:
bear sprays, dog sprays, personal
defense sprays, and law enforcement
sprays. The defense sprays chapter in
the TSD contains more details on these
product categories. HFC–134a is the
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primary propellant currently used for
the majority of defense sprays and is the
only HFC for which EPA has allocated
allowances since 2022. After analyzing
information relevant to the statutory
criteria, as outlined in this section and
the TSD, EPA is proposing two
options—to not renew the eligibility for
entities in this application to receive
ASAs or to renew for two years. EPA is
also taking comment on the possibility
of renewing for a full five-year period.
1. Availability of Safe and Technically
Achievable Substitutes
There has already been
commercialization of alternatives to
HFC–134a as a propellant in some
defense spray uses, and transition is
underway for other parts of the
application. Thus, while many defense
sprays currently use HFC–134a as a
propellant, EPA is aware of entities that
have already successfully
commercialized alternative propellants,
including non-HFCs, in some of their
products. The availability of safe and
technically achievable substitutes for
this application will continue to
expand, and EPA will take any
additional information into account in
the final rulemaking.
All dog defense sprays
commercialized in the United States
and registered with EPA under FIFRA
use a non-HFC propellant and have
never used an HFC propellant; from
company communications, EPA is
aware that at least three dog sprays
utilize compressed nitrogen gas. In
addition, EPA is aware from company
communications that two bear sprays
using propellants other than HFC–134a
are available domestically, one using a
non-HFC, HFO–1234ze(E), and one
utilizing a lower-GWP HFC, HFC–152a.
Both products have been available for
multiple years. In addition, there is one
bear spray that is manufactured
domestically, but sold into the Canadian
market, that also utilizes HFO–
1234ze(E). EPA is also aware of at least
one defense spray used on humans
available in other countries, but
manufactured in the United States, that
uses HFO–1234ze(E).
The commercialization of defense
sprays with alternative propellants
suggests that there are safe and
technically achievable substitutes to
HFC–134a available within this
application, but it is not clear that they
are immediately available for the entire
application. In other words, there are
multiple different uses within this
application, and many of the uses have
similar technical requirements (e.g.,
large spray volume and distance) and
safety considerations (e.g.,
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flammability). Thus, EPA’s assessment
is that while there are certain
differences amongst the uses, generally
a propellant commercialized for one use
should be safe and technically
achievable for another use as explained
in more detail below. It is EPA’s
understanding that defense sprays have
industry-set technical requirements that
differentiate them from other aerosols,
but that outside of FIFRA requirements
for bear sprays,12 defense sprays do not
need to be certified or comply with
Federal regulatory standards to be sold
in the United States. EPA is aware of
some voluntary standards for law
enforcement sprays, explained in more
detail in the defense sprays chapter of
the TSD, that specify performance
requirements and test methods for the
evaluation of these sprays. EPA’s
understanding is that defense sprays do
not need to be certified under this
standard to be sold into the law
enforcement market.
While some entities have successfully
commercialized alternative propellants,
there are steps other entities will need
to undertake in order to use these
alternatives, such as their own research
and development process, approval
under FIFRA for bear sprays, and
potentially changes to manufacturing
facilities. For example, EPA is aware of
at least two defense spray manufacturers
that had made significant investments to
potentially transition to a non-HFC as a
propellant that did not pursue the
transition due to performance
concerns.13 The multiple defense spray
products commercialized using
alternative propellants suggests that past
challenges can be overcome, though
EPA acknowledges that
commercialization of alternative
12 Defense sprays used to deter bears, dogs, and
other animals are considered pesticides under
FIFRA, so must comply with related requirements,
including approval for the inert ingredients (e.g.,
the propellant) used in the product. In addition to
HFC–134a, both HFC–152a and HFO–1234ze(E) are
approved for use as inert ingredients for non-food
pesticidal use (e.g., animal sprays). Transitioning a
product to another approved propellant is a
relatively simple process that only requires
submission of product performance data (i.e., no
tests related to safety, impacts on human health,
etc.), and approval can occur in five to seven
months. This action would be a Pesticide
Registration Improvement Act B680 or B681. See
https://www.epa.gov/pria-fees/pria-fee-categorytable-biopesticides-and-pollution-preventiondivision-bppd-amendments for more information.
13 Written testimony submitted for the record
from Safariland and Security Equipment
Corporation for the U.S. Senate Committee on
Environment and Public Works hearing on the AIM
Act. https://www.epw.senate.gov/public/index.cfm/
2020/3/s-2754-american-innovation-andmanufacturing-act-of-2019-written-testimony-andquestions-for-the-record.
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propellants across this entire
application may take a few years.
Outside of what has already been
commercialized by some defense spray
companies, EPA is not aware of any
other substances under consideration as
safe and technically achievable
substitutes for this application. Multiple
propellants, including HFC–152a, HFO–
1234ze(E), and hydrocarbons, have been
listed as acceptable under SNAP and
identified as technically and
economically feasible alternatives for
propellants in aerosols by the TEAP’s
MCTOC. However, there are additional
technical demands in the defense spray
application that provide unique
challenges as compared to other types of
aerosol applications. For example, given
their use for personal protection and
crowd control, defense sprays need to
have a larger spray cloud and longer
spray distance, and stakeholders have
noted that law enforcement’s use of
defense sprays alongside stun guns (e.g.,
Tasers) poses specific concerns around
flammability. Therefore, alternatives
identified as acceptable for aerosols,
such as hydrocarbons, may not be
available for all defense spray uses.
SNAP lists substitutes for aerosols at the
end use level, not the application level
(e.g., the Agency has listed substitutes
for aerosol propellants, which would
allow for those substitutes in defense
sprays), and TEAP’s MCTOC has not
specifically discussed or evaluated
defense sprays as an individual use.
More information about the specialized
nature of defense sprays can be found in
the defense sprays chapter of the TSD.
To inform determinations in this
rulemaking, EPA invites comment on
whether the alternatives
commercialized for some defense spray
uses are not available for the entire
application, including any supporting
data and information; EPA is
particularly interested in data regarding
flammability of alternative propellants
at the concentrations found in defense
sprays and testing results demonstrating
safety risks in the situations where
defense sprays are typically utilized.
2. Supply
The majority of defense sprays
currently use HFC–134a as their
propellant. HFC–134a is the most
widely produced HFC globally and is
produced in substantial quantities in
multiple countries, including the United
States. In 2022, domestic production of
HFC–134a was 61,377 metric tons (MT),
making up 46 percent of U.S. HFC
production on a mass basis; this
production amount is also nearly double
the domestic production amount of the
HFC produced in the second highest
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quantity. EPA is aware that one
domestic producer of HFC–134a is
transitioning its facility to produce a
different chemical.14 In addition, there
are multiple entities that import HFC–
134a. In 2022, 7,363.1 MT of HFC–134a
were imported into the United States.
Overall, HFC–134a made up
approximately 32 percent of total U.S.
HFC consumption 15 in 2022 on a mass
basis. This application has very limited
demand for HFC–134a in comparison to
U.S. consumption of HFC–134a;
allocated ASAs for this application in
2024 are equivalent to 0.1 percent of
calculated domestic consumption of
HFC–134a in 2022, on a metric tons of
exchange value equivalent (MTEVe)
basis. In addition, at the end of 2022,
suppliers held 51,902.9 MT of HFC–
134a in domestic inventory, which is
equivalent to about 101 percent of
calculated consumption of HFC–134a in
2022, and 1,036.8 MT of HFC–134a was
reclaimed; the entities both holding this
material in inventory and reclaiming
these HFCs are broader than EPA’s
interpretation of chemical
manufacturers (see Section IV.B for
more information), so not all of this
HFC–134a may be considered available
supply.
However, as described in more detail
in Section V.A of this preamble, the
overall market for HFCs and for HFC–
134a in particular is likely to continue
changing in light of the AIM Act and
other restrictions. There is uncertainty
regarding how the market is reacting to
the stepdown of the level of permissible
production and consumption of HFCs
that took effect on January 1, 2024, and
EPA anticipates further market changes
as a result of the stepdown taking effect
on January 1, 2029. However, global
production capacity is expected to
remain substantial over the coming
years, given production will continue in
countries on later HFC phasedown
schedules, and EPA expects continued
domestic and global demand for HFC–
134a. EPA will analyze any available
information on market adjustment to the
January 1, 2024, stepdown and
regulations effective January 1, 2025, in
finalizing this rulemaking.
In considering supply of the regulated
substance currently used by this
application, EPA also notes that the
Agency is unaware of any reason why
this application cannot use recovered
and reprocessed HFCs. For example,
EPA is not aware of any specific purity
14 See https://www.arkema.com/usa/en/media/
news/global/corporate/2022/20221006-two-majorsteps-develop-supply-forane-1233zd/.
15 Consumption = (Total Production + Production
for Feedstock + Imports [Virgin and
Used])¥(Exports [Virgin and Used] + Destruction).
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requirements for HFCs used in this
application. As a result, the supply of
recovered and reprocessed HFCs that
can be secured from chemical
manufacturers is relevant when
assessing whether the supply of HFC–
134a is insufficient to accommodate this
application. The likeliest source of these
reprocessed HFCs for defense sprays
would be reclaimed refrigerants, which
must meet specific purity
requirements.16 Since there are no
Federal purity requirements or industry
purity standards for HFCs used in
aerosols, the purity of reclaimed HFCs
is likely the same or higher than the
virgin HFCs used in this application.
The supply of reclaimed HFC–134a in
the United States is substantial and
increases the supply of HFC–134a
available to this application. However,
as is true in many other parts of EPA’s
supply analysis, there is uncertainty
regarding the overall supply and
demand for reclaimed HFCs.
There is additional uncertainty
around the supply and demand for
HFC–134a as a result of the 2023
Technology Transitions Rule (88 FR
73098, October 24, 2023). GWP
restrictions under the 2023 Technology
Transitions Rule begin taking effect
January 1, 2025, with the latest
restriction taking effect on January 1,
2028. Overall demand for HFC–134a
could fall since all subsectors subject to
Technology Transitions restrictions will
not be permitted to use neat HFC–134a,
as its GWP of 1,430 is greater than the
highest GWP limit (i.e., 700). However,
many subsectors subject to Technology
Transition restrictions already use
chemicals that fall below the GWP
restriction levels, and where this is the
case EPA does not anticipate any change
in demand of HFC–134a. Additionally,
some sectors may use blends with HFC–
134a as a component where the GWP is
below the applicable limit. Moreover,
HFC–134a will likely continue to be
16 In alignment with the definition in 42 U.S.C.
7675(b)(9), EPA defined reclaim as ‘‘the
reprocessing of regulated substances to all of the
specifications in appendix A to 40 CFR part 82,
subpart F (based on Air-Conditioning, Heating, and
Refrigeration Institute (AHRI) Standard 700–2016)
that are applicable to that regulated substance and
to verify that the regulated substance meets these
specifications using the analytical methodology
prescribed in section 5 of appendix A to 40 CFR
part 82, subpart F’’ (40 CFR 84.3). Thus, HFC–134a
refrigerant that is reclaimed and used by a different
user than the one recovering the refrigerant must
meet the purity requirements of AHRI 700,
Standard for Specifications for Refrigerants. That
standard, among other things, requires that
reclaimed HFC–134a must be visibly clean (that is,
no visible solids or particulate), no more than 1.5
percent by volume of air in the vapor phase, no
more than 10 parts per million of water by weight,
and no more than 0.5 percent by weight of other
volatile impurities.
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used in other applications not subject to
these restrictions (e.g., heavy-duty
trucks), as well as for servicing existing
equipment (e.g., light-duty motor
vehicle air conditioning). HFC suppliers
may also shift their production and
import practices, such that supply of
HFC–134a changes. EPA intends to
review available information on market
shifts that occur when the first set of
Technology Transition restrictions take
effect on January 1, 2025, and where
possible will incorporate any relevant
information into the analysis
underpinning finalization of this
rulemaking. Based on this additional
information, at finalization of this
proposed rule, EPA may be in a position
to determine that the supply of HFC–
134a is not insufficient to accommodate
this application once all of the
Technology Transition restrictions take
effect as of January 1, 2028, if not earlier
(i.e., as early as January 1, 2026).
EPA also intends to finalize a
rulemaking under subsection (h) of the
AIM Act, the Emissions Reduction and
Reclamation Rule (88 FR 72216, October
19, 2023), in the summer of 2024. EPA
proposed a number of requirements
including those concerning use of
reclaimed HFCs for certain activities. In
addition, EPA intends to finalize a
rulemaking, ‘‘Trichloroethylene (TCE);
Regulation Under the Toxic Substances
Control Act (TSCA)’’ (88 FR 74712,
October 31, 2023), later this year; this
rulemaking has proposed to ban the use
of TCE due to unreasonable risk of
injury to human health. If finalized as
proposed, this would prohibit TCE from
being used as a feedstock to
manufacture HFC–134a within eight
and a half years from when that rule is
finalized. While this could end the
production of HFC–134a in the United
States,17 it is unclear how this change
would affect overall supply of HFC–
134a, as there is currently still global
supply of HFC–134a that could be
imported into the United States. EPA
anticipates being able to consider the
projected effects of these other rules
prior to finalizing this rulemaking.
Entities do not need to seek or receive
ASAs in order to use HFC–134a in
defense sprays. Further, entities do not
have to expend an allowance to
purchase HFC–134a from another entity
that has imported or produced the
regulated substance. EPA notes that of
the six defense spray entities that have
received ASAs at some point for
calendar years 2022, 2023, and 2024,
17 Though there are other pathways to produce
HFC–134a, the pathway using TCE is the primary
production pathway in the United States, and it is
EPA’s understanding that it is complex to change
production pathways.
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three did not receive ASAs in at least
one of those years. EPA is also aware of
at least two entities selling bear sprays
that use HFC–134a that have never
applied for, and therefore never
received, ASAs. This suggests that at
least those two entities were able to
acquire HFC–134a on the open market
without having ASAs. These facts could
suggest that ASAs may not be
imperative for entities in this
application to access HFC–134a.
In sum, HFC–134a is currently more
widely available than other HFCs, and
defense sprays’ need for HFC–134a is
small compared to the overall demand
for HFC–134a across a range of sectors.
At the same time, there is inherent
uncertainty in the HFC market due to
future stepdowns and new regulations
coming into effect. Further information
regarding EPA’s assessment of the
supply of HFC–134a related to the needs
of the defense sprays application can be
found in the defense sprays chapter of
the TSD.
EPA is also considering the supply of
HFC–152a, as it is used in at least one
defense spray product, as noted above.
HFC–152a is produced in substantial
quantities, though the current domestic
production of HFC–152a is about half
that of HFC–134a, on a mass basis.18 In
2022, domestic production of HFC–152a
was 29,654.9 MT, about 22 percent of
U.S. HFC production by mass. There is
currently only one U.S. HFC–152a
production facility, and that producer
has announced plans to increase
production by approximately 20 percent
by mid-2024.19 At the time of this
proposal, the facility expansion is not
yet complete, so EPA cannot say with
certainty when it will be available.
However, there is also substantial global
production of HFC–152a, which also
supplies the U.S. market. Multiple
entities imported HFC–152a in 2022,
importing a total of 5,810.1 MT. Overall,
HFC–152a made up approximately 20
percent of total U.S. HFC consumption
in 2022 on a mass basis. In addition, at
the end of 2022, suppliers held 5,076.3
MT of HFC–152a in domestic inventory,
which is equivalent to about 16 percent
of calculated consumption of HFC–152a
in 2022. The company that has
commercialized the bear spray using
HFC–152a has never received
allowances for HFC–152a, which
suggests that at least this entity is able
18 See https://www.epa.gov/climate-hfcsreduction/hfc-data-hub/expanded-hfc-data.
19 See https://www.chemours.com/en/newsmedia-center/all-news/press-releases/2023/
chemours-announces-capacity-increase-of-hfc152a-providing-reliable-domestic-supply-of-lowglobal-wa.
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to acquire HFC–152a on the open
market without having ASAs.
In addition, HFC–152a has one of the
lowest EVs relative to other regulated
HFCs, so fewer allowances are needed
to import or produce HFC–152a in
comparison to the same volume of
higher-EV HFCs. For example, an
importer would need to expend 143
consumption allowances to import 100
kg of HFC–134a compared to 12.4
allowances to import 100 kg of HFC–
152a—a greater than 90% reduction.
This means that, from a strictly
allowance-focused view, HFC–152a will
be easier to acquire than most other
HFCs as the phasedown progresses and
the number of HFC allowances is
reduced. Allowances allocated to an end
user may therefore not be necessary to
secure production or import of HFC–
152a.
Future projections suggest that there
could be increased demand for HFC–
152a, although there is inherent
uncertainty with how industry will
respond to the phasedown of HFCs at
this early stage. HFC–152a has a GWP
that is below all the GWP limits for
sectors and subsectors subject to the
2023 Technology Transitions Rule (88
FR 73098, October 24, 2023). The 2023
Technology Transitions Rule identified
HFC–152a as an available or potentially
available substitute for all 13 foam
subsectors, aerosol propellants, motor
vehicle air conditioning, and household
refrigerators and freezers.20 However,
there are also multiple other acceptable
alternatives, including non-HFCs, and,
for subsectors where a transition to
another substitute has already occurred
(e.g., motor vehicle air conditioning,
household refrigerators and freezers), it
is highly unlikely that a new transition
to HFC–152a would be considered. For
subsectors where HFC–152a neat or in
blends is likely under consideration, it
is not yet known if there will be any
significant shift toward use of HFC–
152a, particularly as many relevant
subsectors have begun to move out of
HFCs entirely. For example, the MCTOC
2022 Assessment report notes that a
significant proportion of aerosols
already use non-HFCs as propellants.
20 See 2023 Technology Transitions Rule (88 FR
73098, October 24, 2023) TSD ‘‘American
Innovation and Manufacturing Act of 2020—
Subsection (i)(4) Factors for Determination: List of
Substitutes.’’ This list is not exhaustive, so it is
possible HFC–152a is an available alternative for
other subsectors. In addition, EPA did not identify
information for products or equipment containing
certain substitutes, which may indicate a lack of
current commercial demands for the substitutes in
those products or equipment. However, this did not
automatically remove those substitutes from the list
of available substitutes, as commercial demands is
only one subfactor that needed to be considered
under subsection (i)(4)(B).
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Similarly, the FTOC 2022 Assessment
Report highlights that fluorocarbon use
in foams has been falling for decades,
and foams are largely expected to
continue transitioning to non-HFCs,
including hydrocarbons, HFOs, and
hydrochlorofluoroolefins (HCFOs).
Demand for HFC–152a may therefore
change in future years as subsectors
transition to alternatives from their
currently used HFC.
In sum, while there is a reasonably
large supply of HFC–152a that is
expected to increase over the coming
years relative to other HFCs, there is
uncertainty around future demand for
the reasons described above.
3. What is EPA proposing regarding
eligibility for application-specific
allowances?
Given the rapidly changing landscape
for HFC supply and EPA’s assessment of
substitute availability application-wide,
EPA is proposing two options based on
our current analysis and in anticipation
of additional available information
before this proposed rule is finalized.
Specifically, EPA is proposing to
finalize one of the following outcomes:
(1) No renewal, such that the
application will not receive ASAs or (2)
Renew eligibility for ASAs for two
years, such that ASAs are available for
calendar years 2026 and 2027.21 EPA is
also seeking comment on renewing
eligibility for the full five-year period.
As explained earlier in this proposal,
an application must meet both criteria
to be eligible to receive ASAs. For the
reasons described earlier in this section,
EPA is proposing to determine that
there is not a safe and technically
achievable substitute that is
immediately available for the entire
application, but a safe or technically
achievable substitute will be available
for the entirety of the defense spray
application by January 1, 2028. In other
words, EPA proposes to determine that
the criterion in subsection (e)(4)(B)(i)(I)
is not met for defense sprays starting
January 1, 2028. Under this proposed
determination, even if EPA received
information to determine that supply of
the currently used regulated substance
was insufficient, defense sprays would
not be eligible for renewal as of January
1, 2028, unless they have insufficient
supply of a substitute HFC, as discussed
in more detail below.
EPA is also proposing to determine
that either (1) the supply of HFC–134a
is not insufficient to accommodate this
21 The proposed amendatory text included in this
Federal Register notice shows only one of the coproposed options. This is for illustrative purposes
and should not be read as EPA favoring one coproposal over another.
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75913
application; or (2) the supply of HFC–
134a will not be insufficient to
accommodate this application as of
January 1, 2028. In other words, EPA
proposes to determine that the criterion
in subsection (e)(4)(B)(i)(I) is either: (1)
not met at all for this application for
HFC–134a, and therefore the application
would not be eligible to receive ASAs
starting January 1, 2026; or (2) not met
as of January 1, 2028, and therefore the
application would not be eligible to
receive ASAs starting January 1, 2028.
Under the first option, this means that
even if the application does not have a
safe or technically achievable substitute
available, ASAs would not be available
for defense spray manufacturers as of
January 1, 2026. For the second option,
defense sprays would not be an eligible
application for ASAs as of January 1,
2028, regardless of the availability of
substitutes.
EPA does not have sufficient
information to make a definitive
determination on whether supply of
HFC–152a is insufficient to
accommodate this application at the
time of this proposal. We are monitoring
this issue and will be seeking
information on the alternatives that
subsectors subject to Technology
Transitions restrictions transition into
and how much additional domestic
production capacity of HFC–152a comes
online in the coming year.
EPA is also taking comment on
whether defense sprays should be
eligible to receive ASAs for the full fiveyear period from 2026–2030. A full fiveyear renewal could be without
restriction or could be based on and
tailored only to the application’s need to
purchase HFC–152a. As explained
earlier, HFC–152a is used commercially
in one bear spray product, so this latter
scenario could be relevant if HFC–152a
is an available safe and technologically
achievable substitute for the entire
defense spray application by 2028.
Under this scenario, EPA would follow
an approach similar to the option
proposed for SCPPU foams for marine
and trailer uses in Section V.D.3.
EPA intends to review comments and
other relevant information received on
this proposal to further understand how
the market surrounding this application
evolves and the availability of
substitutes application-wide before EPA
finalizes this proposed rule.
Specifically, we intend to review
additional information on how the HFC
market adjusts to the 2024 stepdown,
defense sprays’ research into alternative
propellants and related trials (including
relevant data on flammability), what
alternatives consumer aerosols
transition to (as they are subject to the
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Technology Transitions restrictions
starting in 2025), and research into
alternative propellants intended to be
used in technical aerosols (which are
subject to the Technology Transitions
restrictions starting in 2028). EPA
invites submission of comment and
additional data related to these data
gaps. EPA will consider this new
information, in addition to public
comments, in making a final
determination for this application.
4. Proposed Restriction Under EPA’s
Technology Transitions Program
The 2023 Technology Transitions
Rule (88 FR 73098, October 24, 2023)
restricts the manufacture and import of
all aerosol products that use HFCs or
HFC blends that have a GWP greater
than 150. This restriction begins January
1, 2025, for all aerosols except for those
specifically listed in the final rule as
technical aerosols, which have
manufacture and import restrictions
starting January 1, 2028. The listed
technical aerosols are applications for
which EPA received sufficient
information through the comment
period or through EPA’s own analysis
indicating that additional time is
needed to transition to substitutes due
to various technical requirements, such
as non-flammability and/or a specific
vapor pressure. The list of technical
aerosols does not include defense
sprays.
The 2023 Technology Transitions
Rule exempts applications that receive
ASAs (40 CFR 84.56(a)(2)). However, as
finalized in the October 24, 2023, rule,
if an application no longer qualifies for
ASAs, the Technology Transitions
restrictions then apply.
While most aerosols are required
under the Technology Transitions
Program to meet a 150 GWP limit
starting on January 1, 2025, the EPA
provided additional time to comply
with this limit for some technical
aerosol uses. Most of the U.S. aerosol
industry subject to the January 1, 2025,
compliance date has already
transitioned to using propellants that
meet the 150 GWP limit,22 and therefore
has available substitutes for use based
on EPA’s consideration of the factors
listed in subsection (i)(4)(B) (e.g.,
technological achievability, commercial
demands, safety, consumer costs, etc.).
By contrast, the uses that received an
extension for compliance with the 150
GWP limit until January 1, 2028, 40 CFR
84.54(a)(16)(i)(A)–(O), currently use
22 See Household and Commercial Products
Association (HCPA) and National Aerosols
Association (NAA) Technology Transitions Petition
to EPA dated July 6, 2021. Available in the public
docket at EPA–HQ–OAR–2021–0289–0037.
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HFC–134a (most often as a propellant)
and have limitations that require
additional time ‘‘to reformulate, test,
and transition’’ to ensure availability of
substitutes under subsection (i)(4)(B) for
these technical uses.
EPA is proposing that defense sprays
would be considered under the
Technology Transitions Program
consistent with technical aerosols, with
the corresponding compliance deadlines
on the manufacture and import of
defense sprays using HFCs and blends
containing HFCs with a GWP of 150 or
greater beginning January 1, 2028, with
a three-year sell-through of those
products. Thus, defense sprays
manufactured or imported prior to
January 1, 2028, could continue to be
sold until January 1, 2031. As discussed
in Section V.C.1 of this preamble, while
some defense spray uses may have
substitutes available in the near term
that are technically achievable and safe,
EPA’s proposed assessment under
subsection (e)(4)(B) is that such
substitutes are not immediately
available across all defense spray uses.
In particular, the flammability or
specific vapor pressure of potential
substitute propellants present
availability concerns for some uses in
the near term. Consideration of
technological achievability and safety,
as well as other subsection (i)(4)(B)
factors, indicates that a compliance date
of January 1, 2025, for transition of all
defense spray uses is not appropriate,
but the approval of substitute
propellants as safe under SNAP and
TEAP analyses (see Section V.C.1), as
well as EPA’s assessment that many
propellant uses in this subsector have
been able to successfully transition to
substitutes, provides support for EPA’s
proposed finding that all defense sprays
will have available substitutes by
January 1, 2028. We invite comment on
whether availability of substitutes for
use in defense sprays, particularly
considering those factors enumerated
under subsection (i)(4)(B), indicates that
defense sprays could in fact meet the
existing 150 GWP limit restriction if the
application ceased being eligible for
ASAs on January 1, 2026. We note that
given the January 1, 2028, compliance
date for the transition of the remaining
aerosol sector, comments urging the
Agency to provide additional time for
compliance beyond that date will need
to provide very specific and detailed
information in support of that request,
speaking to the statute’s factors under
subsection (i)(4) and in particular the
subsection (i)(4)(B) factors.
Under the 2023 Technology
Transitions Rule, the labeling
requirements are effective at the same
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time as the manufacture and import
restrictions, which, if EPA finalizes this
action as proposed, would be January 1,
2028. Recordkeeping and reporting
provisions are effective for all sectors
and subsectors under the 2023
Technology Transitions Rule starting
January 1, 2025. EPA proposes that the
recordkeeping requirements would
apply to defense spray manufacturers
and importers beginning January 1 of
the year that use no longer qualifies for
ASAs, and the first report would be due
March 31 of the following year. For
example, if defense sprays are no longer
eligible for ASAs in 2026,
manufacturers and importers would
need to keep records as required by the
2023 Technology Transitions Rule
starting January 1, 2026, and submit
their first Technology Transitions report
to EPA by March 31, 2027, even if EPA
finalizes its proposal that the 150 GWP
limit for the manufacture and import of
defense sprays using HFCs would not
apply until January 1, 2028.
EPA requests comment on the
proposal to consider defense sprays
consistent with technical aerosols for
purposes of the Technology Transitions
Program and the restrictions that result
from such a classification, such as the
GWP limit that would take effect on
January 1, 2028, use restrictions, a threeyear sell-through window for inventory
ending January 1, 2031, and labeling
and reporting requirements.
EPA has previously determined that
available substitutes for use as aerosol
propellants include HFC–152a (GWP
124) and HFO–1234ze(E) (GWP <1) (88
FR 73098, October 24, 2023). EPA is
also interested in any supporting data
and information related to the
availability of substitutes and whether a
different timeline is more appropriate
for transitioning in this application or
for a subset of products in this
application.
D. Structural Composite Preformed
Polyurethane Foam for Marine Use and
Trailer Use
The third application to which EPA
has been allocating ASAs to since 2022
is SCPPU foam for marine and trailer
uses, in accordance with subsection
(e)(4)(B)(iv)(I)(cc) of the AIM Act. In the
Allocation Framework Rule (86 FR
55116, October 5, 2021), EPA defined
this application as ‘‘a foam blown from
polyurethane that is reinforced with
fibers and with polymer resin during the
blowing process, and is preformed into
the required shape (e.g., specific boat or
trailer design) to increase structural
strength while reducing the weight of
such structures’’ (40 CFR 84.3). SCPPU
foam is different from other types of
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polyurethane (PU) foams due to its
specialized structural properties, and it
is preformed into required shapes (e.g.,
specific boat or trailer design). HFC–
134a is the current HFC used in the
blowing process for SCPPU foam. After
analyzing information relevant to the
statutory criteria, as outlined in this
section and the TSD, EPA is proposing
a range of options—to not renew the
eligibility for entities in this application
to receive ASAs, to renew for two years,
or to renew access to ASAs for five years
with allowances determined based on
the use of a lower-GWP HFC substitute
for HFC–134a. EPA is also taking
comment on the possibility of renewing
for a full five-year period consistent
with the current allowance allocation
approach.
1. Availability of Safe and Technically
Achievable Substitutes
EPA anticipates that SCPPU foam for
marine and trailer uses’
commercialization of formulations using
alternatives to HFC–134a as blowing
agents is well underway and will evolve
significantly between issuance of this
proposed rulemaking and its
finalization. The Agency will consider
information collected from regulated
entities and other relevant sources
through the public comment period and
the current reporting requirements to
inform a final determination.
EPA is aware, from manufacturer
communications and reporting, of two
substitutes currently under
development for this application—an
HFC–152a/cyclopentane blend and an
HFO. EPA notes that SNAP has listed
both HFC–152a and cyclopentane as
acceptable for all PU foams, including
rigid PU uses in both marine flotation
and commercial refrigeration (the two
respective end uses for this application).
Based on information from the
manufacturers of SCPPU foam for
marine and trailer uses, EPA
understands that the research and
development phase for both potential
substitutes is nearing completion and
that companies are nearing a phase
where they will be able to
commercialize use of substitutes. If
commercialization occurs as companies
anticipate and as shared with EPA, the
entire application would be able to use
a substitute different from HFC–134a
before January 1, 2026. According to the
information shared with EPA, one
substitute seems close to being
commercialized for SCPPU foam for
marine use, and the other substitute
seems close to being commercialized for
SCPPU foam for trailer use. The
company that is close to
commercializing use of the HFC–152a/
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cyclopentane blend performed multiple
early trial runs with HFOs, all of which
failed to meet their needs, so the
company decided to pursue the HFC–
152a blend. On this basis, we are
proposing to determine that the HFO is
not an available substitute applicationwide for the five-year period from 2026–
2030, given additional research and
development trials are needed, as well
as the subsequent ramp up to
commercialization. EPA understands
that often different companies use
different blowing agents to produce the
same foam. At this time, it is unclear
why an HFC–152a/cyclopentane blend
cannot be used across the entirety of the
application and similarly whether at
some future date another blowing agent
(e.g., an HFO) might be used
application-wide. To inform
determinations in this rulemaking, EPA
invites comment on any potential
reasons why an HFC–152a/cyclopentane
blend might not be safe and technically
achievable for the entire application,
including any supporting data and
information, such as trial data. While
there are two different end uses in this
application, the foam used in both subapplications is the same (i.e., it is an
SCPPU foam).
Other than an HFO and an HFC–152a/
cyclopentane blend, EPA is not aware of
other safe and available alternatives at
this time. There are currently a range of
alternatives identified as acceptable by
SNAP and as technically proven by the
TEAP’s FTOC for other PU foams,
including rigid PU uses in both marine
flotation and commercial refrigeration.
Alternatives include a lower-GWP HFC
(i.e., HFC–152a), hydrocarbons, and
HFOs. However, alternatives identified
as acceptable for PU foams are not
necessarily available for SCPPU foam,
given the unique technical requirements
for this foam (e.g., specialized structural
properties). SNAP generally lists
substitutes at the sector and end use
level, not the application level (e.g., the
Agency has listed substitutes for rigid
PU foam, which would allow for those
substitutes in SCPPU foam, but it has
not evaluated the use of these
substitutes for SCPPU foam in
particular), and TEAP’s FTOC did not
specifically discuss or evaluate SCPPU
foam as an individual use in its 2022
assessment report. More information
about the specialized nature of SCPPU
foam can be found in the SCPPU foam
chapter of the TSD.
Aside from the limitations noted
above, EPA is not aware of significant
Federal regulatory restrictions on the
type of substitutes that could be
considered for this application. EPA is
also not aware of any required standards
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75915
that SCPPU foam needs to meet to be
manufactured and sold in the United
States. The SCPPU foam chapter of the
TSD contains further information on
sources consulted, and EPA invites
comment on any additional information
the Agency should consider in
analyzing substitutes for this
application.
After reviewing the available
information, including reports on
progress made by manufacturers of
SCPPU foam for marine and trailer use,
EPA has not identified a safe and
technically achievable substitute that is
available at the time of this proposal,
but anticipates that substitutes will
likely be available soon. We are
monitoring this issue and are seeking
information from the entities that use
HFCs in this application on whether
progress continues as anticipated to
inform our final determination.
2. Supply
Entities manufacturing SCPPU for
marine and trailer uses currently use an
HFC–134a formulation. As described in
more detail in Section V.C.2 of this
preamble, HFC–134a is the most widely
produced of all HFCs. There is
substantial domestic and global
production of HFC–134a. This
application’s demand for HFC–134a is
very small compared to domestic
consumption; allocated ASAs for this
application in 2024 are equivalent to 0.1
percent of calculated domestic
consumption of HFC–134a in 2022, on
an MTEVe basis. However, as noted
earlier, the global and domestic HFC
markets are continuing to adapt to
regulations promulgated pursuant to the
AIM Act, including the implementation
of the phasedown of production and
consumption of HFCs, and other
authorities. EPA anticipates this market
will continue to change, and EPA will
analyze additional information as it
becomes available ahead of finalizing
this rulemaking. Such additional
information will include whether there
were immediate market shifts as a result
of both the stepdown of the level of
permissible production and
consumption of HFCs that took effect on
January 1, 2024, and regulations
effective January 1, 2025.
In addition to changes in the HFC
market due to the overall phasedown of
production and consumption, other
AIM Act regulatory programs are
expected to take effect both between
proposal and finalization of this
rulemaking and during the applicable
period under review in this rulemaking,
as described in more detail in Section
V.C.2. These requirements may reduce
demand for HFC–134a domestically for
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certain other uses, though EPA expects
continuing demand for HFC–134a in
applications not subject to restrictions
will continue. There may also be new or
expanded use of blends with HFC–134a
as a component designed to meet new
restrictions. In addition, other EPA
regulations may impact domestic supply
of HFC–134a, but global supply should
remain substantial in comparison to this
application’s demand for HFC–134a.
EPA is currently not aware of any
applicable restrictions on where this
application could purchase HFCs,
including any purity requirements or
regulatory restrictions on supply. As
such, it is EPA’s assessment that this
application may be able to use
recovered and reprocessed HFCs
supplied by chemical manufacturers.
This is relevant in assessing what
supply of regulated substance may be
available to an application, since in
such a case EPA does not need to limit
its analysis to only virgin chemicals.
The likeliest source of reprocessed HFCs
for this application would be reclaimed
refrigerants, which are held to AHRI 700
standards (see footnote 17 in Section
V.C.2). Since there are no Federal purity
requirements for HFCs used in foams or
any industry requirements, the purity of
reclaimed HFCs is likely the same or
higher than the virgin HFCs used in this
application. While EPA is not aware of
specific purity requirements for this
application, EPA notes that efficacy of
blowing agents can be influenced by
their composition and purity. As
described in more detail in Section
V.C.2, the supply of reclaimed HFC–
134a in the United States is significant,
though there is uncertainty regarding
the future demand for this material.
As part of this proposed analysis, EPA
is also considering the supply of HFC–
152a. As further explained in Section
IV.C, as part of the framework for its
analysis EPA is proposing to evaluate
the supply of a substitute HFC if that
HFC is a safe or technically achievable
substitute for an application. As
outlined in the prior section (Section
V.D.1), EPA’s analysis suggests that
HFC–152a blended with cyclopentane
appears to be a safe and technically
achievable substitute for this
application. EPA is therefore evaluating
the supply of HFC–152a to determine
whether it would be insufficient to
accommodate this application. As
described in more detail in Section
V.C.2, other AIM Act regulations may
increase demand for HFC–152a
domestically for certain uses, though
EPA notes that many sectors where
HFC–152a is a technically achievable
substitute have already transitioned to
other alternatives. Domestic production
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capacity is also expected to increase, but
EPA cannot say with certainty when it
will be available. Global supply should
also remain substantial in comparison to
this application’s demand for HFC–
152a.
3. What is EPA proposing regarding
eligibility for application-specific
allowances?
In light of the rapid evolution of
information regarding both the
availability of substitutes for this sector
(including all companies in this
application’s stated plans to transition
away from HFC–134a before 2026) and
HFC supply, EPA is proposing a range
of options based on the current Agency
analysis and in anticipation of increased
available information before this
proposed rule is finalized. Specifically,
EPA is proposing to finalize any of the
following outcomes: (1) no renewal,
such that the application will not
receive ASAs, (2) renew eligibility for
ASAs for two years, such that ASAs are
available for calendar years 2026 and
2027, or (3) renew eligibility to continue
receiving ASAs for the full five-year
period with allowance amounts
determined based on the EV of HFC–
152a.23
Before finalization of this rule, we
anticipate new information to become
available on the supply of HFCs and
availability of substitutes for the
application, as outlined in detail in this
section. EPA will consider this new
information, in addition to public
comments, in making a final
determination for this application.
As explained earlier in this section,
the development of safe or technically
achievable substitutes for this
application is a rapidly evolving space,
such that multiple possible outcomes
can reasonably be expected to occur
through 2030. All entities that have
received ASAs for SCPPU foam for
marine and trailer uses to date have told
EPA that they plan to transition to
substitutes before January 1, 2026. One
potential outcome at rule finalization is
that EPA depends on these statements to
determine that a ‘‘safe or technically
achievable substitute is available for the
applicable period’’ for this application.
Statements from all of the companies
that use regulated substances to
manufacture SCPPU foam that they will
transition to substitutes before the next
ASA period could serve as a reasonable
basis to determine that safe and
technically achievable substitutes are
23 The proposed amendatory text included in this
Federal Register document shows only one of the
co-proposed options. This is for illustrative
purposes and should not be read as EPA favoring
one co-proposal over another.
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available. There are also specific
milestones that these entities have
reached, such as one company receiving
a final air permit for an expansion of the
manufacturing facility that will use the
HFC–152a/cyclopentane blend,
indicating the company is able to move
forward with full-scale testing and
commercialization. If the entities’ plans
shared with EPA remain the same at the
time when EPA is finalizing this
proposed rule, particularly if they have
already commercialized use of the
substitutes, it is likely that EPA would
determine that a safe or technically
achievable substitute is available for this
application. If EPA makes this
determination, SCPPU foam for marine
and trailer uses will not be eligible for
ASAs as of January 1, 2026, even if EPA
receives information to determine that
supply of the currently used regulated
substance is insufficient, unless the
application has insufficient supply of a
substitute HFC, as discussed in more
detail below in this section. However,
EPA recognizes there is uncertainty as
to whether plans to commercialize will
remain the same, be delayed, or be
subject to unanticipated hurdles that
could require additional evaluation of
this alternative. EPA also has less
information regarding the deployment
of the HFO alternative outside of
statements from the entity working
toward its development and
commercialization. Before finalization
of this proposed rule, EPA intends to
review and consider, as appropriate, all
available information, specifically
regarding expected timelines and testing
data. EPA invites comment regarding
the availability of safe or technically
achievable substitutes for this
application. The Agency will continue
to collect information from regulated
entities and other relevant sources
through the public comment period and
the current reporting requirements to
inform a final determination of whether
the criterion in subsection (e)(4)(B)(i)(I)
is met.
EPA is also proposing to determine
either: (1) the supply of HFC–134a is not
insufficient to accommodate this
application; or (2) the supply of HFC–
134a is not insufficient to accommodate
this application as of January 1, 2028. In
other words, EPA proposes to determine
that the criterion in subsection
(e)(4)(B)(i)(I) is either: (1) not met at all
for this application for HFC–134a, and
therefore the application would not be
eligible to receive ASAs with
allowances calculated based on HFC–
134a use starting January 1, 2026; or (2)
not met as of January 1, 2028, and
therefore the application would not be
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eligible to receive ASAs with
allowances calculated based on HFC–
134a use starting January 1, 2028. Under
the first option, this means that even if
the application did not have a safe or
technically achievable substitute
available, ASAs would not be available
for manufacturers of SCPPU foam for
marine and trailer uses as of January 1,
2026. For the second option, SCPPU
foam for marine and trailer uses would
not be an eligible application for ASAs
as of January 1, 2028, regardless of the
availability of substitutes. However, if
the available substitute is an HFC with
insufficient supply, EPA may determine
SCPPU foam for marine and trailer uses
are eligible for renewal for that
substitute HFC.
Given the current uncertainty over
which EPA anticipates having more
clarity ahead of finalization of this
proposed rule, at this time EPA
contends that it could determine that
the criterion in subsection (e)(4)(B)(i)(I)
is met now, met as of January 1, 2028,
or is not met at all through the entire
renewal period with respect to HFC–
152a. Under the first possible
determination (supply of HFC–152a is
not insufficient now), even if the
application did not have a safe or
technically achievable non-HFC
substitute available as of January 1,
2026, the application would not be
eligible for renewal as of that date.
Under the second possible
determination (supply of HFC–152a is
not insufficient as of January 1, 2028),
the application would not be eligible for
ASAs as of January 1, 2028, even if the
application did not have a safe or
technically achievable non-HFC
substitute. Under the third possible
determination (supply of HFC–152a is
insufficient), the application would be
eligible for ASAs if there was no safe or
technically achievable non-HFC
substitute for the entire application.
EPA will monitor reported data over the
next year on the noted areas of
uncertainty and invites comment on this
issue.
In light of the range of outcomes EPA
has proposed regarding its
determinations on whether the criteria
in subsection (e)(4)(B)(i)(I) and (II) are
met, EPA is proposing three potential
outcomes on whether and how SCPPU
foam for marine and trailer uses may be
eligible for future ASAs: (1) not eligible
to receive ASAs; (2) eligible to receive
calendar year 2026 and 2027 ASAs; and
(3) eligible to receive ASAs for the fiveyear period of calendar years 2026–2030
with allowance amounts determined
based on the EV of HFC–152a. EPA is
also taking comment on SCPPU foam for
marine and trailer uses eligibility to
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receive ASAs consistent with the
current approach through calendar year
2030 ASAs. EPA also could finalize
different outcomes based on how the
transition to substitutes progresses
between this proposal and rule
finalization.
Under outcome (3), EPA is proposing
to allocate allowances based on an
expectation that the application can use
HFC–152a. To achieve this, EPA is
proposing to base the calculation of
allowance allocations on the estimated
total mass of HFCs needed by the
application and allocate at the level
necessary to purchase HFC–152a on an
EV-weighted basis. For example, if a
company used 1,000 kg of HFC–134a
and 500 kg of HFC–152a in Year 3 (as
defined by the regulatory formula; see
Section VII for further discussion of
regulatory formula and proposed
revisions), and HFC–152a substituted
for HFC–134a one-for-one on a gram
basis for this application, EPA would
multiply 1,500 kg by the applicable
average annual growth rate (AAGR) and
then by the EV of HFC–152a to calculate
the company’s allowance allocation for
the following year. EPA would not limit
which HFCs could be purchased for use
in the application once the allowances
are issued. EPA is taking comment on
whether the Agency should apply any
relevant mass conversions in this
calculation (i.e., if an application
needed more or less HFC–152a on a
gram-by-gram basis when substituting
for HFC–134a) where the total mass of
HFCs used would be multiplied by a
mass ratio, as appropriate, then
multiplied by the AAGR.
As outlined in detail elsewhere in this
section, before EPA finalizes this
proposed rule, the Agency intends to
review available information and
comments received on this proposal to
get further clarity on progress toward
commercialization of substitutes, how
the overall HFC market has adjusted to
the 2024 stepdown, what alternatives
are adopted by subsectors subject to
2025 Technology Transitions Program
restrictions, and how much additional
domestic HFC–152a production
capacity comes online.
4. Proposed Restriction Under EPA’s
Technology Transitions Program
The 2023 Technology Transitions
Rule (88 FR 73098, October 24, 2023)
restricts the manufacture and import of
foam products that use as a blowing
agent HFCs or HFC blends that have a
GWP of 150 or greater (hereafter, ‘‘foam
products’’). This restriction begins
January 1, 2025. Examples of items
subject to this restriction include
products that are foams, such as
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extruded polystyrene boardstock;
products for blowing foam, such as twopart foam systems for blowing PU foam;
and products that are manufactured
using foam, such as boats or refrigerated
trailers.
The 2023 Technology Transitions
Rule exempts applications which
receive ASAs (40 CFR 84.56(a)(2)).
However, as finalized in the October 24,
2023, rule, if an application no longer
qualifies for ASAs, the Technology
Transitions restrictions would apply.
As discussed in the preamble to the
2023 Technology Transitions Rule, the
transition to non-HFC and lower-GWP
substitutes is already well underway or
completed for much of the foams sector
(see 88 FR 73184). EPA therefore
established a uniform GWP limit of 150
for the entire foams sector starting
January 1, 2025. The sole exception to
this restriction for the foams sector was
SCPPU foam for marine and trailer uses,
per their receipt of ASAs. As discussed
above in Section V.D.1, EPA proposes
that while there are no safe and
technically achievable alternatives
available at this time under subsection
(e)(4)(B) specifically for use in SCPPU
foams for marine and trailer uses, we
anticipate, based on currently available
information, that the development of
substitutes for these uses is progressing
rapidly, such that by the time EPA
finalizes this action, substitutes meeting
the (e)(4)(B)(i)(I) criterion may be
available. While the list of
considerations under subsection
(i)(4)(B) that EPA is to factor in, to the
extent practicable, when considering
availability of substitutes for issuing
restrictions under subsection (i)
includes factors beyond those
characteristics listed in subsection
(e)(4)(B)(i)(I), in this instance EPA’s
view is that technological achievability
of lower-GWP substitutes in marine and
trailer uses is the primary barrier to
transitioning away from the use of HFC–
134a in these two uses. Many of the
factors listed in subsection (i)(4)(B) are
not relevant to EPA’s assessment of
availability of substitutes for these two
uses, such as building codes, appliance
efficiency standards, and contractor
training costs. As noted in Section V.D.1
of this preamble, EPA’s SNAP Program
has already listed as acceptable the
potential substitutes under
consideration and the entities actively
developing the substitutes and working
to bring those substitutes to market are
almost certainly considering costs to
consumers and affordability for small
business consumers as part of their
efforts.
We propose that the applicability of
the restriction on HFC foam blowing
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agents in the 2023 Technology
Transitions Rule to SCPPU foam for
marine and trailer uses will depend
entirely on which of the three coproposals EPA ultimately finalizes. That
is, under co-proposal (1), where EPA
would not renew ASAs for SCPPU for
marine and trailer uses as of the
effective date of a final rule based on
this proposal, requirements of the
Technology Transitions Program, which
include labeling, reporting,
recordkeeping, and restrictions on
HFCs, would apply beginning January 1,
2026. Under co-proposal (2), where EPA
would renew ASAs for SCPPU for
marine and trailer uses for 2026 and
2027, requirements of the Technology
Transitions Program would apply
beginning January 1, 2028. For both coproposals (1) and (2), EPA proposes that
the recordkeeping requirements would
apply to manufacturers of SCPPU foams
for marine and trailer uses beginning
January 1 of the year those uses no
longer qualify for ASAs, and the first
report would be due March 31 of the
following year, as discussed above in
Section V.C.4. For example, under coproposal (1), manufacturers would need
to keep records as required by the 2023
Technology Transitions Rule starting
January 1, 2026, and submit their first
Technology Transitions report to EPA
by March 31, 2027; under co-proposal
(2), manufacturers would need to keep
such records starting January 1, 2028,
and would submit their first Technology
Transitions report by March 31, 2029.
Under co-proposal (3), where EPA
would renew ASAs for SCPPU for
marine and trailer uses based upon the
use of HFC–152a instead of HFC–134a,
SCPPU for marine and trailer uses
would continue to be exempt from the
2023 Technology Transitions Rule. The
requirements under each co-proposal for
SCPPU for marine and trailer uses are
summarized in Table 2 below. EPA is
interested in data and information
related to the availability of substitutes
and the proposed timeline for
transitioning in this application.
TABLE 2—APPLICABILITY OF TECHNOLOGY TRANSITIONS REQUIREMENTS UNDER CO-PROPOSALS FOR SCPPU FOR
MARINE AND TRAILER USES
Co-proposal
Technology transitions GWP limit
and compliance date
Date technology transitions
labeling requirements begin
Date technology transitions
reporting requirements begin
(1) No renewal of ASAs .................
GWP limit of 150 beginning January 1, 2026.
January 1, 2026 ............................
First report due March 31, 2027,
including data from January 1,
2026, through December 31,
2026.
(2) Renew eligibility for ASAs for
2026 and 2027.
GWP limit of 150 beginning January 1, 2028.
First report due March 31, 2029, including data from January 1, 2028,
through December 31, 2028.
(3) Renew eligibility for 2026–2030
with allowance amounts determined based on the EV of HFC–
152a.
Because application continues to be eligible for ASAs, it is exempt from Technology Transitions requirements.
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E. Etching of Semiconductor Material or
Wafers and the Cleaning of Chemical
Vapor Deposition Chambers Within the
Semiconductor Manufacturing Sector
EPA has been allocating ASAs for
regulated substances used for the
etching of semiconductor material or
wafers and the cleaning of CVD
chambers within the semiconductor
manufacturing sector in accordance
with subsection (e)(4)(B)(iv)(I)(dd) of the
AIM Act. In the Allocation Framework
Rule, EPA defined ‘‘etching’’ in the
context of semiconductor manufacturing
as ‘‘a process type that uses plasmagenerated fluorine atoms and other
reactive fluorine-containing fragments
that chemically react with exposed thin
films (e.g., dielectric, metals) or
substrate (e.g., silicon) to selectively
remove portions of material. This
includes semiconductor production
processes using fluorinated GHG
reagents to clean wafers.’’ (40 CFR 84.3).
EPA defined ‘‘chemical vapor
deposition chamber cleaning’’ (hereafter
referred to as ‘‘chamber cleaning’’) in
the context of semiconductor
manufacturing as ‘‘a process type in
which chambers used for depositing
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thin films are cleaned periodically using
plasma-generated fluorine atoms and
other reactive fluorine-containing
fragments’’ (40 CFR 84.3). At the time of
this proposal, EPA is aware of three
HFCs that are used for this application
in manufacturing. HFC–23 is commonly
used for selective dry etching of silicon
dioxide (SiO2) and silicon nitride (SiN),
while HFC–32 and HFC–41 are used in
high-aspect-ratio hole etching. HFC–23,
HFC–32, and HFC–41 may also be
minimally used in chamber cleaning
processes.
EPA is proposing to determine that no
safe or technically achievable substitute
will be available for the semiconductor
application and that supply of the
regulated substance that manufacturers
and users are capable of securing from
chemical manufacturers is insufficient
to accommodate the semiconductor
application through calendar year 2030.
Therefore, EPA proposes to renew the
eligibility of entities using regulated
substances for the defined
semiconductor application to receive
ASAs for the five-year period of
calendar years 2026 through 2030.
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1. Availability of Safe and Technically
Achievable Substitutes
EPA has not identified any substitutes
that it would propose to deem safe and
technically achievable that are available
for the entirety of the defined
semiconductor application.
In developing this assessment, EPA
reviewed information from industry
trade groups, the TEAP’s MCTOC, the
Intergovernmental Panel on Climate
Change (IPCC), scientific journal
articles, and more. The sources
examined by EPA are outlined in greater
detail in the TSD included in the docket
for this proposed action.
The MCTOC 2022 Assessment report
reviewed HFC gases commonly used in
semiconductor manufacturing, along
with their alternatives, using the
following criteria: commercially
available, technically proven,
environmentally sound, economically
viable and cost effective, safe to use in
industrial applications considering
flammability and toxicity issues, and
easy to use and maintain.24 Based on
this report and other sources, EPA is
24 See https://ozone.unep.org/system/files/
documents/MCTOC-Assessment-Report-2022.pdf.
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aware that semiconductor
manufacturers currently utilize other
fluorinated gases, such as sulfur
hexafluoride (SF6), nitrogen trifluoride
(NF3), some saturated PFCs (i.e., CF4,
C2F6, c-C4F8), and some unsaturated
PFCs (i.e., C4F6, C5F8) for the processes
of etching and chamber cleaning. The
MCTOC 2022 Assessment report lists
these chemicals as both commercially
available and technically proven and
can be used as substitutes for etching
and chamber cleaning. In developing its
proposed determination regarding
substitutes, however, EPA did not
consider many of these chemicals in its
proposed consideration of the
availability of safe and technically
achievable substitutes because of their
higher GWPs, lower utilization rates
(i.e., higher emission rates), or higher
toxicity than HFCs. Sulfur hexafluoride
(SF6), which is used in the etching of
silicon, silicon dioxide (SiO2), and
silicon nitride (SiN), as well as chamber
cleaning, has a 100-year GWP of 22,800.
Nitrogen trifluoride (NF3), which is used
in the etching of silicon and silicon
nitride (SiN), as well as for chamber
cleaning, has a 100-year GWP of 17,200.
Saturated PFCs, used in the etching of
silicon, silicon dioxide (SiO2), and other
materials, have a 100-year GWP ranging
between 7,390 to 12,200. Saturated PFCs
are also difficult to abate and have
relatively low utilization rates.
Unsaturated PFCs are used in highaspect-hole-ratio etching. They have
GWPs of less than two; however, these
compounds have not been widely
adopted at least in part since these
chemicals can only be used in certain
processes and are not necessarily viable
for all types of etching, etching all
materials, or chamber cleaning. For
example, unsaturated PFCs are not
known to be used in chamber cleaning,
so the Agency does not consider
unsaturated PFCs as available for the
entire application.
The MCTOC 2022 Assessment report
also lists other compounds that are
currently being studied for use but are
not yet technically proven, are not
considered safe or easy to use, and may
have additional toxicity concerns. These
chemicals include carbonyl sulfide,
HFO–1336mzz(E), PFC–1216, chlorine
trifluoride (ClF3), hexafluoroisobutylene
(HFIB), and trifluoroiodomethane (CF3I).
Carbonyl sulfide, used in certain etching
applications, is also highly flammable
and toxic. HFO–133mzz(E) is being
considered as a replacement for certain
etching chemicals. PFC–1216 is being
studied for use in etching silicon
dioxide (SiO2). Chlorine trifluoride
(ClF3) may be used for chamber cleaning
for Low Pressure CVD chambers but is
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extremely flammable and is not
considered safe or easy to use. Although
not known to currently be used,
hexafluoroisobutylene (HFIB) could be
used in certain etching applications for
silicon containing material.
Trifluoroiodomethane (CF3I) is used for
etching of silicon dioxide (SiO2) and
silicon nitride (SiN), but the MCTOC
2022 Assessment report does not list it
as safe or easy to use.
EPA is aware of certain HFCs that
may be in the early stages of research for
high-aspect-ratio hole etching, such as
HFC–134a and HFC–125. ASA holders
have stated that research on lower-GWP
alternatives is ongoing and there are
currently no known alternatives to
HFCs, PFCs, and nitrogen trifluoride
(NF3), and any alternatives would not be
commercially available until at least
2030.
In light of the above analysis, EPA has
not identified a safe and technically
achievable substitute that is available at
the time of this proposal. When a
substitute or substitutes are identified
for the entirety of the application, it
would still take significant time to
replace the current HFC(s) with the
substitute(s). One industry trade group
has stated that semiconductor
technologies require at least 10 years
from fundamental research to high
volume manufacturing to innovate and
implement new technologies and their
associated raw materials. Given that no
promising substitutes have been
identified, there is no information
before the Agency at the time of this
proposal to suggest that there would be
a safe and technically achievable
substitute available prior to the next
five-year review.
2. Supply
HFC–23, HFC–32, and HFC–41 are all
currently used in the etching of
semiconductor material or wafers and
the cleaning of CVD chambers within
the semiconductor manufacturing
sector. As described earlier in Section
IV.B of the preamble, EPA is proposing
to determine that an application meets
this criterion if EPA determines that any
of the HFCs currently used in an
application’s equipment or to
manufacture the application’s products
for use have insufficient supply.
As described above in Section E of
this preamble, HFC–23 is used in the
etching of silicon dioxide (SiO2) and
silicon nitride (SiN) and is also used
minimally in chamber cleaning. In 2022,
domestic producers produced
approximately 1,049.3 MT of HFC–23.
876.2 MT were subsequently destroyed,
and one producer sold 5.2 MT of this
HFC–23 for consumptive uses, which
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could be used for semiconductors as
well as other uses. In addition, there
were about a half dozen entities that
imported HFC–23 with total amount of
imports equaling 125.6 MT. Overall,
HFC–23 made up only 0.07 percent of
total U.S. HFC consumption in 2022 on
a mass basis. Moreover, as HFC–23 has
the highest EV, it may be possible that
this supply is further constricted in the
future as the phasedown progresses and
the number of available allowances is
reduced. As stated elsewhere in this
proposed rule, EPA recognizes that
there is inherent uncertainty regarding
HFC production, and in particular for
HFCs with a more limited number of
production facilities and/or higher
GWPs than other regulated HFCs, this
uncertainty may be greater. Therefore,
EPA understands there will be changes
to the market conditions resulting from
the domestic and global phasedown of
HFC production and consumption.
In addition, the use of HFC–23 in the
semiconductor manufacturing
application is large compared to the
annual consumption of HFC–23. In
2022, semiconductor ASA holder
purchases 25 of HFC–23 accounted for
about 81 percent of calculated
consumption of HFC–23. Furthermore,
at the end of 2022, suppliers held 304.0
MT of HFC–23 in domestic inventory,
which is equivalent to about 293
percent of calculated consumption of
HFC–23 in 2022; not all of this HFC–23
may be considered available supply, as
the entities both holding this material in
inventory and reclaiming these HFCs
are broader than EPA’s interpretation of
chemical manufacturers (see Section
IV.B for more information).
EPA also analyzed the supply of
HFC–32. In 2022, the one domestic
producer of HFC–32 produced 17,744.3
MT of HFC–32. There were also over a
dozen entities that imported HFC–32,
with total import quantities equaling
9,885.3 MT. Overall, HFC–32 made up
approximately 17 percent of total U.S.
HFC consumption in 2022 on a mass
basis. The use of HFC–32 in the
semiconductor manufacturing
application is small compared to the
annual consumption of HFC–32. In
2022, semiconductor ASA holder
purchases of HFC–32 accounted for less
than 0.035 percent of calculated
consumption of HFC–32. At the end of
2022, suppliers held 21,435 MT of HFC–
32 in domestic inventory, which is
equivalent to about 80 percent of
calculated consumption of HFC–32 in
2022; similar to considerations for
25 For this calculation, EPA is using purchases in
2022 instead of allowances allocated so that percent
of consumption can be calculated for each HFC.
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supply of HFC–23 and for other
applications, not all of this inventory
may be considered available.
Another factor EPA is considering is
the impact that other regulatory actions
may have for the available supply of
HFC–32. As described in more detail
above in Section V.A, the overall market
for HFCs is likely to continue changing
in light of AIM Act and potentially other
restrictions. There is particular
uncertainty regarding demand for HFC–
32. The 2023 Technology Transitions
Rule (88 FR 73098, October 24, 2023) set
a GWP threshold of 700 for certain
sectors and subsectors where previously
higher-GWP HFCs or HFC blends have
been used. HFC–32 has a GWP of 675
and may be a suitable alternative in
those sectors and subsectors. In other
cases, the 2023 Technology Transitions
Rule set a GWP threshold of 150 and
thus HFC–32 could not be used unless
as a component of blends. The first set
of restrictions under the 2023
Technology Transitions Rule have
compliance dates of January 1, 2025,
with the latest compliance dates taking
effect on January 1, 2028. Additionally,
the proposed Emissions Reduction and
Reclamation Rule (88 FR 72216, October
19, 2023) proposes requirements for the
use of recycled or reclaimed HFCs for
certain uses, as discussed elsewhere in
this preamble. When finalized, that rule
may affect the use of reclaimed HFC–32.
EPA also analyzed the supply of
HFC–41. There is one domestic supplier
of HFC–41 that produced 22.2 MT of
HFC–41 in 2022. In addition, there were
multiple entities that imported HFC–41,
with total import quantities equaling
38.3 MT. Overall, HFC–41 made up only
0.03 percent of total U.S. HFC
consumption in 2022 on a mass basis.
The use of HFC–41 in the
semiconductor manufacturing
application is moderately large
compared to the annual consumption of
HFC–41. In 2022, semiconductor ASA
holder purchases of HFC–41 accounted
for 21.5 percent of calculated
consumption of HFC–41. At the end of
2022, suppliers held 26.7 MT of HFC–
41 in domestic inventory, which is
equivalent to about 60 percent of
calculated consumption of HFC–41 in
2022; as noted for the supply of HFC–
23 and HFC–32 and for other
applications, not all of this inventory
may be considered available.
One factor that plays into the
sufficiency of supply of these HFCs is
the purity specifications used by
individual companies in the
semiconductor manufacturing sector.
While there is no Federal standard or
regulation governing the purity of HFCs
used in semiconductor manufacturing,
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EPA is aware that individual companies
in this sector set their own
requirements. HFCs purchased for use
in semiconductor manufacturing is
produced at around 95–97 percent
purity and then typically is purified to
99.999–99.9999 percent purity before it
is used by semiconductor
manufacturers. Supplying refined HFCs
to end users can take up to one year, as
purifiers require long lead times.
These purity requirements are also
relevant when considering if reclaimed
HFCs can be used in this application.
EPA notes that virgin HFCs produced
for semiconductor use are typically only
at 95–97 percent purity, so EPA is not
aware of why reclaimed HFCs cannot
also be purified to industry
specifications; EPA invites comments
on this. Of the three HFCs utilized by
the semiconductor industry, only HFC–
23 and HFC–32 were reclaimed in 2022
and thereby could be a source of supply
for this application, though the amount
of reclaimed material is small. In
addition, it is possible to capture the
unreacted process gases used in
semiconductor manufacturing, but the
reclamation of fluorinated gases from
the semiconductor manufacturing
process is not currently economically
viable.
There are other factors that may
further impact the supply of HFCs for
this application. The Creating Helpful
Incentives to Produce Semiconductors
Act of 2022 (CHIPS Act) has allocated
over 50 billion dollars to semiconductor
research, development, manufacturing,
and workforce development in the
United States, which has led to
additional investment by semiconductor
manufacturers. The U.S. market share of
memory chip production is projected to
grow from less than 2 percent to up to
10 percent over the next decade.26 27
3. What is EPA proposing regarding
eligibility for application-specific
allowances?
EPA is proposing to renew the
eligibility of entities using regulated
substances for the etching of
semiconductor material or wafers and
the cleaning of CVD chambers within
the semiconductor manufacturing sector
to receive ASAs for the five-year period
of calendar years 2026 through 2030.
EPA is proposing to determine ‘‘that the
requirements described in subclauses (I)
26 See https://www.whitehouse.gov/briefing-room/
statements-releases/2022/01/21/fact-sheet-bidenharris-administration-bringing-semiconductormanufacturing-back-to-america-2/.
27 See https://www.mckinsey.com/industries/
industrials-and-electronics/our-insights/
semiconductor-fabs-construction-challenges-in-theunited-states.
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and (II) of clause (i) are met’’ in
accordance with the requirements of 42
U.S.C. 7675(e)(4)(B)(v)(II). Specifically,
for the reasons outlined earlier in this
section, EPA is proposing to determine
that no safe or technically achievable
substitute will be available for the
etching of semiconductor material or
wafers and the cleaning of CVD
chambers within the semiconductor
manufacturing sector for the entire fiveyear period. EPA is also proposing to
determine that supply of the regulated
substance that manufacturers and users
are capable of securing from chemical
manufacturers is insufficient to
accommodate this application through
calendar year 2030. As explained
earlier, EPA is proposing to determine
the supply criterion is met if supply of
one HFC used by the application is
insufficient to accommodate the
application. EPA proposes to determine
that the supply of HFC–23 and HFC–41
are insufficient to accommodate the
application for the reasons outlined in
the prior section.
F. Mission-Critical Military End Uses
EPA has been allocating ASAs for
regulated substances used for MCMEU
in accordance with subsection
(e)(4)(B)(iv)(I)(ee) of the AIM Act. In the
Allocation Framework Rule, EPA
defined ‘‘mission-critical military end
uses’’ as ‘‘those uses of regulated
substances by an agency of the Federal
Government responsible for national
defense which have a direct impact on
mission capability, as determined by the
U.S. Department of Defense (DOD),
including, but not limited to uses
necessary for development, testing,
production, training, operation, and
maintenance of Armed Forces vessels,
aircraft, space systems, ground vehicles,
amphibious vehicles, deployable/
expeditionary support equipment,
munitions, and command and control
systems’’ (40 CFR 84.3). In the
Allocation Framework Rule, EPA
finalized an approach that treats the
allocation of MCMEU allowances
differently than the other applications
given the ‘‘complex nature of the way
DOD sources and uses HFCs for
mission-critical applications,’’ (e.g.,
significantly larger networks of sites and
users, including contractors, of HFCs
than others covered by ASAs) (86 FR
55116, 55153, October 5, 2021). EPA set
up a system whereby DOD must provide
the amount of HFCs needed for missioncritical military use and that the two
agencies would ‘‘work together to
ensure the amount necessary is
available for mission-critical military
applications’’ (86 FR 55116, 55153,
October 5, 2021).
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As the definition states, DOD has
discretion to identify which uses of
HFCs have a direct impact on mission
capability. DOD is required to report to
EPA ‘‘the broad sectors of use covered
by current mission-critical military end
uses in the next calendar year,’’ per 40
CFR 84.31(h)(3)(iv). Given the complex
nature of the way DOD sources and uses
HFCs for mission-critical applications,
EPA has always maintained that DOD
should have discretion to request the
amount of allowances necessary to meet
its mission-critical end uses and the
Agency is not altering that approach
through this rulemaking.
Recognizing the sensitive nature of
the application, as well as the expert
judgement that DOD has in identifying
which uses of HFCs have a direct
impact on mission capability, EPA
consulted with DOD throughout
development of this proposed rule,
including in advance of interagency
review, and received input to support
EPA’s evaluation of the statutory criteria
described in Section IV of this
preamble.
After analyzing information relevant
to the statutory criteria, as outlined in
this section, and based on input from
DOD, EPA is proposing to determine
that no safe or technically achievable
substitute will be available for the
MCMEU application and that the supply
of the regulated substances that the
application is capable of securing from
chemical manufacturers is insufficient
to accommodate the MCMEU
application through calendar year 2030.
Therefore, EPA proposes to renew the
eligibility of the MCMEU application to
receive ASAs for the five-year period of
calendar years 2026 through 2030.
1. Availability of Safe and Technically
Achievable Substitutes
As discussed earlier in the preamble,
in situations where there are not safe
and technically achievable substitutes
available for the entirety of the
application, EPA would consider the
statutory criterion regarding substitutes
as being met. In public technical reports
DOD (included in the rulemaking
docket), DOD identified mission-critical
end uses that do not have safe and
technically achievable substitutes
available. For example, DOD uses a
mixture of HFC–227ea and sodium
bicarbonate dry chemical in automatic
fire extinguishing systems that protect
the crew compartments of ground
vehicles. DOD has tested potential
replacements but has not identified a
viable alternative to date. There are
distinct technical specifications for
some mission-critical end uses that are
distinct from civil standards for the
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same category of use (e.g., refrigerants
and fire suppression agents). For
example, automatic fire suppression
systems in ground vehicles must meet
unique military requirements for
inhalation toxicity that allow personnel
to stay within the protected space for at
least five minutes after fire suppression.
Furthermore, because Congress
defined this application as what is
‘‘mission-critical,’’ EPA has always
acknowledged that this application is
more fluid in terms of what particular
HFC uses fall within the application.
DOD may change which end uses it
determines to be mission-critical over
time. This further feeds into EPA’s
proposed assessment that the Agency
cannot determine at this time that there
will be safe and technically achievable
substitutes available for the entirety of
the application.
2. Supply
In 2021, DOD sent a letter to EPA with
information regarding mission-critical
end uses at the time, including a list of
six HFCs used in the application (HFC–
125, –134a, –143a, –227ea, –236fa, and
–32). EPA has determined through
communications with DOD that at least
some of these HFCs continue to be
utilized in mission-critical end uses. As
described in section IV.B of the
preamble, EPA is proposing to
determine that an application meets this
criterion if EPA determines that any of
the HFCs currently used to manufacture
products or systems for use in the
application have insufficient supply.
In the analysis of other applications in
this proposal, EPA has evaluated the
supply of five out of six HFCs that DOD
identified as using in 2021 (i.e., all but
HFC–143a). EPA is proposing to
determine that supply of some of these
HFCs is insufficient to accommodate the
application. For example, in the
evaluation of supply for the onboard
aerospace fire suppression application,
EPA is proposing to determine that the
supply of HFC–227ea and HFC–236fa is
insufficient to accommodate the
application. This is in addition to the
unique restrictions that apply to the
Defense Logistics Agency and DOD
purchasing requirements that impact the
available supply of HFCs to DOD for
MCMEUs. For example, there are Buy
America requirements in Federal
Acquisition Regulation (FAR) 25.1 and
Defense Federal Acquisition Regulation
Supplement (DFARS) 225.1 which may
restrict how DOD can procure goods,
which may include HFCs. Furthermore,
as noted in the substitutes discussion
for the MCMEU application, EPA has
always acknowledged that this
application is more fluid in terms of
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75921
what HFC uses fall within the
application. DOD may change which
end uses it determines to be missioncritical over time. The fact that DOD
may determine that different HFCs and
different annual quantities of those
HFCs are necessary for mission-critical
end uses further feeds into EPA’s
proposed assessment that the supply of
HFCs will be insufficient to
accommodate the application.
3. What is EPA proposing regarding
eligibility for application-specific
allowances?
EPA proposes to renew eligibility for
DOD to receive MCMEU ASAs for the
five-year period of calendar years 2026
through 2030. EPA is proposing to
determine ‘‘that the requirements
described in subclauses (I) and (II) of
clause (i) are met’’ in accordance with
the requirements of 42 U.S.C.
7675(e)(4)(B)(v)(II). Specifically, for the
reasons outlined earlier in this section,
EPA is proposing to determine that no
safe or technically achievable substitute
will be available for the entirety of the
application and that the supply of the
regulated substance that manufacturers
and users are capable of securing from
chemical manufacturers is insufficient
to accommodate the application through
calendar year 2030.
G. Onboard Aerospace Fire Suppression
EPA has been allocating ASAs for
regulated substances used for onboard
aerospace fire suppression in
accordance with subsection
(e)(4)(B)(iv)(I)(ff) of the AIM Act. In the
Allocation Framework Rule, EPA
defined ‘‘onboard aerospace fire
suppression’’ as the ‘‘use of a regulated
substance in fire suppression equipment
used on board commercial and general
aviation aircraft, including commercialderivative aircraft for military use;
rotorcraft; and space vehicles. Onboard
commercial aviation fire suppression
systems are installed throughout
mainline and regional passenger and
freighter aircraft, including engine
nacelles, auxiliary power units (APUs),
lavatory trash receptacles, baggage/crew
compartments, and handheld
extinguishers’’ (40 CFR 84.3). At the
time of this proposal, EPA is aware of
only one area, lavatory trash receptacles,
in which HFCs (specifically HFC–227ea
and HFC–236fa) are used in commercial
aviation. For military uses, HFC–125
has been used in engine nacelles and
APUs, and HFC–236fa has been used in
a streaming application (i.e., a portable
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extinguisher).28 In addition to HFC uses
in commercial and military aviation,
EPA is aware that HFCs have limited
usage in general aviation, which
consists of private and/or business
aircraft. The Agency seeks additional
information on how HFCs are used for
general aviation and how widespread
the use is.
After analyzing information relevant
to the statutory criteria, as outlined in
this section and the TSD, EPA is
proposing to determine that no safe or
technically achievable substitute will be
available for the entirety of onboard
aerospace fire suppression and that
supply of the regulated substance that
manufacturers and users are capable of
securing from chemical manufacturers
is insufficient to accommodate the
onboard aerospace fire suppression
application through calendar year 2030.
Therefore, EPA proposes to renew the
eligibility of entities using regulated
substances for onboard aerospace fire
suppression to receive ASAs for the
five-year period of calendar years 2026
through 2030.
lotter on DSK11XQN23PROD with PROPOSALS2
1. Availability of Safe and Technically
Achievable Substitutes
Identification of available safe and
technically achievable substitutes in
this application requires considering a
range of factors, including fire
suppression effectiveness, toxicity, and
space and weight considerations. EPA
has not identified available substitutes
that it would propose to deem safe and
technically achievable for the entirety of
the onboard aerospace fire suppression
application. As discussed earlier in the
preamble, in situations where there are
not safe and technically achievable
substitutes available for the entirety of
the application, EPA would not
consider this statutory criterion met.
HFCs are used in onboard aerospace
fire suppression in fixed systems for
total flooding applications and in
portable equipment for streaming uses
(e.g., handheld fire extinguishers). Fire
suppression agents must satisfy
environmental and safety criteria,
including but not limited to acceptable
ODPs and GWPs, be effective
extinguishants, and, for spaces where
people would be present, have
sufficiently low toxicity such that under
normal use the discharge of agent in
occupied spaces would not harm
people. Other important features that
are sometimes relevant for onboard
aerospace fire suppression include
28 See https://www.epw.senate.gov/public/_
cache/files/d/1/d152a591-878f-4a4d-b9c1dc7121c06eca/9D366FF1E61F7
EFFD6A71C37C92924A5.04.03.2020-boeing.pdf.
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being electrically non-conductive, and
‘‘clean’’ in certain applications such as
for high-value electronics, controls, or
other critical systems in the protected
spaces where it is important to leave no
non-volatile residue that could damage
the equipment.
As noted at the start of this section,
HFCs are used in limited areas within
the application. Because there are
potentially overlapping ASAs available
for a military use of HFCs, EPA has
focused its analysis of substitute
availability primarily on commercial
aviation. EPA is aware of only one
application where HFCs are used in
commercial aviation: lavatory trash
receptacle fire extinguishing systems.
Lavatory trash receptacle systems are
total flooding systems; total flooding
systems are designed to automatically
discharge a fire extinguishing agent
throughout a confined space. EPA has
not identified any safe and technically
achievable substitutes for lavatory trash
receptacle systems. In coming to this
proposed determination, EPA reviewed
information from multiple sources
including FAA, the EPA SNAP Program,
FSTOC, and the International Civil
Aviation Organization (ICAO) which is
outlined in greater detail in the TSD
included in the docket for this proposed
action. The FSTOC 2022 Assessment
Report noted that it is not aware of any
research to develop an HFC substitute in
lavatory trash receptacle fire
extinguishing systems. Furthermore,
FSTOC noted that identifying
substitutes for lavatory trash receptacles
is a low priority for industry given that
it makes up less than one percent of the
installed fire suppression base on board
aircraft.
In developing its proposed
determination, given the global effort to
find viable halon alternatives, EPA did
not consider halons in its proposed
consideration of the availability of safe
and technically achievable substitutes.
However, both Halon 1301 and Halon
1211 are technically achievable and
continue to be used in onboard
aerospace fire suppression. Although
the onboard aerospace fire suppression
industry has relied on halons for fire
suppression for decades, the United
States phased out the production and
import of virgin halons in 1994 due to
their high ODP. Recycled halons have
been the only supply of halons in the
United States for nearly 30 years and
still comprise the majority of installed
fire suppression capacity on most
aircraft. Industry has made extensive
efforts to identify alternatives to halons
particularly with recent estimates from
the TEAP’s FSTOC that the dwindling
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supply of recycled halons could lead to
shortages in the next decade.
In assessing whether there was a safe
and technically achievable substitute
available, EPA also considered what
alternatives are listed for use under
SNAP for fire suppression that would be
relevant for these applications. EPA
notes that 2-bromo-3,3,3trifluoropropene (2–BTP) is listed as an
acceptable substitute subject to use
conditions for use as a streaming agent
in handheld extinguishers and for
certain total flooding applications (e.g.,
engine nacelles and APUs). FAA has
approved the use of 2–BTP in handheld
extinguishers, and commercial aircraft
manufacturers have begun replacing
Halon 1211 with 2–BTP extinguishers
on newly designed aircraft. As noted
above, the SNAP Program listed 2–BTP
as acceptable as a total flooding agent in
engine nacelles and APUs; however, 2–
BTP has not been listed as acceptable in
lavatory trash receptacles and the
factors for consideration are different
from other acceptable SNAP-listed uses.
For examples, use in lavatory trash
receptacles would be in a space
occupied by people, whereas use in
engine nacelles and APUs are in
unoccupied spaces. Furthermore, FAA
has not approved 2–BTP for any total
flooding systems to date.
As noted in the introduction to this
section, in addition to the use of HFCs
for lavatory trash receptacles in
commercial aviation, HFC–125 has been
used in engine nacelles and APUs on
commercial-derivative aircraft for
military use. Industry has explored
several other fire suppression agents in
engine nacelles and APUs, but none
have proven to be a viable solution. For
example, the industry previously
explored FK–5–1–12 for use as a fire
suppression agent in engine nacelles,
but it failed an FAA-required live fire
test. As a result, for the purposes of its
evaluation under the AIM Act
subsection (e), EPA has not identified
safe and technically achievable
substitutes that are available for use in
engine nacelles or APUs.
In addition to the areas in which
HFCs are used in total flooding systems,
HFC–236fa is used as a streaming agent
in commercial-derivative aircraft for
military use. As previously noted in this
section, 2–BTP has been listed as
acceptable by SNAP, is FAA-approved,
and commercial aircraft manufacturers
have begun transitioning to 2–BTP
extinguishers on newly produced
aircraft. While EPA analysis suggests
that 2–BTP is available as a safe and
technically achievable substitute, as
explained elsewhere in this proposal,
EPA would only determine the statutory
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criterion in subsection (e)(4)(B)(i)(I) is
not met if the Agency determines
substitutes are available for the entirety
of the application.
If a substitute were identified for the
entirety of the application, it would still
take significant time for transition to the
substitute to occur for this application.
FAA has testing requirements and
minimum performance standards that a
new fire suppression agent must meet
before it can be used commercially.
While there is no prescribed amount of
time it takes to meet these requirements,
a stakeholder indicated to EPA in a
November 2023 public stakeholder
meeting that the certification process
can take three to five years. Another
stakeholder described the FAA process
as arduous and noted that it could take
many years to receive certification for a
new fire suppression agent. There is no
information before the Agency at the
time of this proposal to suggest that
there would be a safe and technically
achievable substitute available prior to
the next five-year review.
2. Supply
As previously discussed, HFC–227ea,
HFC–236fa, and HFC–125 are all
currently used in onboard aerospace fire
suppression. As described in Section
IV.B of the preamble, EPA is proposing
to determine that the requirements of 42
U.S.C. 7675(e)(4)(B)(i)(II) are met for this
application if EPA determines that any
of the HFCs currently used in a
commercial product or to manufacture
products for use in the application have
insufficient supply.
HFC–227ea is the only regulated
substance for which onboard aerospace
fire suppression allowances have been
expended to date. As previously stated,
HFC–227ea is used in commercial
aviation whereas HFC–236fa and HFC–
125 are used in commercial-derivative
aircraft for military use. As intended in
the Allocation Framework Rule, there is
overlap between the onboard aerospace
fire suppression application and the
MCMEU application. EPA is not
reopening this approach through this
rulemaking, so as long as DOD
continues to classify the operation of
Armed Forces aircraft as missioncritical, then DOD may use MCMEU
allowances for fire suppression
equipment installed on commercialderivative aircraft. Therefore, in
addition to HFC–227ea being the only
regulated substance for which onboard
aerospace fire suppression allowances
have been expended, the uses of HFC–
227ea are the only uses for which the
onboard aerospace fire suppression
application is the sole pathway to
receive allowances. In 2022, the sole
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domestic producer of HFC–227ea
produced 1,324.7 MT of HFC–227ea,
comprising one percent of U.S. HFC
production on a mass basis. In addition,
there were nine entities that imported
HFC–227ea with the total amount of
imports equaling 454.2 MT. Overall,
HFC–227ea made up only 0.2 percent of
all U.S. HFC consumption in 2022 on a
mass basis. At the end of 2022,
suppliers held 1,008.3 MT of HFC–
227ea in domestic inventory, which is
equivalent to about 323 percent of
calculated consumption of HFC–227ea
in 2022; as noted in the supply
discussions for the other applications
above (Sections B–E), not all of this
HFC–227ea may be considered available
supply, as the entities holding this
material are broader than EPA’s
interpretation of chemical
manufacturers. As stated elsewhere in
this proposed rule, EPA recognizes that
there is inherent uncertainty regarding
HFC production, and in particular for
HFCs with a more limited number of
production facilities and/or higher
GWPs than other regulated HFCs, this
uncertainty may be greater; HFC–227ea
has one of the highest GWPs of the
regulated HFCs. Additionally, EPA
understands there will be changes to
market conditions resulting from the
domestic and global phasedown of HFC
production and consumption that could
affect future supply of HFC–227ea.
Given the relative size of the market for
HFC–227ea and the limited number of
producers in the United States and
abroad, the supply chain for HFC–227ea
is potentially more fragile than other
supply chains (e.g., HFC–134a). This
makes it more likely that the supply of
HFC–227ea available from chemical
manufacturers will be insufficient
during 2026–2030 for this application.
The use of HFC–227ea in onboard
aerospace fire suppression is small
compared to the annual consumption of
HFC–227ea. Allocated ASAs for this
application in 2024 are equivalent to 0.8
percent of calculated consumption of
HFC–227ea in 2022. While this small
usage could make it easier for suppliers
to divert a fraction of their available
supply to this application, the supply
chain for HFC–227ea remains fragile for
reasons mentioned earlier in this
section, including low production and a
limited number of suppliers.
Another factor EPA is considering is
the impact that other regulatory actions
may have for the available supply of
HFC–227ea. Specifically, the proposed
Emissions Reduction and Reclamation
Rule proposes requirements for the use
of recycled HFCs for the initial charge
(i.e., installation) and/or servicing in fire
suppression systems generally, but not
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75923
onboard aerospace fire suppression
systems as long as the application
continues to be eligible for ASAs. If this
requirement is finalized as proposed,
this could decrease the demand for
virgin HFC–227ea.
EPA also analyzed the supply of the
other HFCs currently used in this
application to determine whether
supply of those HFCs was also
insufficient to accommodate the
application. HFC–236fa is used in
portable extinguishers in commercialderivative aircraft. There is currently
one producer in the United States of
HFC–236fa, however, there was no
domestic production reported in 2022.
Globally, HFC–236fa is produced in
even smaller quantities than HFC–
227ea. In 2022, there were seven entities
that imported HFC–236fa with the total
amount of imports equaling 301.4 MT.
Overall, HFC–236fa made up less than
0.2 percent of all U.S. HFC consumption
in 2022 on a mass basis. At the end of
2022, suppliers held 127.5 MT of HFC–
236fa in domestic inventory, which is
equivalent to about 47 percent of
calculated consumption of HFC–236fa
in 2022; as noted for HFC–227ea and
other HFCs discussed in this preamble,
not all of this inventory may be
considered available supply (see Section
IV.B for more information). While
onboard aerospace fire suppression
allowance holders have not used
allowances for HFC–236fa to date,
allocated ASAs for this application in
2024 are equivalent to 0.3 percent of
calculated consumption of HFC–236fa
in 2022. However, similar to the
analysis for HFC–227ea, given the
relative size of the market for HFC–
236fa and the limited number of
producers in the United States and
abroad, the supply chain for HFC–236fa
is potentially more fragile than other
supply chains (e.g., HFC–134a). This
makes it more likely that the supply of
HFC–236fa available from chemical
manufacturers will be insufficient
during 2026–2030 for this application.
Also, if finalized as proposed, the
Emissions Reduction and Reclamation
Rule (88 FR 72216, October 19, 2023)
could result in similar changes for HFC–
236fa as previously discussed with
HFC–227ea.
HFC–125 is used in engine nacelles
and APUs in military use. HFC–125 is
one of the most widely produced HFCs
in the world with multiple producers in
the United States and globally. In 2022,
U.S. production of HFC–125 totaled
19,175.7 MT, comprising 14 percent of
U.S. HFC production on a mass basis. In
addition, there were 19 entities that
imported HFC–125 with the total
amount of imports equaling 23,849 MT.
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Overall, HFC–125 made up
approximately 25 percent of total U.S.
HFC consumption in 2022 on a mass
basis. At the end of 2022, suppliers held
56,208.2 MT of HFC–125 in domestic
inventory, which is equivalent to about
141 percent of calculated consumption
of HFC–125 in 2022; for reasons
explained elsewhere in this preamble,
not all of this inventory may be
considered available supply. Allocated
ASAs for this application in 2024 are
equivalent to 0.0059 percent of
calculated consumption of HFC–125 in
2022. The 2023 Technology Transitions
Rule (88 FR 73098, October 24, 2023) is
restricting the use of HFCs and HFC
blends above certain GWP limits in a
number of sectors and subsectors as
early as 2025. In all likelihood, demand
for certain blends containing HFC–125
will decrease. However, given HFC–125
could be used in lower-GWP blends,
including blends with GWPs that are
less than the relevant GWP limits, there
is uncertainty regarding how HFC–125
demand will be impacted. A reduction
in demand for HFC–125 in the
refrigeration and air conditioning
sectors could result in an increase in
available supply for use in fire
suppression equipment.
lotter on DSK11XQN23PROD with PROPOSALS2
3. What is EPA proposing regarding
eligibility for application-specific
allowances?
EPA is proposing to renew the
eligibility of entities using regulated
substances for onboard aerospace fire
suppression to receive ASAs for the
five-year period of calendar years 2026
through 2030. EPA is proposing to
determine ‘‘that the requirements
described in subclauses (I) and (II) of
clause (i) are met’’ in accordance with
the requirements of 42 U.S.C.
7675(e)(4)(B)(v)(II). Specifically, for the
reasons outlined earlier in this section,
EPA is proposing to determine that no
safe or technically achievable substitute
will be available for onboard aerospace
fire suppression and that the supply of
the regulated substance that
manufacturers and users are capable of
securing from chemical manufacturers
is insufficient to accommodate onboard
aerospace fire suppression through
calendar year 2030. As explained
earlier, EPA is proposing to determine
the supply criterion is met if supply of
one HFC used by the application is
insufficient to accommodate the
application. EPA proposes to determine
that the supply of HFC–227ea and the
supply of HFC–236fa are insufficient to
accommodate the application for the
reasons outlined in the prior section.
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VI. What are the proposed
requirements associated with a petition
to be listed as an application that will
receive application-specific
allowances?
The Agency is proposing a procedural
framework for a petition filed pursuant
to 42 U.S.C. 7675(e)(4)(B)(ii) requesting
the designation of an application as
eligible for ASAs. Subsection
(e)(4)(B)(ii) outlines requirements that
apply if the Administrator receives a
petition requesting consideration of
eligibility for ASAs. In the event a
complete petition is received, the
Agency would make a determination on
whether to designate the application as
eligible for ASAs after considering the
criteria listed in 42 U.S.C.
7675(e)(4)(B)(i). The AIM Act specifies a
timeline by which the Agency must
consider these petitions. Within 180
days, the Agency must make the
complete petition available to the public
and propose and seek comment on
whether to designate the application as
eligible for ASAs and if so, the requisite
number of allowances. Within 270 days
of receiving the petition, the Agency
must take final action on the petition.
In order to have sufficient information
to evaluate a petition based on the
criteria in subsection (e)(4)(B)(i), EPA is
proposing to require that certain
information must be included in order
for a petition to be considered complete.
The Agency envisions that petitions
could be submitted by a single entity,
such as a company or trade association,
or a group of entities. The information
listed as required is not meant to be a
comprehensive list of what a petition
may include, but rather a minimum
threshold after which the Agency would
consider a petition complete. EPA
would only consider the statutory
timeline triggered upon the filing of a
complete petition. If the Agency were to
receive a petition that did not include
all required elements listed in this
section, EPA proposes that it would
consider that petition incomplete. In the
event that an entity filed an incomplete
petition, EPA would notify that entity
that their petition was incomplete, but
not process the petition any further.
After a petition is submitted, if the
petitioner supplements the petition,
EPA would consider the petition to be
re-submitted, and the statutory
timelines for action would restart. New
information may fundamentally alter
the merits of a petition and therefore
EPA would have to restart its review in
order to account for new information
holistically. Comments on EPA’s
proposed determination would not
restart the statutory timelines unless the
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petitioner formally requested to
supplement or revise their petition.
EPA proposes that a complete petition
must include, at a minimum:
• A description of the application,
including an explanation of what the
application is, what purpose or function
it achieves, and what populations or
commercial products benefit from the
application;
• A list of regulated substances and
description of their use in the
application and an explanation as to
why HFCs are required in the
application;
• Evidence that no safe or technically
achievable substitute, including not-inkind technologies, is or is expected to be
available, and that the petitioner has
conducted research to evaluate
substitutes for the HFC(s). Examples of
evidence that may be accepted include,
but are not limited to, third-party
analyses and technical reports by
recognized experts in the field, test
results evaluating potential substitutes
on safety and technical achievability,
decisions by EPA to list alternatives
under the SNAP Program, or Federal
regulatory standards that inhibit the
ability of the application to transition to
a substitute;
• Evidence that supply of the
regulated substance(s) used in the
application is insufficient to
accommodate the application. Examples
of evidence that may be accepted
include, but are not limited to, signed
and notarized communication from
responsible corporate officers at
multiple representative suppliers and
potential suppliers for the sector or
related sectors that the application falls
in stating that the currently used HFCs
cannot be sourced; signed and notarized
communication from responsible
corporate officers at 10 or more
allowance holders, including at least
three of the 10 largest consumption
allowances holders, stating that the
currently used HFCs cannot be sourced;
• A signed certification from a
responsible corporate officer at the
requesting entity that the application
cannot use recovered and reprocessed
HFCs in conjunction with or in place of
virgin HFCs, either due to demonstrated
lack of technical achievability or
insufficient supply, and an explanation
and evidence documenting why
recovered and reprocessed HFCs cannot
be used for the application;
• Total quantity (in kg) of all
regulated substances acquired for the
application specified in the petition in
each of the previous three years,
including a copy of the sales records,
invoices, or other records documenting
that quantity; if multiple entities are
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submitting a joint petition, they must
each provide EPA with unaggregated
entity-specific information, which may
be transmitted jointly or individually;
• The name of the entity or entities
supplying regulated substances for and
contact information for those suppliers
over the past three years; if multiple
entities are submitting the petition, they
must each provide this information
individually to EPA;
• Total quantities (in kg) of regulated
substances held in inventory as of the
date the petition is submitted; if
multiple entities are submitting the
petition, they must each provide this
information individually to EPA;
• An estimate of the total quantity of
HFCs the petitioner expects to purchase
in the first year it would be eligible for
ASAs;
• Data on the proportion of the
overall cost of the product or system
that reflects the cost of regulated
substances; if multiple entities are
submitting the petition, they must each
provide this information individually to
EPA;
• Historic and projected sales of the
product or system; if multiple entities
are submitting the petition, they must
each provide this information
individually to EPA;
• Evidence of research into design
changes to decrease the amount of HFCs
used in the product or system;
• An explanation regarding whether
the use of the regulated substance is
necessary for the health, safety, or is
critical for the functioning of society
(encompassing cultural, intellectual,
and economic aspects);
• An explanation regarding steps
taken to minimize the use of the
regulated substance and any associated
emission of the HFC(s); and
• Information on regulatory
restrictions related to possible
alternatives and substitutes.
Requiring minimum information be
included in order for the Agency to
deem a petition complete and process
that petition would help provide clarity
for the Agency and ensure timeliness
and transparency for the petitioner. If
EPA does not take this approach, it
could prevent EPA from having
sufficient data to determine whether the
application warrants receiving ASAs
and would unnecessarily delay a
response from the Agency. This would
mean that a petitioner would have to
wait longer to re-submit a petition if a
necessary element were omitted from
the original submission. EPA seeks
comment on the proposed petition
process, including all of these proposed
elements and the associated burden
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with providing such information to the
Agency.
In addition to proposing to establish
required elements of a complete
petition, EPA is providing a nonexhaustive list of other elements that are
optional, but the Agency may find
compelling or helpful in making a
determination on a petition:
• Market research on the application,
which could include: an estimate of the
number of domestic entities within the
application; an estimate of the amount
of bulk HFCs used domestically within
the application; an estimate of the
projected annual growth rate for the
duration of the period for which the
application is seeking eligibility to
receive ASAs, with supporting evidence
by third-party sources;
• Economic research on the elasticity
of demand for products or systems
within the application, with supporting
evidence by third-party sources;
• Research on whether products or
systems in the application outside of the
United States have had success in
transitioning to substitutes or otherwise
reducing use of HFCs;
• Other information that may be
relevant as the Agency evaluates the
petition, based on the factors listed in
subsection (e)(4)(B)(i).
EPA notes that for an entity to be
eligible to receive ASAs in a given
calendar year, a complete petition
should be submitted no later than
January 31 two calendar years prior to
provide the Agency sufficient time to
review a petition and be able to issue
allowances in advance of the statutory
deadline of October 1 each year. For
example, if an entity would like to
receive allowances in calendar year
2027, the entity should submit a
complete petition no later than January
31, 2025. EPA is setting this clear
expectation so entities can factor this
into their planning when deciding to
petition EPA to be added to the list of
eligible applications. This proposed
timeline would allow the Agency the
requisite time to review and take final
action on the petition, consistent with
the statutory timeline in subsection
(e)(4)(B)(ii), and also issue a final rule to
effectuate that decision in 40 CFR 84.13.
EPA proposes to allocate allowances
to entities in a new application through
the same manner as other entities
receiving ASAs, per 40 CFR 84.13 and
40 CFR 84.31(h). EPA contends that
allocating allowances based on the
established regulatory approach would
be the fairest and most transparent
method of determining allowance
allocations for entities in a new
application. While EPA is proposing
that a petition be required to include
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some of the information that would be
necessary to determine an allowance
allocation, it is possible that not all
entities within an application would be
involved in the submission of the
petition. In other words, having entities
within a new application request ASAs
by July 31 like all other applications
(per 40 CFR 84.13(b)) would ensure that
all entities in a new application have
equal opportunity to request
allowances. This may mean that in cases
where there is a final rule pending to
add an application to the list of entities
eligible for ASAs at 40 CFR 84.13, any
entity wishing to be eligible for ASAs in
the next calendar year would need to
provide the information required at 40
CFR 84.13(h)(2) by July 31.
EPA proposes that if a petition is
granted and a new application is listed
as eligible to receive ASAs, that
eligibility would apply until the end of
the five-year review cycle during which
its petition was granted. Per subsection
(e)(4)(B)(v), EPA must review each ASA
use receiving an allocation of
allowances not less frequently than once
every five years. EPA proposes that, at
the end of each five-year review cycle,
it will review any applications listed in
40 CFR 84.13(a) at the time of review,
regardless of how they were initially
included on the list. For example, the
five-year review period covered in this
proposed rule includes calendar years
2026 through 2030. If a petition were
granted to receive ASAs starting for
calendar year 2028, that application
would be eligible for calendar year
2028, 2029, and 2030 allowances, and
then EPA would review the eligibility
for that application to continue
receiving ASAs starting with calendar
year 2031 allowances.
Consistent with the reporting
requirements under 40 CFR 84.31(a),
EPA is proposing that all reports,
petitions, and any related supporting
documents must be submitted
electronically in a format specified by
EPA; 29 and quantities of regulated
substances must be stated in terms of
kilograms unless otherwise specified.
EPA is proposing that these records and
copies of reports required by this
section must be retained for three years.
VII. Proposed Revisions to Existing
Regulations
EPA finalized an approach under the
Allocation Framework Rule for issuing
ASAs for the initial years after
enactment of the AIM Act. EPA set up
a framework to determine ASA
29 Currently, most HFC reports under the AIM Act
are submitted through the HAWK module in the
electronic Greenhouse Gas Reporting Tool (eGGRT).
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allocations for calendar years 2022
through 2025 for five of the six
applications identified in the AIM Act:
propellants in MDIs; defense sprays;
SCPPU foam for marine use and trailer
use; etching of semiconductor material
or wafers and the cleaning of CVD
chambers within the semiconductor
manufacturing sector; and onboard
aerospace fire suppression. As
explained in more detail in the
Allocation Framework Rule, EPA
allocates ASAs differently for MCMEU,
given the complex nature of the way
DOD sources and uses HFCs in the
mission-critical context (86 FR 55116,
55153, October 5, 2021).
The 2024 HFC Allocation Rule did
not reopen the methodology for issuing
ASAs but noted that the Agency had
begun development of this proposed
rule to review and consider whether to
renew eligibility for each of the six
applications for ASAs and would herein
consider revisions to existing regulatory
requirements (88 FR 46836, 46840, July
20, 2023). As EPA foreshadowed in the
2024 HFC Allocation Rule, the Agency
is proposing targeted regulatory changes
after considering whether any changes
should be made to the existing
regulatory requirements governing
ASAs based on implementation over the
past several years. EPA is also proposing
one specific regulatory change to clarify
how EPA’s regulations would apply to
any illegally imported HFCs that are
seized and auctioned by enforcement
officials, proposing to require exporting
companies to report ITNs quarterly, and
proposing to simplify the ‘‘date of
purchase’’ requirement for a RACA.
Under the current regulations
established in the Allocation
Framework Rule, EPA issues ASAs
based on multiplying the company’s
HFC use in the prior year by the higher
of:
Æ The AAGR of use for the company
over the past three years; or
Æ The AAGR of use by all entities
requesting that type of ASA (e.g., for
MDIs) over the past three years.
For the calculation of AAGR, EPA
calculates the growth rate between the
first and second year plus the growth
rate between the second and third year,
divided by two. The formula is as
follows:
(( Application or Entity HFC Purchases in Year 2 _ 1) + (Application or Entity HFC Purchases in Year 3 _ 1))
Application or Entity HFC Purchases in Year 1
Application or Entity HFC Purchases in Year 2
EPA relies on activity from July 1 to
June 30 for each of the three preceding
years prior to the annual allocation
because of the biannual reporting
deadlines and to include the most
recent year of data prior to the October
1 allocation deadline in the allowance
allocation determinations. EPA
established the information an entity
requesting ASAs must provide in 40
CFR 84.31(h)(2). EPA is proposing to
codify the existing practice such that
entities reporting on or applying for
ASAs provide supporting
documentation to verify reported data
on total quantities of HFCs acquired
through conferring allowances,
expending allowances for direct import,
purchases without expending
allowances, and quantity held in
inventory.
EPA also established that the Agency
would consider unique circumstances
that are not reflected by the rates of
growth calculated in the methodology
outlined above that are also factually
documented when determining
allowance allocations. EPA finalized the
following circumstances as potentially
meriting an increased allocation to an
individual company beyond historical
growth rates: (1) additional capacity will
come on line in the next year, such as
a new manufacturing plant or expanded
manufacturing line, (2) a domestic
manufacturer or some of its
manufacturing facilities has been
acquired, and (3) a global pandemic or
other public health emergency increases
demand for use of HFCs in an
application, such as an increase in
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patients diagnosed with medical
conditions treated by MDIs. These
scenarios could provide reasons to
increase allowance allocations to
affected companies in the affected years.
Furthermore, if a company wanted to
make a claim that it qualifies for
individualized treatment due to one of
these unique circumstances, the
company must sufficiently document in
a verifiable way why it qualifies.
Specific documentation includes, but is
not limited to, recent invoices for new
tools; permit documentation for new
facilities, facility expansion, or
installation of equipment related to
retooling; agency or company press
releases for the launch of new products;
or Securities and Exchange Commission
filings documenting facility acquisitions
or expansions. Ultimately,
accommodating unique circumstances
that are fully documented and proven
help the Agency fulfill Congress’s
mandate that EPA ‘‘allocate the full
quantity of allowances necessary’’ (86
FR 55116, 55151, October 5, 2021). As
a result of the multiple allocations
between 2021 and 2023 and the lessons
learned through this process, EPA is
now proposing limited changes to these
existing regulations.
Specifically, EPA is proposing: to
require companies provide the total
expected amount of HFCs they intend to
purchase in the calendar year, to expand
permissible scenarios that could qualify
as unique circumstances, a different
allocation methodology for certain very
small users of HFCs and entities with
irregular purchasing history, how to
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account for inventory in allocation
decisions, new requirements for
conferrals of MCMEU allowances, to
establish a pool of set-aside allowances
for situations that meet the criteria for
unique circumstances related to medical
conditions treated by MDIs, and to
allow ASA holders to return a portion
of their allowances voluntarily if they
do not intend to use them. EPA is
proposing other specific regulatory
changes to: clarify how EPA’s
regulations would apply to any illegally
imported HFCs that are seized and
auctioned by enforcement officials,
require exporting companies to report
ITNs quarterly, and simplify the ‘‘date
of purchase’’ requirement for a RACA.
A. Expected Total HFC Purchases
Under EPA’s current program, entities
may voluntarily state the total amount
of HFCs they expect to purchase for the
next year. EPA has encouraged entities
to provide this data on a voluntary basis
to provide an additional data element
for the Agency to consider in making
allocation decisions.
EPA proposes to amend the
regulations to require all entities to
provide their total expected HFC
purchases for the next calendar year as
a component of overall applications due
July 31 for ASAs for the following
calendar year. Under this proposed
requirement, entities would be required
to provide an estimate of the total
quantity of HFCs they expect to
purchase next year based on their
expected eligibility for allowances. EPA
will allocate at that level if it is lower
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than what that entity is eligible for
based on the regulatory formula.
EPA is proposing this approach to
better understand each entity’s HFC
needs in the next year. The regulatory
allocation methodology established in
the Allocation Framework Rule, and
outlined at the start of this section, is
designed to determine an allocation
based on ‘‘projected, current, and
historical trends.’’ However, this
formula may not fully take into account
other considerations that could impact
an entity’s HFC needs in the next year.
This proposed approach may also avoid
overallocation at the expense of general
pool allowance holders.
B. Unique Circumstances
Under EPA’s current regulations,
entities may request that EPA consider
unique circumstances that are not
reflected by the rates of growth
calculated. Entities ‘‘must provide
additional information if requesting that
EPA consider unique circumstances’’
under 40 CFR 84.13(b)(1). EPA is
proposing to codify into the regulations
the Agency’s existing practice of
requiring entities to provide supporting
documentation to verify any claimed
need. EPA previously codified three
situations that would be considered as
unique circumstances (40 CFR
84.13(b)(1)). After multiple allocations
and many conversations with
stakeholders, EPA is proposing to add to
the list of unique circumstances under
which EPA may allocate additional
allowances beyond what is calculated
from the regulatory allocation formula.
EPA is also proposing to broaden the
third unique circumstance related to
MDIs.
First, EPA is proposing to create a
unique circumstance for economic
disruption outside the immediate
control of the entity applying for ASAs,
such as an economy-wide recession or
other documented short- to mediumterm market events that negatively
impact a company’s operations, such as
a strike that affects product demand or
supply chain disruption. EPA proposes
to consider this situation as a unique
circumstance as such an event could
lead to an increased need to purchase
HFCs beyond what is reflected in the
regulatory formula, but likely would not
be captured under an existing scenario
that EPA would consider as an
acceptable unique circumstance. If
finalized, entities would still have to
submit documentation that verifies that
this situation has taken place, the
current status of the market event (e.g.,
whether it has concluded and demand
for the HFCs has returned), and that this
situation has materially impacted an
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entity’s HFC needs. The entity would
also have to provide supporting
documentation to justify the projected
amount of HFCs needed, including
explaining how projections compare to
pre-market event use.
EPA is also proposing to add building
a stockpile of a specific HFC as a
scenario which EPA would consider a
unique circumstance in the event a
major producer for an application
announces they will be ceasing
production of the HFC used by the
application-specific entity in the near
future. An entity could request
additional allowances for the purpose of
building inventory ahead of the cease in
production. For an entity to be eligible
for additional allowances under this
unique circumstance, EPA proposes that
the entity must provide EPA with a
letter from their supplier signed by a
responsible corporate officer 30 stating
that the supplier is ceasing all
production of the HFC at issue within
three years. Further, EPA proposes that
an eligible entity must certify that they
have regulatory requirements beyond
the 40 CFR part 84 requirements that
limit its ability to switch suppliers or
there are no other suppliers that could
meet their needs (e.g., because there no
other chemical manufacturers that can
supply the needed HFC). EPA proposes
to also require evidence that the entity
has a restricted HFC supply chain, such
as required purity requirements. If
additional allowances were granted
because of this requested unique
circumstance, EPA proposes to require
reporting specific to the building of
inventory by the entity that would be
allocated ASAs in advance of their
supplier’s production facility ceasing
production. Such inventory buildup
must be held by the entity that is
allocated allowances, and EPA would
subtract those quantities from the
entity’s purchase history such that it is
not included in the regulatory formula
to determine the entity’s allocation the
following year.
EPA is also proposing to expand the
scope of the unique circumstance for a
global pandemic or other public health
emergency that increases patients
diagnosed with medical conditions
treated by MDIs to include ‘‘healthcare
system needs.’’ EPA notes that the
reference in the regulations to an ‘‘other
30 EPA is also proposing to define this term,
which is used elsewhere under the HFC Allocation
Program. For purposes of 40 CFR part 84, subpart
A, EPA is proposing that responsible corporate
officer and responsible official mean a person who
is authorized by the regulated entity to make
representations on behalf of, or obligate the
company as ultimately responsible for, any activity
regulated under 40 CFR part 84, subpart A.
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public health emergency’’ is not limited
to situations where the Department of
Health and Human Services (HHS) has
officially declared a public health
emergency. The proposed expansion of
the unique circumstance is a direct
outgrowth of experience over the past
three years of implementing the
phasedown and is designed to ensure a
sufficient volume of HFCs is available to
manufacture MDIs to treat asthma,
chronic obstructive pulmonary disease,
and other respiratory diseases when
unexpected market events occur.
EPA proposes to define a healthcare
system need as circumstances where an
increase in demand for MDIs used to
treat asthma, chronic obstructive
pulmonary disease, and other
respiratory diseases may occur because
of a change in market conditions that
otherwise would not be included in
calculated rates of growth. If finalized,
EPA intends to consult closely with the
FDA and potentially HHS more broadly
before allocating allowances for
‘‘healthcare system needs.’’
Examples of the types of events that
could fall into a healthcare system need
include, but are not limited to:
• A manufacturer that makes MDIs
outside of the United States stops
selling approved MDI products in the
United States;
• Major recall or suspension of
production of alternative (non-MDI)
emergency asthma treatments
prompting increase in MDI demand;
• Change in preferred products from
pharmacy benefit managers or State
Medicare programs to patients;
• FDA compliance or enforcement
actions that impact MDI market
dynamics by reducing availability of
generic drug products that;
• Significant increase in respiratory
infections in general population (e.g.,
respiratory syncytial virus (RSV),
coronavirus disease (COVID)); and
• Decrease in availability of active
pharmaceutical ingredient or device
component for one or more MDI
manufacturers causing a supply
shortage.
C. Methodology for Entities With
Irregular Purchasing History and Very
Small Users
EPA has observed that there are
certain entities with purchase patterns
for which the regulatory formula either
is not able to calculate an allocation or
applying the terms of the regulatory
formula would produce absurd results.
For these entities, EPA is proposing an
alternative approach for calculating the
quantity of allowances each entity is
eligible to receive. Specifically, EPA is
proposing to create an alternative
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method of allocating to entities that are
either of the following: (1) Entity has
small purchases of HFCs (<100 kg) at
least one of the last three years where
their purchase history would result in
200 percent or higher AAGR of use for
the company over the past three years,
or (2) entity’s growth rate cannot be
calculated because it had zero purchases
in one of the last three years for reasons
other than newly using HFCs. For
entities that fall into either category, the
Agency is proposing to allocate the
highest, as measured in exchange value
equivalent (EVe), verified purchase
amount in the last three years.
With respect to the first category, EPA
is proposing these cutoff numbers to
allow for some narrow flexibility in an
entity’s purchasing patterns and to
recognize the variability for entities that
purchase relatively small quantities of
HFCs. EPA is proposing to move away
from applying the existing regulatory
formula for entities where a relatively
small fluctuation in purchasing
measured on a mass basis would result
in an extraordinarily large and
nonsensical growth rate. EPA reviewed
data from the past three October 1
allocation cycles and found that the top
three highest entity-specific AAGRs
from each of the allocation cycles
ranged from about 125 percent or
higher, with the lowest ‘‘small use’’ of
HFCs in a particular year of less than 5
kg. Thus, the Agency is proposing 200
percent as the AAGR cutoff and less
than 100 kg as the ‘‘small use’’ cutoff.
For the second category, it is
mathematically impossible to calculate
a growth rate based on zero purchases
in a year under EPA’s existing
regulatory formula. Entities that had
zero purchases in one of the three years
under consideration would also have to
be determined to be an active purchaser
prior to a year with zero purchases. It
is not EPA’s intent to capture entities
that are new in an application under
this alternative pathway.
EPA is separately proposing a
different allocation approach for all very
small purchasers of HFCs. EPA is
proposing to define entities in this
category as anyone whose HFC
purchases add up to less than 100 kg in
each of the previous three years. The
Agency recognizes there are certain
entities that purchase the same small
quantities of regulated substances every
year who may not follow a growthoriented use similar to that of entities
that use HFCs in wide-scale,
commercial operations. Examples of
these uses could include those meant
for small batch use in one of the eligible
applications for research and
development and/or entities that may
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not yet be manufacturing commercially
if, for example in the case of MDIs, the
entity is still in the product
development phase, is only
manufacturing small numbers of MDIs
(e.g., for clinical trials), and is waiting
for final FDA approval. For these
entities, EPA proposes to allocate the
highest, determined on an EVe basis, of
an entity’s past three years’ worth of
purchases, since their use stays
relatively consistent over time. EPA is
taking comment on whether the Agency
should look back further at up to five
years’ worth of purchase history. EPA
based this number on the past three
October 1 allocation cycles, and
reviewed purchasing patterns for the
smallest purchasers who are not new to
the HFC market and would not be
considered entities with irregular
purchase histories. EPA is taking
comment on the cutoff threshold on
what size purchases would allow for an
entity to be considered a ‘‘small user.’’
EPA is also soliciting comment on
whether, combined with this approach
or as an alternative to this approach,
EPA should round allowance
allocations for very small purchasers to
account for purchase of a specific
cylinder volume. In order to take this
approach, EPA requests comment on the
typical cylinder volume sizes used in
these small purchases. EPA would also
require eligible applicants to provide
information on the cylinders being
purchased in their biannual reporting.
D. Average Annual Growth Rate
Calculations
EPA currently calculates AAGR on an
MTEVe basis. This process involves
converting the mass (e.g., kilogram) of
each HFC into MTEVe and summing
those MTEVe quantities across each
year, before applying the AAGR formula
described earlier in this section. The
Agency is providing courtesy notice of
a change going forward to calculate
AAGR on a mass basis. This new
process would be based on summing all
HFCs together for each year to get a total
quantity based on mass and using this
mass quantity in the AAGR formula.
AAGR calculations are not codified in
the regulations, so this is not a
regulatory revision, but EPA is
providing this notice given broader
methodology changes proposed in this
rulemaking.
EPA is modifying this calculation
because we are concerned that as
entities transition to lower-GWP HFCs,
an AAGR calculated on an MTEVe basis
will not appropriately reflect their
projected demand for HFCs in the
upcoming calendar year. For example,
under an MTEVe-based AAGR
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calculation, an entity transitioning to a
lower-GWP HFC, which has an
associated lower EV, could have a
negative AAGR while simultaneously
experiencing a growth in actual HFC
usage. In this situation, the entity would
be allocated an amount of allowances
lower than its current year’s HFC use.
While entities will require fewer
allowances to purchase these lowerGWP HFCs, until a company has a full
three years of purchase data with this
lower-GWP HFC, the calculated
allowances may be substantially less
than projected demand, either
increasing by too small an amount or in
some cases declining despite an actual
increase in demand. It would be a
perverse outcome for entities to receive
an insufficient HFC allocation because
they are transitioning to a lower-GWP
alternative.
In addition, growth calculated on a
mass basis is more reflective of demand
than MTEVe and is not impacted by any
potential swings resulting from
purchasing differing levels of HFCs with
different EV values each year. For
example, a company purchasing 20 kg
of HFC–41 in one year and 40 kg of
HFC–23, which has an EV
approximately 160 times that of HFC–
41, the following year would have the
same growth rate as a company
purchasing 20 kg of HFC–41 in one year
and 40 kg of HFC–41 the next year (i.e.,
the growth rate for that year is 100
percent for both companies versus
32,000 percent for the first company and
100 percent for the second company).
E. Inventory
EPA’s current regulations require
entities receiving ASAs to provide, as
part of their biannual reporting
requirements, information on the
quantities of HFCs left in their inventory
at the end of the previous six-month
reporting period (40 CFR
84.31(h)(1)(iv)). Upon finalization of
this rulemaking and heading into the
allocation of calendar year 2026
allowances, EPA will have several years
of data on inventory, including how
inventory levels have changed over
time. In the Allocation Framework Rule,
EPA noted its intent to account for
changes in inventory in the allocation of
ASAs (86 FR 55116, 55152, October 5,
2021).
EPA is proposing to include verified
changes in inventory into the
calculation of the quantity of HFCs an
entity used over the 12-month period for
all allocations except MCMEU. Changes
in inventory are documented
information as to how an entity used
HFCs in a particular year. For example,
if an entity purchased 100 kg of HFCs,
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and their inventory grew by 50 kg, this
would suggest that the entity used 50 kg
in the manufacturing process under the
applicable application. In this instance,
consideration of purchases minus
inventory buildup is a more accurate
reflection of HFC use by the entity than
HFC purchases would be alone. EPA
proposes to factor in both drawdown
and growth in inventory; a drawdown of
inventory would be added to HFC
purchases and a buildup of inventory
would be subtracted from HFC
purchases.
EPA is proposing that this approach
would not apply to calculation of
MCMEU allowance allocations because
DOD has a history of building up
inventory and may need to do so for
mission-critical or national security
purposes. The Agency acknowledges
that building inventories can be an
important strategy for other entities to
navigate changing market conditions,
especially in advance of the 2029
reduction step. Therefore, as part of this
proposal, EPA is also including that
entities may provide a rationale as to
why a buildup in inventory should not
be subtracted from the quantities of
HFCs they annually acquire. An
example of what the Agency would
consider to be acceptable rationale
would be if a producer announced that
they would be ceasing production of an
HFC that is used in a particular
application, and the entity wanted to
build up inventory of that HFC to
continue manufacturing of their product
while they figured out their transition
timeline. Another example could
include a situation where an entity had
to purchase a minimum volume (e.g., a
full ISO tank) and that last purchase
resulted in an increase in inventory.
In the alternative, EPA is proposing to
not incorporate small amounts of
growth in inventory in allocation
decisions. EPA would propose to define
a small amount of growth as below 20
percent or, alternatively, growth in
inventory for only a single year. EPA
invites comment on this alternative
pathway and also what the Agency
should consider to be a small amount of
inventory growth.
F. Department of Defense Conferrals
In the Allocation Framework Rule,
EPA finalized that anyone conferring an
ASA, except for the conferral of
allowances for MCMEU, would be
required to submit information about
each conferral prior to conferring
allowances (40 CFR 84.31(h)(4)). While
DOD was not required to submit
conferral information to EPA, DOD was
required to maintain records
documenting the conferral(s) of ASAs to
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other entities up to and including the
producer or importer of the chemical
(40 CFR 84.31(h)(7)(iv)).
In order to ensure that certain imports
are not delayed or denied, EPA is
proposing to modify the 40 CFR part 84,
subpart A regulations to require that
DOD report information consistent with
the required reporting of conferral data
from all other ASA holders. This would
include the identity of each conferrer
and conferee and the quantity in MTEVe
of ASAs being conferred. This proposed
regulatory change would not be a
significant burden for DOD because
DOD is already required to track this
data internally (40 CFR 84.31(h)(7)).
If finalized, this regulatory revision
would bring the process for conferring
MCMEU allowances in line with other
entities receiving ASAs. The Allocation
Framework Rule noted that one of the
goals of this requirement was ‘‘to ensure
EPA has the requisite information to
track application-specific allowances’’
(86 FR 55116, 55189, October 5, 2021).
When an HFC supplier reports to EPA
that they have expended ASAs other
than MCMEU allowances, conferral
reports have allowed EPA to confirm
whether that supplier was in possession
of ASAs. With MCMEU allowances,
given that DOD is not required to share
information about the conferral of
MCMEU allowances with EPA, the
Agency has encountered difficulty
verifying whether suppliers are in
possession of MCMEU allowances. EPA
is particularly concerned that without
conferral information for MCMEU
allowances, the Agency would
recommend that U.S. Customs and
Border Protection (CBP) deny entry of
an import of HFCs bound for MCMEU.
This could cause unnecessary delays for
DOD and extra costs for importers.
Different reporting requirements for
MCMEU allowances has resulted in
unexpected confusion and delays in the
approval of some producer and/or
importer quarterly reports, increasing
administrative burden for DOD, entities
who are producing and importing on
behalf of DOD, and EPA. If finalized,
this regulatory change would help
address these issues.
In addition to bringing the process for
conferring MCMEU allowances in line
with other entities receiving ASAs, EPA
is proposing one additional requirement
for the conferral of MCMEU allowances,
per a request from DOD. To enable
clearer tracking of MCMEU allowances
from initial conferral to expenditure,
EPA is proposing to require that a
certificate number, generated by DOD,
be reported to EPA for each conferral
and expenditure of MCMEU allowances.
For example, if an intermediary receives
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a conferral of MCMEU allowances from
DOD and then confers the allowances
further to a supplier, both DOD and the
intermediary must report the same
certificate number as part of the
conferral. Finally, when the supplier
expends the conferred MCMEU
allowances for production or import of
HFCs, the supplier must report the
certificate number in the same report in
which the expenditure of MCMEU
allowances is reported. This additional
layer of tracking conferrals could further
relieve any unexpected confusion.
G. Limited Set-Aside for Unique
Circumstances Related to MDIs
Some stakeholders have expressed
concern that an annual allocation
decision is not always sufficient to meet
the needs of the entities eligible for
ASAs. Entities have noted that
unanticipated events may arise after
July 31, when requests for ASAs are
due, that legitimately necessitate an
increased need to purchase more HFCs
than expected. EPA received a comment
to the Allocation Framework Rule (86
FR 55116, October 5, 2021) requesting
that EPA create a separate additional
pool of allowances to accommodate
growth, new mid-year entrants, and
‘‘under-allocation.’’ At the time of that
rulemaking, EPA determined that
establishing such a pool of allowances
was unnecessary because the Agency
had set up an allocation formula to
allocate the full quantity of allowances
necessary, and setting allowances aside
just in case they were needed would
reduce the allowances available to
general pool allowance holders thereby
reducing how many HFCs can be
imported or produced if the set-aside
allowances went unexpended. EPA also
noted that a company can access HFCs
from the open market; if a company
used more HFCs in a given year, that
increased use would be reflected in the
next year’s allocation. However, EPA
also noted that the Agency would learn
from implementation of the program
and consider adjusting the methodology
(86 FR 55116, 55151, October 5, 2021).
Based on the Agency’s observations in
implementing the ASA allocations over
the past three years, EPA is proposing
to create a set-aside of allowances
specifically for situations that meet the
criteria for the unique circumstance
established in 40 CFR 84.13(b)(1)(iii),
including the proposed changes
described in Section VII.B of this
preamble. In other words, this would be
a set aside to accommodate unforeseen
need for regulated substances related to
a global pandemic, other public health
emergency, or other healthcare system
needs related to increased patients
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diagnosed with medical conditions
treated by MDIs. EPA still sees
significant downsides to creating a setaside of allowances for unforeseen
demands in the eligible applications as
outlined in the Allocation Framework
Rule, but does see benefit in creating a
set-aside for the singular narrow
possibility of a public health emergency
or other unforeseen event that would
specifically affect availability of MDIs.
As a result, EPA is proposing to set
aside allowances that would be
available for the use of HFCs as a
propellant in MDIs if the requester
meets the criteria for the unique
circumstance as defined in in 40 CFR
84.13(b)(1)(iii). Application-specific
entities could apply to EPA for these
allowances based on a demonstrated
need to purchase more HFCs in the
present calendar year in light of events
that were unforeseen at the time of the
entity’s application for ASAs for the
calendar year at issue. For example,
during the beginnings of the COVID–19
pandemic in 2020, MDI manufacturers
purchased nearly 40% more HFC–134a
than they did in 2019, which is
substantially more than they would
have been allocated based on Year 3
purchases and the application’s AAGR;
this extra demand also could not have
been predicted in July 2019, when
manufacturers would have applied for
calendar year 2020 allowances. EPA
would consult with the FDA in
determining whether the presented
situation meets the criteria as defined,
but scenarios could include a global
pandemic. Other examples of situations
that could qualify are described in
Section VII.B. EPA is also taking
comment on whether there are other
analogous situations where an
unexpected increased need for HFCs
resulting from the other established and
proposed unique circumstances could
arise in which the facts would justify
the potential use of another set-aside for
ASA holders. If a commenter identifies
such a situation, EPA requests that the
commenter also provide information on
how EPA would appropriately cabin
requests to demand that was truly
unexpected and unforeseeable and also
information on what entities should
have to provide as evidence when
applying for set-aside ASAs. At a
minimum, it seems appropriate to
require a requesting entity to present
EPA with information on how facts have
changed that were unknowable at the
time the entity applied for that year’s
ASAs and also evidence that the entity
has been unable to acquire needed HFCs
from the open market or through
allowance transfer. EPA seeks comment
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on the appropriate records that would
need to be provided to EPA to document
the entity’s unsuccessful efforts to
acquire HFCs without additional
allowances from EPA. EPA would likely
require at least some of the records
described in Section VI of this
preamble.
EPA is presenting a series of options
for comment on how such a set-aside
pool would be created. Under Option 1,
which is EPA’s preferred option, EPA
would form this pool by setting aside 10
percent of the allocation of certain
entities—those that produced or
imported HFCs during 2011–2019 to
serve the applications eligible for ASAs,
except MCMEU. An entity that
produced or imported HFCs in the time
range of 2011–2019 for a separate entity
now receiving ASAs is getting a current
HFC allowance allocation based on
those past purchases. At the same time,
ASAs are being issued to entities for
conferral to a producer or importer. This
can be viewed as a double allocation.
For example, if Entity A imported for an
MDI manufacturer in 2011–2019, those
historic imports are included in
calculating Entity A’s allowance
allocation. In other words, Entity A is
getting a higher allowance allocation
because of their imports for an MDI
manufacturer. At the same time, the
MDI manufacturer is being allocated
ASAs, which can be conferred to Entity
A to import HFCs for the MDI
manufacturer. Therefore, Entity A has
two sets of allowances available to them
as a result of being an importer for MDI
manufacturers. Because of this aspect of
the design of EPA’s allocation system, if
EPA were to create a set-aside of
allowances for application-specific
entities, EPA proposes to hold back 10
percent of the allocation of entities that
produced and imported for applicationspecific uses during 2011–2019. This
appears more equitable than holding
back a set amount of allowances from all
general pool allowance holders, since
only those that historically imported
and produced for application-specific
uses may have two sets of allowances
now available to them. Of course,
because a company that historically
produced or imported for applicationspecific uses has two sets of allowances
available to them, it seems that they
should have sufficient production and/
or consumption allowances available to
purchase additional HFCs for an
application-specific entity if an
unexpected need arises. EPA is
soliciting comment on whether, because
of this fact, a set-aside is not truly
needed, or if a set-aside is necessary
because historic importers and
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producers are requiring conferral of
ASAs to meet the needs of applicationspecific entities.
Under this proposed Option 1
approach, EPA would withhold 10
percent of the identified entities’
allowances until April 30. If no
application-specific entity applied for
the allowances by April 30, then the
withheld allowances would be issued to
the entities from which they were
withheld. If a request is pending, EPA
would withhold allowances until that
request was evaluated and allowances
were issued. Such issuance would be
done in a proportionate fashion if some,
but not all, of the set-aside allowances
were allocated to application-specific
entities. EPA seeks comment on
whether April 30 is late enough in the
year to provide the appropriate safety
value for unforeseen public health
emergencies and other healthcare
system needs.
Alternatively, Option 2 would be that
EPA would create a set-aside pool for
application-specific entities in the event
of a public health emergency or other
healthcare system need from any
revoked allowances, including from
administrative consequences already
finalized. In the Allocation Framework
Rule, EPA created administrative
consequences whereby EPA can adjust
allowance allocations if EPA determines
that a person failed to comply with
certain requirements relating to the HFC
allowance allocation and trading
program. Under the administrative
consequence tool, a revoked allowance
is one that EPA takes back from an
allowance holder and redistributes to all
other allowance holders (86 FR 55116,
55169, October 5, 2021). Under this
second option, instead of redistributing
revoked allowances to all other
allowance holders, EPA would put the
revoked allowances into a set-aside pool
in case additional ASAs were needed as
a result of a public health emergency.
One potential flaw with this proposed
approach is that to date, entities could
expend ASAs to either produce or
import HFCs. EPA created ASAs to
function this way because end users in
the identified applications may not
know in advance how they will procure
HFCs, and this method provides
flexibility to ensure that end users
receive the ‘‘full quantity of allowances
necessary,’’ (86 FR 55148). To ensure
that these ASAs are provided within the
overall annual production and
consumption caps, EPA subtracts the
amount of ASAs allocated from both the
production and consumption general
allowance pools (40 CFR 84.9(a)(3);
84.11(a)(3)). However, to date, EPA has
only revoked consumption
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allowances.31 EPA would likely need to
hold back some amount of production
allowances under this option, up to
1,000,000 MTEVe, to ensure sufficient
allowances were available.
A third, less preferred option, would
be to hold back a set amount of
allowances. This set-aside would be
created from all general pool allowance
holders. EPA proposes that the Agency
could hold back allowances in the range
of 500,000 to 1,000,000 MTEVe
production and consumption
allowances. If no application-specific
entity applied for the allowances by
April 30, then the withheld allowances
would be issued to the entities from
which they were withheld. If a request
is pending, EPA would withhold
allowances until that request was
evaluated and allowances were issued.
As explained previously, this approach
seems less equitable than Option 1. This
approach also does not allay the
concerns identified by EPA in the
Allocation Framework Rule for
establishing a set-aside for ASAs.
However, EPA is interested in
stakeholder input regarding this option.
Finally, as an alternative to creating a
set-aside at all, EPA is taking comment
on the possibility of allowing conferral
of ASAs from other applications in the
event an unforeseen event that meets
the unique circumstance outlined in 40
CFR 84.13(b)(1)(iii). Under EPA’s
current regulations, conferred ASAs
may only be used to produce or import
HFCs for the application-specific use
associated with the allowance(s) (40
CFR 84.13(h)). Under this alternative,
EPA would amend the regulations such
that if an unforeseen event meeting 40
CFR 84.13(b)(1)(iii), ASAs could be
conferred and expended to produce or
import HFCs for application-specific use
different from the application associated
with the allowance. For example, if EPA
agreed that there was a public health
emergency that created an unexpected
need to purchase more HFCs for MDI
manufacturing, under this approach
ASAs allocated for aerospace fire
suppression could be conferred to
import or produce HFCs for use in MDI
manufacturing.
EPA seeks comment on these
proposals, in particular on the scope of
the need, the number of allowances that
are expected to need to be set aside, the
date by which requests must be received
to be considered, and all other aspects
of the proposal.
31 See https://www.epa.gov/climate-hfcsreduction/administrative-consequences-under-hfcallocation-rule.
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H. Return of Unneeded Allowances
EPA is aware that some applicationspecific entities are allocated more
allowances than are necessary to
accommodate their needs for a given
calendar year. This may be because for
that specific year, the regulatory formula
overestimated that individual entity’s
need. It is also possible that the entity’s
expectations for the year did not match
reality because of unexpected
intervening events, such as a drop in
demand for the entity’s products or
supply chain difficulties. In light of
these considerations, EPA is proposing
to allow ASA holders to return their
allowances voluntarily if they do not
intend to use them. ASA holders could
return allowances up to and including
June 30 of the year for which the
allowances can be expended (e.g.,
calendar year 2025 allowances would
have to be returned by June 30, 2025).
This would be completely optional and
intended to be used at the discretion of
the ASA holder. EPA proposes to use
any returned allowances to either: (1)
fulfill unexpected higher demand of
another ASA holder (see proposal in
Section VII.G of this preamble); or (2)
return the allowances to the general
pool of allowance holders proportionate
to respective market shares. EPA sees
benefit of redeploying allowances that
would go unused into the overall HFC
market for smoother transition and to
ease the overall HFC phasedown.
EPA is soliciting comment on this
proposal, including whether it is needed
if EPA finalizes other proposals outlined
in this notice. EPA is particularly
interested in whether this proposed
approach is needed if EPA finalizes the
requirement for entities to include in
their application for allowances their
anticipated need for the following
calendar year. EPA is also interested in
stakeholder input on whether codifying
an ability for entities to return unneeded
allowances would have unintended
negative effects, including limiting the
availability of allowances for transfer to
another application-specific entity that
has an unanticipated need for more
allowances during the calendar year.
I. Enabling Auctions of Illegally
Imported HFCs
In addition to the proposed changes to
EPA’s application-specific regulations
outlined in this section, EPA is also
proposing a targeted change to the
regulations related to the enforcement
and compliance provisions EPA
finalized in the Allocation Framework
Rule. As explained in the Allocation
Framework Rule, EPA established a
comprehensive system of mechanisms
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that together and by themselves
discourage and prevent illegal
production, import, and subsequent
sales of illegally produced or imported
HFCs. Since the requirement came into
effect that entities must expend
allowances to produce or import HFCs,
EPA has been working with partner
agencies across the Federal government
to implement a comprehensive
enforcement and compliance program.
One issue that EPA has been
grappling with is what to do with HFCs
that an entity imports or attempts to
import without expending the requisite
number of allowances. Among other
things, the Federal government has been
considering reexport, destruction, and
auctions as potential available pathways
for such HFCs. EPA is in the process of
working with partner Federal agencies,
particularly CBP, to consider the
feasibility of an auction of HFCs that
have been stopped or seized by CBP as
was done in the past with illegally
imported ODS. As part of this process,
EPA has identified a provision in the
existing 40 CFR part 84 regulations that
could be read to inhibit some auctions
of HFCs, although there is nothing in 40
CFR part 84 that prohibits auctions. In
order to ensure auctions are an option,
if the Federal government otherwise
chooses to pursue them, EPA in this
rulemaking is proposing to amend the
prohibition relating to the sale and
prohibition of illegally imported HFCs
in 40 CFR 84.5 to clarify that a person
may sell or distribute, or offer for sale
or distribution, a regulated substance
purchased at an auction authorized by
CBP if the buyer expended consumption
allowances or ASAs in a quantity equal
to the EV-weighted equivalent of the
illegally imported regulated substances.
This proposed change would provide
explicit clarity to an entity that
purchases HFCs at such an auction that
the HFCs they purchase can be sold as
if they were initially imported with
allowances.32
EPA is also proposing targeted
changes to the reporting requirements to
provide clarity in the regulations for
how such purchases would be reported.
EPA proposes that entities purchasing
HFCs at auction would need to report
the import of those HFCs (that was done
by another entity prior to the auction
purchase) under 40 CFR 84.31(c)(1) and
maintain records consistent with 40
CFR 84.31(c)(2). EPA proposes that
entities would use the date that entry
32 The sales provision in 40 CFR 84.5 does not
apply to other government personnel or contractors
that need to move the HFCs for eventual disposition
consistent with the regulatory requirements, such as
through an auction with verification by EPA prior
to sale.
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was filed for the HFCs purchased at
auction for purposes of 40 CFR
84.31(c)(1) reporting and maintain
records of that purchase under 40 CFR
84.31(c)(2). This would provide a date
that can be easily verified and would
align with when the entity formally
expressed intent to CBP to enter the
HFCs into U.S. commerce.
Additionally, EPA is proposing that
entities who purchase HFCs at auction
would not be subject to the advance
notification requirement in 40 CFR
84.31(c)(7) for HFCs purchased via an
auction authorized by CBP, as the
window for the notification would have
already passed and EPA would be
verifying whether a prospective
purchaser has sufficient allowances as
part of any auction. However, EPA
proposes that entities would still have
to provide notification to EPA via a
CBP-authorized electronic data
interchange system, such as the
Automated Broker Interface, prior to the
HFCs entering U.S. commerce and
provide the same data elements as in 40
CFR 84.31(c)(7). If a certificate of
analysis (see 40 CFR 84.31(c)(7)(xvi)) is
not available at the time of filing entry,
EPA is proposing that the entity would
need to do any required sampling and
testing prior to sale in U.S. commerce.
J. Quarterly Exporter Reporting of
Internal Transaction Numbers
ITNs uniquely identify shipments
being exported from the U.S. to another
country. EPA currently requires
companies to report ITNs when they
request additional consumption
allowances after exporting bulk HFCs.
EPA is proposing to require companies
to additionally report ITNs quarterly for
all HFC exports. It is EPA’s
understanding that reporters can obtain
ITNs from either CBP or their broker
with relative ease, once they have a
process to do so in place. Many
reporters already gather ITNs on a
regular basis for the purpose of
submitting RACA reports.
Under CBP regulations, there are
some instances in which exporters may
acquire ITNs but are not required to do
so. These instances may include exports
to Canada and lower-value exports, for
example. EPA proposes that exporters
would not be required to report ITNs for
shipments that are exempt from needing
ITNs under CBP regulations. EPA is not
proposing any changes to the existing
regulations related to RACAs, so
reporters would still need to obtain
ITNs for any exports listed in RACA
submissions (e.g., exports to Canada).
EPA is proposing to require exporters
to report ITNs quarterly to better enable
EPA to perform quality assurance and
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integrity checks between exports
reported to the Agency under the
reporting requirements in 40 CFR 84.31
with Customs records. This, in turn,
will enable EPA to better ensure the
accuracy of the overall volume of HFCs
that are exported, which is a critical
component of the overall calculation of
the HFC phasedown, in addition to
being communicated for transparency to
stakeholders and being a key part of the
Agency’s international reporting
obligations under the Montreal Protocol.
K. Date of Purchase for Requests for
Additional Consumption Allowances
(RACAs)
EPA is proposing to change the
existing requirement in 40 CFR
84.17(a)(5) to report the date HFCs were
purchased as part of a RACA. Instead,
EPA would require an entity to only
report whether the HFCs exported were
purchased before January 1, 2022, or
after that date. EPA has received
feedback from entities requesting
RACAs that it is difficult to report the
date HFCs were purchased because the
information can be difficult to obtain.
For example, a company may purchase
several batches of HFCs over the course
of several months and combine these
batches into a homogenous mixture in
an on-site holding tank. These batches
of HFCs could come from multiple
suppliers. The contents of the holding
tank are then siphoned off into smaller
containers and exported to a foreign
country, at which point the company
seeks a RACA for those exported HFCs.
In this scenario, it is difficult to
determine what the ‘‘date of purchase’’
was for any given container of HFCs that
was exported.
When EPA initially codified the
requirement to provide the date
purchased as part of a RACA, the
primary purpose of this data element
was to track how much material is being
exported out of pre-2022 inventory,
before the phasedown program was in
effect. This, in turn, helps the Agency
understand certain market trends (e.g.,
how many containers are being sold out
of older inventory as opposed to more
recently purchased inventory).
However, EPA can track this trend with
a simpler data element. Accordingly,
EPA proposes to change the existing
requirement to provide the date HFCs
were purchased to whether the HFCs
were purchased before or after January
1, 2022.
VIII. Authorization To Produce for
Export
In previous rulemakings, i.e., the
Allocation Framework Rule and the
2024 Allocation Rule, some commenters
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expressed concern that under EPA’s
methodology for issuing production and
consumption allowances, certain
producers were not allocated sufficient
allowances to meet the demands of their
international customers working in
applications for which ASAs were
allocated to the domestic manufacturers.
Commenters said that foreign
semiconductor manufacturing remains
important even while domestic
semiconductor manufacturing increases
under the CHIPS Act.
This issue was generally beyond the
scope of prior rulemakings, but EPA
recognizes that under the methodology
for issuing general pool production and
consumption HFC allowances 33 in
tandem with how ASAs have
historically been issued, domestic HFC
producers that manufacture low EV
HFCs with proportionally smaller
market shares may face challenges due
to a combination of the phasedown
itself, EPA’s allocation methodology,
and that EPA does not allocate ASAs for
entities’ operations outside the United
States.
Subsection (e)(5) of the AIM Act
provides that the Administrator may
authorize an entity to produce a
regulated substance in excess of the
number of production allowances
otherwise allocated to that entity,
subject to several conditions including:
• The authorization is valid for a
renewable period of not more than five
years;
• Authorization must be established
via notice and opportunity for public
comment; and
• The production is solely for export
to, and use in, a foreign country that is
not subject to the prohibition in
subsection (j)(1); 34 and
• The production so authorized
would not violate the production or
consumption limits.
EPA has received a request from
Iofina Chemical (Iofina) to authorize
additional production of HFCs under
subsection (e)(5) that can be exported to
supply semiconductor manufacturers
outside of the United States. Iofina has
informed EPA that it has experienced
challenges acquiring HFC allowances
via a transfer from another allowance
holder so it can produce low-EV, HFC–
41, to sell to semiconductors
manufacturers abroad. Iofina has flagged
33 EPA is not reopening nor proposing to revisit
the methodology for issuing general pool
production and consumption HFC allowances in
this rulemaking.
34 Given that the prohibition of (j)(1) does not take
effect until 2033, and EPA is proposing to make
allowances available to Iofina through 2030, EPA
does not consider this restriction related to
subsection (j)(1) as relevant to this rulemaking.
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this challenge for EPA for several years.
The company has also noted that even
if it were able to secure a transfer for a
single year, Iofina could not plan over
multiple years.
EPA has considered Iofina’s specific
situation, the limited number of
allowances that would be needed to
accommodate its request, and its stated
intent to export HFCs for use in an
application that Congress specified in
subsection (e)(4)(B) of the AIM Act, and
is proposing to authorize Iofina to
undertake additional production for
export as contemplated by AIM Act
subsection (e)(5). To operationalize this
subsection of the AIM Act, EPA is
proposing to establish a production for
export category of allowances and
associated recordkeeping and reporting
requirements. EPA is proposing that this
new category of allowances would be
nontransferable. Consistent with
language in subsection (e)(5) of the AIM
Act that EPA may ‘‘authorize an entity’’
(emphasis added), the Agency is
proposing that these production for
export allowances would be available
only to Iofina to supply regulated HFCs
to application-specific end users located
abroad, specifically and only for the
etching of semiconductor material or
wafers and cleaning of CVD chambers
within the semiconductor
manufacturing sector. EPA is proposing
to issue 3,000.0 MTEVe of allowances
annually to Iofina for the stated purpose
for each of the calendar years 2026
through 2030.
EPA proposes to determine that
authorization of production for export to
Iofina in this instance is appropriate and
consistent with subsection (e)(5) of the
AIM Act. EPA proposes that this is
particularly true where the ASA
requirements of subsection (e)(4)(B)(iv)
provide priority access to HFCs for
defined applications. This proposal is
intended to address a need that has been
voiced consistently and exclusively by
Iofina, for which Iofina has provided
supporting information to substantiate
the request.
EPA is proposing to allocate 3,000.0
MTEVe non-transferrable production for
export allowances exclusively to Iofina
on an annual basis for each of the
calendar years 2026 through 2030. A
detailed discussion of the rationale for
the Agency’s proposal follows.
A. To what entities is EPA proposing to
allocate production for export
allowances?
As described above, EPA is proposing
to only allocate production for export
allowances to Iofina. The Agency has
determined that the company has
demonstrated their need for production
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for export allowances. Iofina has made
good faith efforts to acquire allowances
via an inter-company transfer and has
had difficulty finding another allowance
holder willing to transfer production
and consumption allowances to them in
order to produce regulated HFCs for
export. Iofina has documented foreign
customer demand in an applicationspecific end use for the HFC they
produce. Iofina has committed to
conduct extensive due diligence to
verify and ensure that the HFCs they
sell abroad are only sold to an entity
that will use the HFC for the etching of
semiconductor material or wafers and
cleaning of CVD chambers within the
semiconductor manufacturing sector
and are not going to be diverted for
some other use (e.g., destroyed for
carbon credits, sold to another entity
that will use the HFCs for another end
use).
EPA has also considered how this
authorization supports the HFC
phasedown overall. Iofina produces
only one HFC, HFC–41, one of the
lowest EV HFCs controlled by the AIM
Act with an EV of 92, at its facility in
Covington, Kentucky. Iofina produced
HFCs during the 2011–2019 timeline
and in subsequent years, and
accordingly have been allocated
allowances for calendar years 2022,
2023, and 2024. Because Iofina has
always produced a low EV HFC, their
allocation is smaller than companies
that have historically produced higher
EV HFCs, which now have flexibility to
transition into a lower EV HFC at higher
volumes. HFC–41 comprises a small
portion of overall U.S. HFC calculated
production 35 (0.02 percent in 2022 on a
mass basis and approximately 0.001
percent on an EVe basis), and Iofina is
the only U.S. producer of HFC–41 for
consumptive use. Further, HFC–41 has
a lower EV than all other regulated
substances used in the etching of
semiconductor material or wafers and
the cleaning of CVD chambers within
the semiconductor manufacturing
sector. Coupled with the extremely
small volume of allowances that this
production would require, EPA sees
authorizing this additional flexibility as
appropriate to support continued U.S.
production of HFC–41.
EPA recognizes that upon reviewing
this proposed rulemaking, there may be
other HFC producers who would be
interested in receiving production for
export allowances for applicationspecific uses abroad. At this time, EPA
has only assessed the appropriateness of
proposing an allocation for Iofina in
B. How many production for export
allowances is EPA proposing to issue to
Iofina on an annual basis, and for how
many years is EPA proposing to issue
these allowances?
EPA is proposing to issue Iofina nontransferrable production for export
allowances in the amount of 3,000.0
MTEVe on an annual basis. The Agency
arrived at this proposed amount based
on an evaluation of a combination of
factors including: Iofina’s request;
supporting information from the
company explaining and demonstrating
the need for production for export
allowances; Iofina’s relative market
share of production allowances and
recent yearly allocations from EPA;
recent conferral activity where Iofina is
the recipient; and, the general effect to
other producers of issuing Iofina
production for export allowances in the
proposed amount.
The production cap for calendar year
2024 through 2028 (the current
phasedown step) is 229,521,263 MTEVe
and the production cap for calendar
year 2029 through 2033 (the next
phasedown step) is 114,760,632 MTEVe.
The proposed number of production for
export allowances the Agency would
issue Iofina would be approximately
0.001 percent of the overall production
cap for 2026 through 2028 and 0.003
percent for 2029 and 2030.36
Accordingly, the Agency does not
envision any shortage of production
allowances for these years as a result of
the proposal to issue Iofina 3,000.0
MTEVe of production for export
allowances. In essence, the proposed
3,000.0 MTEVe of production for export
allowances issued to Iofina would not
materially affect any other domestic
producer even in light of the next
phasedown step.
Consistent with the provisions in
subsection (e)(5)(A)(i), EPA is proposing
that if finalized, Iofina would be issued
35 See EPA HFC Data Hub at https://
www.epa.gov/climate-hfcs-reduction/hfc-data-hub.
36 Percent = (Number of Production of
Allowances Issued)/(Production Cap)*100.
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light of the specific circumstances
presented by that entity. The Agency is
not proposing, nor creating a
mechanism to finalize, production for
export allowances for any other entity
through this rulemaking. If other
producers were to express a similar
interest, EPA would consider whether to
act in a separate rulemaking under
subsection (e)(5), but we emphasize that
this action is dependent on facts
specific to Iofina, including the
relatively small size of Iofina’s
production and the modest impacts on
the overall market for HFCs that will
result.
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production for export allowances on an
annual basis for a five-year period
between 2026 through 2030.
are issued on an annual basis and is
neither revising nor reopening the
methodology codified in 40 CFR 84.11.
C. Would Iofina need to expend
consumption allowances for materials
produced with production for export
allowances and subsequently exported?
Subsection (e)(5) of the AIM Act
allows EPA to ‘‘authorize a person to
produce’’ for export if such production
would not violate the yearly cap
described in subsection (e)(2)(B). To
operationalize this statutory
requirement, EPA proposes to require
that any material produced with
production for export allowances must
be exported in the same year it was
produced. The AIM Act defines
‘‘consumption’’ as the amount of HFCs
produced and imported minus the
quantity of HFCs exported. Therefore,
production of an HFC in a given year
would be ‘‘netted out’’ when calculating
consumption if that HFC is exported in
that same year. Because HFCs produced
with production for export allowances
would be exported in the same year and
therefore would be ‘‘netted out’’ when
evaluating the United States’ calculated
yearly consumption, EPA is proposing
that when Iofina produces for export
using this specific category of
allowances, it is not required to expend
consumption allowances in an
equivalent amount. Relatedly, EPA is
also proposing that Iofina’s materials
produced with production for export
allowances are not eligible for
additional consumption allowances
through the RACA provisions in 40 CFR
84.17.
E. What are the proposed recordkeeping
and reporting requirements for
production for export allowances?
In order to maintain overall
stringency while allowing for the
flexibilities in the AIM Act described in
this general information section of the
preamble, EPA is proposing that Iofina
comply with recordkeeping and
reporting requirements in addition to
what is already required of the entity as
a domestic producer under 40 CFR
84.31(a) and (b) and as an exporter
under 40 CFR 84.31(d).
D. How will this process affect the
issuance of other types of allowances?
Under 40 CFR part 84, subpart A, EPA
first issues ASAs. Because the Agency is
proposing an annual finite number of
production for export allowances for
Iofina, EPA proposes to issue these nontransferrable allowances immediately
after ASAs are issued. As a result, EPA
is proposing small modifications to 40
CFR 84.9 to reflect that the number of
available general pool production
allowances is the difference between the
yearly production cap and the sum of
ASAs issued and the number of
production for export allowances. It
should be noted that because
production for export allowances is a
separate category from general pool
production allowances, Iofina would be
eligible for both of these types of
allowances beginning in 2026 through
2030 if the production for export
allowance provisions are finalized. EPA
is not proposing any changes to how
general pool consumption allowances
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1. Annual Certifications
EPA is proposing that Iofina secure
signed certifications by a responsible
corporate officer from their overseas
application-specific customers attesting
that any regulated HFCs produced using
production for export allowances will
only be used in application-specific
uses (i.e., only for the etching of
semiconductor material or wafers and
the cleaning of CVD chambers within
the semiconductor manufacturing
sector). EPA is proposing that Iofina
must provide such written and signed
certification for each of their overseas
customers, accompanied by a
description of how the foreign use
aligns with the definitions in 40 CFR
84.13(a) and 40 CFR 84.3. If the
regulated HFCs produced by Iofina
using product for export allowances are
to be held at an intermediary prior to
receipt by the semiconductor
manufacturer, the intermediary must
also submit the same certification. As
part of the yearly written certification,
EPA is proposing that the name and
address of the foreign entity, and the
contact person’s name, email address,
and phone number are included.
Further, EPA is proposing that Iofina
must provide copies of these signed
certifications with its end of year fourth
quarter report due February 14 (i.e.,
certifications for calendar year 1 are due
on February 14 of year 2).
2. Quarterly Export and Inventory
Reporting
In addition to submitting the quarterly
exporter reports currently required
under 40 CFR 84.31(a) and (b), the
Agency is proposing that Iofina must, as
part of these quarterly exporter reports,
document the amounts exported that
were produced using production for
export allowances. Iofina would also be
required to document the country to
which HFCs were exported. As part of
this documentation and to help ensure
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that EPA can quickly locate exports of
regulated HFCs produced by Iofina, the
Agency is proposing that an ITN be
provided for each shipment regardless
of monetary value, destination country,
or other characteristics that could
otherwise exempt or preclude an
exporting entity from obtaining an ITN.
Additionally, EPA is proposing that
Iofina report quarterly no later than 45
days after the applicable quarterly
control period on inventory of regulated
HFCs produced with production for
export allowances so EPA can
effectively track their use. Inventory of
regulated HFCs produced with
production for export allowances must
be zero as of December 31 for that
calendar year; otherwise, EPA may
pursue actions including but not limited
to allowance adjustments, i.e.,
administrative consequences, or
enforcement action. All reports
described in this section would be
subject to EPA’s auditing provisions
under 40 CFR 84.33 if finalized as
proposed.
3. Recordkeeping
EPA is proposing that Iofina
maintains for a period of five years the
certifications from all of its customers
and any intermediaries attesting that the
regulated HFCs they are receiving are
only to be used for the etching of
semiconductor material or wafers and
cleaning of CVD chambers within the
semiconductor manufacturing sector.
The Agency is also proposing that Iofina
maintain for a period of five years
records demonstrating that Iofina has
conducted extensive due diligence to
verify and ensure that the HFCs they
sell abroad are only sold to an entity
that will use the HFC for an applicationspecific use and are not going to be
diverted for some other use (e.g.,
destroyed for carbon credits, sold to
another entity that will use the HFCs for
another end use).
IX. How will EPA handle
confidentiality for newly reported
information?
Consistent with EPA’s commitment to
transparency in program
implementation, as well as to
proactively encourage compliance,
support enforcement of program
requirements, and enable third-party
engagement to complement EPA’s
enforcement efforts, EPA is proposing
several ways it intends to release data
that would be collected if this proposed
rule is finalized as proposed.
EPA has reviewed the data elements
that are proposed to be reported under
this rulemaking. Based on that review,
EPA is proposing certain confidentiality
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determinations in advance through this
notice and comment rulemaking for
individual reported data elements that
EPA would be collecting through this
rulemaking. This proposal identifies
certain information that must be
submitted to EPA that may be subject to
disclosure to the public without further
notice because the Agency proposes to
find that the information does not meet
the standard for confidential treatment
under Exemption 4 of the Freedom of
Information Act (FOIA). EPA is also
proposing to identify certain other
categories of information that would be
entitled to confidential treatment. For
data elements for which EPA is not
making a confidentiality determination
in this action, EPA will apply the 40
CFR part 2 process for establishing caseby-case confidentiality determinations.
The confidentiality determinations in
this proposed action are intended to
increase the efficiency with which the
Agency responds to FOIA requests and
to provide consistency in the treatment
of the same or similar information.
Establishing these determinations
through this rulemaking will provide
predictability for both information
requesters and entities submitting
information to EPA. The confidentiality
determinations are also proposed to
increase transparency around this
program’s implementation.
A. Background on Determinations of
Whether Information Is Entitled to
Treatment as Confidential Information
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Exemption 4 of the FOIA exempts
from disclosure ‘‘trade secrets and
commercial or financial information
obtained from a person [that is]
privileged or confidential’’ (5 U.S.C.
552(b)(4)). In order for information to
meet the requirements of Exemption 4,
EPA must find that the information is
either: (1) a trade secret, or (2)
commercial or financial information
that is: (a) obtained from a person, and
(b) privileged or confidential.
Generally, when we have information
that we intend to disclose publicly that
is covered by a claim of confidentiality
under FOIA Exemption 4, EPA has a
process to make case-by-case or class
determinations under 40 CFR part 2 to
evaluate whether such information
qualifies for confidential treatment
under the exemption. 40 CFR 2.205.37 In
37 This approach of making categorical
determinations for a class of information is a wellestablished Agency practice. Prior examples of rules
where EPA has made such categorical
determinations include Confidentiality
Determinations for Data Required Under the
Mandatory Greenhouse Gas Reporting Rule and
Amendments to Special Rules Governing Certain
Information Obtained Under the Clean Air Act (76
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this action, EPA is proposing to make
categorical confidentiality
determinations in advance through this
notice and comment rulemaking for
some information that must be
submitted to EPA under the proposed
requirements. If EPA finalizes these
determinations, that information could
be disclosed to the public without
further notice.
The U.S. Supreme Court decision in
Food Marketing Institute v. Argus
Leader Media, 139 S. Ct. 2356 (2019)
(Argus Leader) addresses the meaning of
‘‘confidential’’ within the context of
FOIA Exemption 4. The Court held that
‘‘[a]t least where commercial or
financial information is both
customarily and actually treated as
private by its owner and provided to the
government under an assurance of
privacy, the information is ‘confidential’
within the meaning of Exemption 4.’’
Argus Leader, 139 S. Ct. at 2366. The
Court identified two conditions ‘‘that
might be required for information
communicated to another to be
considered confidential.’’ Id. at 2363.
Under the first condition, ‘‘information
communicated to another remains
confidential whenever it is customarily
kept private, or at least closely held, by
the person imparting it.’’ Id. (internal
citations omitted). The second condition
provides that ‘‘information might be
considered confidential only if the party
receiving it provides some assurance
that it will remain secret.’’ Id. (internal
citations omitted). The Court found that
the first condition necessary for
information to be considered
confidential within the meaning of
Exemption 4, but did not address
whether the second condition must also
be met.
Following the issuance of the Court’s
opinion in Argus Leader, the U.S.
Department of Justice (DOJ) issued
guidance concerning the confidentiality
prong of Exemption 4, articulating ‘‘the
newly defined contours of Exemption
4’’ post-Argus Leader.38 Where the
Government provides an express or
implied indication to the submitter
prior to or at the time the information
is submitted to the Government that the
Government would publicly disclose
the information, then the submitter
FR 30817) (May 26, 2011); Control of Air Pollution
From New Motor Vehicles: Heavy-Duty Engine and
Vehicle Standards (88 FR 4296) (January 24, 2023);
and Renewable Fuel Standard (RFS) Program: RFS
Annual Rules (87 FR 39600) (July 1, 2002).
38 ‘‘Exemption 4 After the Supreme Court’s Ruling
in Food Marketing Institute v. Argus Leader Media
and Accompanying Step-by-Step Guide,’’ Office of
Information Policy, U.S. DOJ, (October 4, 2019),
available at https://www.justice.gov/oip/exemption4-after-supreme-courts-ruling-food-marketinginstitute-v-argus-leader-media.
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75935
generally cannot reasonably expect
confidentiality of the information upon
submission, and the information is not
entitled to confidential treatment under
Exemption 4.39 In this proposed rule,
EPA intends to clearly assert that certain
information would not be kept
confidential and may be disclosed
publicly, if it is determined to not be
entitled to confidential treatment in the
final version of this rulemaking. This
assertion aligns with the Supreme
Court’s decision, and the subsequent
DOJ guidance that the government’s
assurances that a submission will be
treated as not confidential should
dictate the expectations of submitters. If
EPA were to finalize these
determinations, submitters would be on
notice before they submit any
information that EPA has determined
that the identified information outlined
in the memorandum provided in the
docket for this action titled Proposed
Confidentiality Determinations for Data
Elements in the Proposed Rule, will not
be entitled to confidential treatment
upon submission and may be released
by the Agency without further notice.
As a result, submitters will not have a
reasonable expectation that the
information will be treated as
confidential; rather, they should have
the expectation that the information will
be disclosed.
As described further below, EPA is
proposing to make categorical
confidentiality determinations as some
of the proposed data elements that
would be submitted to EPA contain
information that is not entitled to
confidential treatment. For data
elements not explicitly listed in the
document in the docket, EPA will apply
the 40 CFR part 2 process for
establishing case-by-case confidentiality
determinations.
There may be additional reasons not
to release information determined to not
be entitled to confidential treatment, for
example if it is personally identifiable
information (PII). The Agency will
separately determine whether any data
should be withheld from release for
reasons other than business
confidentiality before data is released.
EPA requests comment on the proposed
confidentiality determinations.
39 See id.; see also ‘‘Step-by-Step Guide for
Determining if Commercial or Financial
Information Obtained from a Person is Confidential
under Exemption 4 of the FOIA,’’ Office of
Information Policy, U.S. DOJ, (updated October 7,
2019), available at https://www.justice.gov/oip/stepstep-guide-determining-if-commercial-or-financialinformation-obtained-person-confidential.
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B. Data Elements Associated With a
Petition To Be Listed as an Application
That Will Receive Application-Specific
Allowances
In light of the statutory requirement in
subsection (e)(4)(B)(ii) to make a
complete petition available to the
public, and consistent with EPA’s
commitment to transparency in program
implementation, EPA has reviewed the
data elements EPA has proposed would
be required for a petition to be listed as
an application that will receive ASAs.
Specifically, EPA proposes to not
provide confidential treatment to, and
may release without further process, all
required elements of the petition, except
for a subset of the elements for which
EPA has proposed that multiple entities
could submit information individually
to EPA; 40 and all information submitted
to EPA that does not correspond to a
required element. The memorandum to
the docket lists each individual element
of a complete petition, as proposed by
EPA, with an accompanying proposed
determination on whether that element
would be entitled or not to confidential
treatment. EPA is proposing that
through this rulemaking, entities are put
on notice of data release in line with the
Argus Leader decision. EPA is providing
an express indication to all potential
petitioners prior to the time information
is submitted to EPA that EPA will
publicly disclose the information
without further process. Therefore,
potential future submitters cannot
reasonably expect confidentiality of the
information upon submission, and the
information is not entitled to
confidential treatment under Exemption
4. EPA invites comment on this
proposed determination.
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C. Data Elements Related to Proposed
Revisions to Existing Regulations
To maximize program transparency,
EPA is proposing to release several data
elements associated with the proposed
limited changes to existing regulations,
including specific data elements
associated with the following proposed
regulatory revisions: (1) a pool of setaside allowances for situations that meet
the criteria for unique circumstances
related to the propellants in MDIs
application; (2) allowing ASA holders to
return their allowances voluntarily if
they do not intend to use them; and (3)
40 For example, EPA is proposing that (1) data on
the proportion of the overall cost of the product or
system that reflects the cost of regulated
substance(s) and (2) historic and projected sales for
the product or system would not be treated as
confidential business information, as these are
important elements for the public to consider when
EPA is taking action on a petition for applicationspecific allowances.
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the ‘‘date of purchase’’ requirement for
a RACA. The memorandum to the
docket lists each individual element
EPA has proposed related to these
regulatory revisions with an
accompanying proposed determination
on whether that element would be
entitled or not to confidential treatment.
EPA is proposing that through this
rulemaking notice, entities are put on
notice of data release in line with the
Argus Leader decision. EPA is providing
an express indication to all entities prior
to the time information is submitted to
EPA that EPA will publicly disclose the
information without further process.
Therefore, potential future submitters
cannot reasonably expect confidentiality
of the information upon submission,
and the information is not entitled to
confidential treatment under Exemption
4. EPA invites comment on this
proposed determination.
EPA is proposing to regulatorily
determine that certain other information
would be entitled to confidential
treatment. EPA is proposing that
supporting documentation verifying a
need to purchase regulated substances
in the present calendar year for
purposes of the proposed set aside
because it is likely to include the type
of information that submitters
customarily keep private or closely
held. EPA is also proposing that data
elements associated with the following
proposed regulatory revisions would be
entitled to confidential treatment: (1)
requiring companies provide the total
expected amount of HFCs they intend to
purchase in the calendar year; (2) new
requirements for the conferral of
MCMEU allowances; and (3) requiring
exporters to report ITNs quarterly.
These data elements constitute the type
of information that submitters
customarily keep private or closely
held. Furthermore, in the case of ITNs
reported by exporters, it is EPA’s
understanding that the ITN, as part of
the Electronic Export Information (EEI)
contained in the Automated Export
System (AES), is considered
confidential by the Department of
Commerce. Additional information on
the proposed determinations for specific
data elements associated with the
proposed regulatory revisions is
provided in the memorandum in the
docket for this action. EPA invites
comments on these proposed
confidentiality determinations,
including information on whether the
listed elements are the type of
information customarily kept private or
closely held.
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D. Data Elements Reported to EPA
Related to Production for Export
EPA is proposing to establish a
production for export category of
allowances as described in Section VIII.
If EPA were to finalize the proposal for
production for export allowances, EPA
is proposing to release several data
elements that a production for export
allowance holder would be required to
submit, including: (1) quantity of
allowances expended for each regulated
substance; (2) quantity of each regulated
substance produced for export; (3)
quantity of each regulated substance,
produced using production for export
allowances, that was exported; (4)
quantity of each regulated substance
held in inventory at the end of the
quarter; and (5) the country to which
regulated substances, produced using
production for export allowances, were
exported. The memorandum to the
docket lists each individual element
EPA has proposed related to the
production for export allowances with
an accompanying proposed
determination on whether that element
would be entitled or not to confidential
treatment. EPA is proposing that
through this rulemaking, entities are put
on notice of data release in line with the
Argus Leader decision. EPA is providing
an express indication to all entities prior
to the time information is submitted to
EPA that EPA will publicly disclose the
information without further process.
Therefore, potential future submitters
cannot reasonably expect confidentiality
of the information upon submission,
and the information is not entitled to
confidential treatment under Exemption
4. EPA invites comment on this
proposed determination.
EPA is proposing that the ITNs
submitted for all exports of regulated
substances produced using production
for export allowances would be entitled
to confidential treatment for the same
rationale described earlier in this
section for the proposed requirement
that exporters report ITNs on a quarterly
basis. EPA requests comment on this
proposed determination, including
comments on why this information may
not be entitled to confidential treatment.
EPA is proposing that the signed
certifications would be entitled to
confidential treatment because it is
EPA’s understanding that these
certifications could have the potential to
reveal confidential business
relationships (i.e., the relationship
between the allowance holder, overseas
customer, and any intermediaries). EPA
requests comment on this proposed
determination, including comments on
why this information may not be
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entitled to confidential treatment.
Specifically, EPA requests comment on
whether the existence of a business
relationship between an HFC producer
and customer is information that is
customarily closely held.
X. What are the costs and benefits of
this action?
The changes proposed in this
proposed rule would not result in any
significant changes to the phasedown
program as a whole, and thus do not
fundamentally change the assumptions
made in the Allocation Framework Rule
RIA and subsequent RIA addenda. The
Allocation Framework Rule RIA
estimated benefits and costs for the HFC
phasedown between 2022 and 2050,
including assuming for analytical
purposes that the allocation system
would continue unchanged for years
past the initial period (i.e., for 2024 and
beyond). This action would not change
the total number of allowances issued
each year or the associated
environmental impacts. Further, the
2023 Technology Transitions Rule RIA
Addendum quantified the costs and
benefits associated with the transitions
necessary for compliance based on the
sector- and subsector-specific
restrictions finalized in that rule. Given
that the 2023 Technology Transitions
Rule promulgated restrictions for sectors
that encompass both defense sprays and
SCPPU foams (aerosols and foam
blowing sectors, respectively), the
compliance costs associated with the
proposals described in Section V of this
proposed rule to restrict the use of
certain HFCs in defense sprays and
SCPPU foams have already been
accounted for in the 2023 Technology
Transitions Rule RIA Addendum.
Therefore, EPA is not developing an
update to the RIA for this proposed rule;
however, given that some elements
proposed in this rulemaking could
result in incremental impacts for a
subset of entities, the Agency did
analyze potentially salient costs and
benefits considerations associated with
this proposed rulemaking. A summary
of this analysis is included below, and
additional details are presented in
Discussion of Costs and Benefits for
Phasedown of Hydrofluorocarbons:
Review and Renewal of Eligibility for
Application-specific Allowances, which
is available in the docket for this action
(EPA–HQ–OAR–2024–0196).
This analysis is intended to provide
the public with information on the
relevant costs and benefits of this action
and to comply with Executive Orders.
The analysis does not form a basis or
rationale for any of the actions EPA is
proposing in this rulemaking.
For entities in applications for which
EPA is co-proposing an option to not
renew eligibility for ASAs, the biggest
drivers for any costs would be no longer
being exempted from the restrictions
promulgated under the Technology
Transitions Program. However, entities
within those applications that currently
receive ASAs would also avoid
recordkeeping and reporting costs
associated with being an ASA holder
because they would no longer receive
ASAs and thereby no longer need to
comply with related recordkeeping and
reporting provisions, resulting in
burden relief.
General pool allowance holders may
receive benefits in the form of
additional allowances if EPA finalized
one or more applications no longer
being eligible for ASAs. However, EPA
anticipates that the number of
additional allowances would be
insignificant, totaling well under one
percent of consumption allowances in a
given year. For example, the number of
allowances allocated in calendar year
2024 to the two applications for which
EPA is co-proposing an option to not
renew is equivalent to 0.1 percent of
calendar year 2024 consumption
allowances. In addition, as these
marginal benefits constitute a transfer
from one group to another and do not
75937
change the total number of allowances
issued, there is no net societal impact.
EPA estimates that there may be costs
related to the proposed requirements for
ASA petitions and revisions to existing
regulations. For example, in a scenario
in which EPA does not renew the
defense sprays and SCPPU foam for
marine and trailer uses applications, the
estimated costs of this proposed rule
would be $19,052 in one-time costs and
$54,310 in annual costs. More
discussion of this scenario is included
in the costs and benefits memo available
in the docket that is referenced above.
Other than these costs, EPA has not
identified additional costs or benefits
beyond those estimated in the
Allocation Framework Rule RIA and
subsequent RIA addenda.
XI. Statutory and Executive Order
Review
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 14094: Modernizing Regulatory
Review
This action is a ‘‘significant regulatory
action’’ as defined in Executive Order
12866, as amended by Executive Order
14094. Accordingly, EPA submitted this
action to the Office of Management and
Budget (OMB) for Executive Order
12866 review. Documentation of any
changes made in response to the
Executive Order 12866 review is
available in the docket. EPA prepared
an economic analysis of the potential
impacts associated with this action.
This analysis, ‘‘Discussion of Costs and
Benefits for Phasedown of
Hydrofluorocarbons: Review and
Renewal of Eligibility for Applicationspecific Allowances,’’ is available in the
docket for this action (EPA–HQ–OAR–
2024–0196) and is briefly summarized
in Section X of this preamble, titled,
‘‘What are the costs and benefits of this
action?’’. The high end costs of this
proposed rule are estimated in the table
below:
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TABLE 3—SUMMARY OF COSTS IN SCENARIO IN WHICH DEFENSE SPRAYS AND SCPPU FOAM FOR MARINE AND TRAILER
USES APPLICATIONS ARE NOT RENEWED
Activity
One-time
costs
Application-specific allowance recordkeeping and reporting burden relief for entities no longer eligible for ASAs
Technology Transitions recordkeeping and reporting burden for entities no longer eligible for ASAs ..................
Petitions requesting eligibility for ASAs ...................................................................................................................
Other regulatory revisions .......................................................................................................................................
........................
19,052
........................
........................
$(189,728)
221,462
12,758
9,818
Total ..................................................................................................................................................................
19,052
54,310
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Annual costs
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B. Paperwork Reduction Act (PRA)
The information collection activities
in this proposed rule have been
submitted for approval to OMB under
the PRA. The Information Collection
Request (ICR) document that the EPA
prepared has been assigned EPA ICR
number 2685.05. You can find a copy of
the ICR in the docket for this proposed
rule, and it is briefly summarized here.
Subsection (d)(1)(A) of the AIM Act
specifies that on a periodic basis, but
not less than annually, each person that,
within the applicable reporting period,
produces, imports, exports, destroys,
transforms, uses as a process agent, or
reclaims a regulated substance shall
submit to EPA a report that describes, as
applicable, the quantity of the regulated
substance that the person: produced,
imported, and exported; reclaimed;
destroyed by a technology approved by
the Administrator; used and entirely
consumed (except for trace quantities)
in the manufacture of another chemical;
or, used as a process agent. EPA collects
such data regularly to support
implementation of the AIM Act’s HFC
phasedown provisions. EPA requires
quarterly reporting to ensure that annual
production and consumption limits are
not exceeded. It is also needed for EPA
to be able to review allowance transfer
requests, of which remaining
allowances is a major component of
EPA’s review. In addition, EPA collects
information to calculate allowances, to
track the movement of HFCs through
commerce, and to require auditing.
Collecting these data elements allows
EPA to confirm that the entity has not
exceeded its allowed level of production
and consumption and that the
aggregated annual quantity of
production and consumption in the
United States does not exceed the cap
established in the AIM Act. As
described above in this preamble, EPA
is proposing a procedural process for
submitting a petition to designate a new
application as eligible for priority access
to allowances; reporting and
recordkeeping requirements relevant for
narrow revisions to the methodology
used to allocate allowances to ASA
holders for calendar years 2026 and
beyond; and other limited reporting and
recordkeeping revisions, such as for the
proposal to authorize an entity to
produce regulated substances for export.
All information sent by the submitter
electronically is transmitted securely to
protect information that is CBI or
claimed as CBI consistent with the
confidentiality determinations made in
the Allocation Framework Rule and the
proposed confidentiality determinations
described in Section IX of this
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preamble, if finalized as proposed. The
reporting tool guides the user through
the process of submitting such data.
Documents containing information
claimed as CBI must be submitted in an
electronic format, in accordance with
the recordkeeping requirements.
Respondents/affected entities:
Respondents and affected entities will
be individuals or entities that produce,
import, export, reclaim, recycle for use
as a fire suppressant, distribute, destroy,
transform, use HFCs as a process agent,
or produce for export, certain HFCs that
are defined as a regulated substance
under the AIM Act. Respondents and
affected entities will also be any entity
issued or conferred ASAs.
Respondent’s obligation to respond:
Mandatory (AIM Act).
Estimated number of respondents:
342.
Frequency of response: Quarterly,
biannual, annual, and as needed
depending on the nature of the report.
Total estimated burden: 36,248 hours
(per year). Burden is defined at 5 CFR
1320.3(b).
Total estimated cost: $5,486,236 (per
year), includes $1,038,450 annualized
capital or operation & maintenance
costs.
An agency may not conduct or
sponsor, and a person is not required to
respond to, a collection of information
unless it displays a currently valid OMB
control number. The OMB control
numbers for the EPA’s regulations in 40
CFR are listed in 40 CFR part 9.
Submit your comments on the
Agency’s need for this information, the
accuracy of the provided burden
estimates and any suggested methods
for minimizing respondent burden to
the EPA using the docket identified at
the beginning of this proposed rule. The
EPA will respond to any ICR-related
comments in the final rule. You may
also send your ICR-related comments to
OMB’s Office of Information and
Regulatory Affairs using the interface at
www.reginfo.gov/public/do/PRAMain.
Find this particular information
collection by selecting ‘‘Currently under
Review—Open for Public Comments’’ or
by using the search function. OMB must
receive comments no later than October
16, 2024.
C. Regulatory Flexibility Act (RFA)
I certify that this action will not have
a significant economic impact on a
substantial number of small entities
(SISNOSE) under the RFA. The small
entities subject to the requirements of
this action are entities that hold HFC
allowance allocations (including
production, consumption, and
application-specific allowances),
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entities that applied for but did not
receive set-aside allowances in 2022,
entities that previously imported HFCs
between 2017 and 2019 but did not
receive 2022 allowance allocations, and
entities that recover and reprocess
HFCs. Given there are co-proposals for
two applications, EPA conducted this
preliminary screening analysis based on
the pathway that could lead to the
highest cost burden on small entities;
therefore, this analysis assumes for
analytical purposes that the defense
sprays and SCPPU foam for marine and
trailer uses applications will not be
renewed. The Agency has determined
that four of the 276 affected small
businesses—or 1.4 percent of all
affected small businesses—could incur
costs in excess of one percent of annual
sales, and three of those four small
businesses—or 1.1 percent of all
affected small businesses—could incur
costs in excess of 3 percent of annual
sales. The four entities that could incur
costs in excess of one percent of annual
sales are all entities that currently
receive ASAs in the defense sprays and
SCPPU foam for marine and trailer uses
applications. These costs are primarily
driven by these entities no longer being
exempted from Technology Transition
Program restrictions. Further details of
this analysis are presented in Economic
Impact Screening Analysis for
Phasedown of Hydrofluorocarbons:
Review and Renewal of Eligibility for
Application-specific Allowances, which
is available in the docket for this action
(EPA–HQ–OAR–2024–0196).
D. Unfunded Mandates Reform Act
(UMRA)
This action does not contain any
unfunded mandate of $100 million
(adjusted annually for inflation) or more
(in 1995 dollars) as described in UMRA,
2 U.S.C. 1531–1538, and does not
significantly or uniquely affect small
governments. The action imposes no
enforceable duty on any State, local or
Tribal governments and the costs
involved in this action are estimated not
to exceed $183 million in 2023$ ($100
million in 1995$ adjusted for inflation
using the GDP implicit price deflator) or
more in any one year.
E. Executive Order 13132: Federalism
This action does not have federalism
implications. It will not have substantial
direct effects on the States, on the
relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government.
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F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This action does not have Tribal
implications as specified in Executive
Order 13175. EPA is not aware of Tribal
businesses engaged in activities that
would be directly affected by this
action. Based on the Agency’s
assessments, EPA also does not believe
that potential effects, even if direct,
would be substantial. Accordingly, this
action will not have substantial direct
effects on Tribes, on the relationship
between the Federal government and
Indian Tribes, or on the distribution of
power and responsibilities between the
Federal government and Indian Tribes,
as specified in Executive Order 13175.
Thus, Executive Order 13175 does not
apply to this action.
EPA periodically updates Tribal
officials on air regulations through the
monthly meetings of the National Tribal
Air Association and has shared
information on this rulemaking through
this and other fora.
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
EPA interprets Executive Order 13045
as applying only to those regulatory
actions that concern environmental
health or safety risks that EPA has
reason to believe may
disproportionately affect children, per
the definition of ‘‘covered regulatory
action’’ in section 2–202 of the
Executive Order.
Therefore, this action is not subject to
Executive Order 13045 because it does
not concern an environmental health
risk or safety risk. Since this action does
not concern human health, EPA’s Policy
on Children’s Health also does not
apply.
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H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution or Use
This action is not a ‘‘significant
energy action’’ because it is not likely to
have a significant adverse effect on the
supply, distribution, or use of energy.
This action applies to certain regulated
substances and certain applications
containing regulated substances, none of
which are used to supply or distribute
energy.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations and Executive
Order 14096: Revitalizing Our Nation’s
Commitment to Environmental Justice
for All
The EPA believes that this type of
action does not concern human health
or environmental conditions and
therefore cannot be evaluated with
respect to potentially disproportionate
and adverse effects on communities
with environmental justice concerns.
This proposed rule does not change the
HFC phasedown schedule.
Although this action does not concern
human health or environmental
conditions, the EPA identified and
addressed environmental justice
concerns associated with the HFC
phasedown within the Allocation
Framework Rule (86 FR 55116, October
5, 2021) and the 2024 Allocation Rule
(88 FR 46836, July 20, 2023). In these
rulemakings, EPA identified and
addressed environmental justice
concerns by assessing available
information to analyze baseline human
health or environmental conditions,
conducting updated analyses based on
more recently available data, and
providing meaningful participation
opportunities for communities with
environmental justice concerns. EPA
carefully evaluated available
information on HFC production
facilities and the characteristics of
nearby communities. Based on EPA’s
analysis, EPA found evidence of
environmental justice concerns near
HFC production facilities from
cumulative exposure to existing
environmental hazards in these
communities.
List of Subjects in 40 CFR Part 84
Environmental protection,
Administrative practice and procedure,
Air pollution control, Chemicals,
Climate Change, Emissions, Imports,
Reporting and recordkeeping
requirements.
Michael S. Regan,
Administrator.
For the reasons set out in the
preamble, the EPA proposes to amend
40 CFR part 84 as follows:
PART 84 PHASEDOWN OF
HYDROFLUOROCARBONS
I. National Technology Transfer and
Advancement Act
■
This rulemaking does not involve
technical standards.
Authority: Pub. L. 116–260, Division S,
Sec. 103.
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1. The authority citation for part 84
continues to read as follows:
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75939
2. Amend § 84.3 by adding the
definitions ‘‘Healthcare system need’’,
‘‘Responsible corporate officer’’, and
‘‘Responsible official’’ in alphabetical
order to read as follows:
■
§ 84.3
Definitions.
*
*
*
*
*
Healthcare system need means
circumstances where an increase in
demand for MDIs used to treat asthma,
chronic obstructive pulmonary disease,
and other respiratory diseases may
occur because of a change in market
conditions that otherwise would not be
included in calculated rates of growth.
*
*
*
*
*
Responsible corporate officer means a
person who is authorized by the
regulated entity to make representations
on behalf of, or obligate the company as
ultimately responsible for, any activity
regulated under 40 CFR part 84, subpart
A.
Responsible official means a person
who is authorized by the regulated
entity to make representations on behalf
of, or obligate the company as
ultimately responsible for, any activity
regulated under 40 CFR part 84, subpart
A.
*
*
*
*
*
■ 3. Amend § 84.5 by:
■ a. In paragraph (a)(1), adding ‘‘,
unexpended production for export
allowances,’’ after the phrase
‘‘unexpended production allowances
and consumption allowances’’.
■ b. Revising paragraph (c)(2).
■ c. In paragraph (d), adding
‘‘production for export,’’ after ‘‘All
production, consumption,’’ and adding
‘‘production for export,’’ after the phrase
‘‘confer a production, consumption,’’.
■ d. Revising paragraph (f).
■ e. Adding paragraph (k).
The revisions and additions read as
follows:
§ 84.5 Prohibitions relating to regulated
substances.
*
*
*
*
*
(c) * * *
(2) No person may use a regulated
substance produced or imported by
expending application-specific
allowances for any purpose other than
those for which the application-specific
allowance was allocated, and as set
forth in this paragraph (c). Applicationspecific allowances are apportioned to a
person under §§ 84.13 and 84.15 for the
production or import of regulated
substances solely for the individual
application listed on the allowance.
*
*
*
*
*
(f) Sale and distribution. No person
may sell or distribute, or offer for sale
or distribution, any regulated substance
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Federal Register / Vol. 89, No. 179 / Monday, September 16, 2024 / Proposed Rules
that was produced or imported in
violation of paragraphs (a) through (d) of
this section, except:
(1) for such actions needed to reexport the regulated substance; or
(2) if the regulated substance was
purchased at a government auction
authorized by the United States
Customs and Border Protection and
consumption allowances were
expended in the requisite quantity to
cover the regulated substances at issue.
Every kilogram of a regulated
substance sold or distributed, or offered
for sale or distribution, in contravention
of this paragraph constitutes a separate
violation of this subpart. Sale or
distribution, or offer for sale or
distribution, of less than one kilogram of
regulated substance in contravention of
this paragraph constitutes a separate
violation of this subpart.
*
*
*
*
*
(k) Production for export allowances.
No person may use a regulated
substance produced by expending
production for export allowances for
any purpose other than those for which
the production for export allowance was
allocated, aligning with the applications
as listed in § 84.13(a).
■ 4. Amend § 84.9 by:
■ a. In paragraph (b)(3) adding ‘‘and
3,000.0 MTEVe allowances to be
allocated pursuant to § 84.18,’’ after
‘‘§ 84.13’’.
■ b. Redesignating paragraph (c) as
paragraph (d).
■ c. Adding new paragraph (c).
The addition reads as follows:
§ 84.9 Allocation of calendar-year
production allowances.
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*
*
*
*
*
(c) Starting with the allocation of 2026
calendar year allowances, the relevant
Agency official will withhold ten
percent of production allowances
otherwise calculated under paragraph
(b) of this section from any entity that
produced regulated substances in any
calendar year 2011 through 2019 for a
separate entity that is being issued
application-specific allowances in
accordance with § 84.13, except for
mission-critical military end uses. If
there are remaining production
allowances after distribution from the
set-aside under § 84.15, the relevant
agency official will distribute such
allowances to the entity from which
they were withheld.
*
*
*
*
*
■ 5. Amend § 84.11 by:
■ a. Redesignating the second paragraph
(c) as paragraph (e).
■ b. Redesignating paragraph (c) as
paragraph (d).
■ c. Adding new paragraph (c).
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The addition reads as follows:
§ 84.11 Allocation of calendar-year
consumption allowances.
*
*
*
*
*
(c) Starting with the allocation of 2026
calendar year allowances, the relevant
Agency official will withhold ten
percent of consumption allowances
otherwise calculated under paragraph
(b) of this section from any entity that
imported regulated substances in any
calendar year 2011 through 2019 for a
separate entity that is being issued
application-specific allowances in
accordance with § 84.13, except for
mission-critical military end uses. If
there are remaining consumption
allowances after distribution from the
set-aside under § 84.15, the relevant
agency official will distribute such
allowances to the entity from which
they were withheld.
*
*
*
*
*
■ 6. Amend § 84.13 by:
■ a. In paragraph (a), removing ‘‘2022,
2023, 2024, and 2025’’ and adding in
their place ‘‘as designated’’.
■ b. In paragraph (a)(1), adding ‘‘for
calendar years 2022–2030’’ after the
phrase ‘‘metered dose inhalers’’.
■ c. In paragraph (a)(2), adding ‘‘for
calendar years 2022–2025’’ after the
phrase ‘‘defense sprays’’.
■ d. In paragraph (a)(3), adding ‘‘for
calendar years 2022–2030’’ after the
phrase ‘‘trailer use’’.
■ e. In paragraph (a)(4), adding ‘‘for
calendar years 2022–2030’’ after the
phrase ‘‘semiconductor manufacturing
sector’’.
■ f. In paragraph (a)(5), adding ‘‘for
calendar years 2022–2030’’ after the
phrase ‘‘end uses’’.
■ g. In paragraph (a)(6), adding ‘‘for
calendar years 2022–2030’’ after the
phrase ‘‘fire suppression’’.
■ h. In paragraph (b)(1), adding ‘‘,
including supporting documentation
that verifies this need’’ after the phrase
‘‘this section’’.
■ i. In paragraph (b)(1)(ii) remove ‘‘or’’
after the phrase ‘‘facility or facilities;’’.
■ j. In paragraph (b)(1)(iii), removing ‘‘A
global pandemic or other public health
emergency that increases’’ and adding
in their place ‘‘A global pandemic, other
public health emergency, or other
healthcare system needs related to
increased’’ and removing ‘‘inhalers.’’
and adding in its place ‘‘inhalers;’’.
■ k. Adding paragraphs (b)(1)(iv) and
(v).
■ l. Adding paragraph (b)(2).
■ m. Redesignating paragraph (c)(1) as
paragraph (c)(7).
■ n. Adding new paragraph (c)(1).
■ o. Adding paragraphs (c)(4) through
(6).
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p. Revising newly redesignated
paragraph (c)(7) introductory text.
■ q. Removing paragraph (e).
■ r. Redesignating paragraphs (f)
through (h) as paragraphs (e) through
(g), respectively.
■ s. Adding new paragraph (h).
The revisions and additions read as
follows:
■
§ 84.13 Allocation of application-specific
allowances.
*
*
*
*
*
(b) * * *
(1) * * *
(iv) Economic disruption outside the
immediate control of the applicant; or
(v) Buildup of a stockpile of a specific
regulated substance in the event of a
production cessation. Requests for this
unique circumstances must include: a
letter from the applicant’s supplier
signed by a responsible corporate officer
stating that the supplier is ceasing all
production of the regulated substance at
issue within three years; certification
that the applicant has regulatory
requirements beyond this part that limit
ability to switch suppliers or there are
no other suppliers that could meet their
needs; and evidence that the applicant
has a restricted HFC supply chain.
(2) Entities must provide an estimate
of the total quantity of regulated
substances they expect to purchase in
the following calendar year based on
their expected eligibility for allowances.
(c) * * *
(1) Accounting for verified changes in
inventory in calculating growth rates
and purchase amounts, except:
(i) for applications for mission-critical
military end uses; and
(ii) if the applying entity provides a
rationale deemed acceptable by the
relevant agency official as to why
inventory buildup should not be
accounted for;
*
*
*
*
*
(4) Subtracting out quantities reported
under § 84.31(h)(1)(x) in calculating
growth rates and purchase amounts;
(5) Allocating allowances equivalent
to the highest verified purchase amount
measured in exchange value equivalent
from the prior three years for entities
that meet any of the following criteria:
(i) entity purchased less than 100
kilograms of regulated substances in at
least one of the last three years, and the
average growth rate of use for the
company over the past three years
calculated under paragraph (7)(i) is
equal to or greater than 200 percent;
(ii) entity had zero purchases in one
of the last three years for reasons other
than newly using regulated substances;
or
(iii) entity purchased equal to or less
than 100 kilograms of regulated
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substances in each of the past three
years;
(6) For the application of structural
composite preformed polyurethane
foam for marine use and trailer use,
utilizing the exchange value for HFC–
152a in calculating the allowance
allocation, regardless of what regulated
substance was used by an entity;
(7) For all other entities, multiplying
the use of regulated substances by the
company in the specific application in
the prior year by the higher of:
*
*
*
*
*
(h) Any entity receiving an allocation
of allowances pursuant to this section
may voluntarily choose to return any
quantity of allowances to EPA up to,
and including, June 30 of the calendar
year in which the allowances can be
expended. If any allowances are so
returned, those allowances will be
distributed to the persons who meet the
criteria listed in §§ 84.9 and 84.11
proportionate to entities’ market share
as calculated in §§ 84.9(b)(2) and
84.11(b)(5).
■ 7. Add § 84.14 to read as follows:
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§ 84.14 Petition for designation of an
application as eligible for applicationspecific allowances.
(a) Petitions filed pursuant to 42
U.S.C. 7675(e)(4)(B)(ii) must include:
(1) A description of the application,
including an explanation of what the
application is, what purpose or function
it achieves, and what populations or
commercial products benefit from the
application;
(2) A list of regulated substance(s) and
description of their use in the
application and an explanation as to
why regulated substances are required
in the application;
(3) Evidence that no safe or
technically achievable substitute is or is
expected to be available, and that the
petitioner has conducted research to
evaluate substitutes for the regulated
substance(s);
(4) Evidence that supply of the
regulated substance(s) used in the
application is insufficient to
accommodate the application;
(5) A signed and notarized
certification from a responsible
corporate officer at the requesting entity
that the application cannot use
recovered and reprocessed regulated
substance in conjunction with or in
place of virgin regulated substance,
either due to demonstrated lack of
technical achievability or insufficient
supply, and an explanation and
evidence documenting why recovered
and reprocessed regulated substance
cannot be used for the application;
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(6) Total quantity (in kilograms) of all
regulated substances acquired by each
entity submitting the petition for the
application specified in the petition in
each of the previous three years,
including records documenting that
quantity;
(7) The name of the entity or entities
supplying regulated substances and
contact information for those suppliers
over the past three years;
(8) Total quantity (in kilograms) of
each regulated substance held in
inventory by each entity submitting the
petition as of the date the petition is
submitted;
(9) An estimate of the total quantity of
regulated substances the petitioner
expects to purchase in the first year it
would be eligible for ASAs;
(10) Data on the proportion of the
overall cost of the product or system
that reflects the cost of regulated
substances for each entity;
(11) Historic and projected sales for
the product or system for each entity;
(12) Evidence of research into design
changes to decrease the amount of
regulated substance used in the product
or system;
(13) An explanation regarding
whether the use of the regulated
substance(s) is necessary for the health,
safety, or is critical for the functioning
of society (encompassing cultural and
intellectual aspects);
(14) An explanation regarding steps
taken to minimize the use of the
regulated substance and any associated
emission of the HFC(s); and
(15) Information on regulatory
restrictions related to possible
alternatives and substitutes.
(b) If the petition does not include the
required information listed in paragraph
(a), the petition will be deemed
incomplete, and EPA will notify the
entity submitting the petition.
(c) In the event that an application
becomes eligible to receive applicationspecific allowances:
(1) EPA will allocate allowances to
entities in a new application in
accordance with § 84.13; and
(2) A new application would be
eligible to receive application-specific
allowances for no longer than the latest
calendar year included in § 84.13(a).
■ 8. Amend § 84.15 by adding paragraph
(h) to read as follows:
§ 84.15 Set-aside of application-specific
allowances, production allowances, and
consumption allowances.
*
*
*
*
*
(h) Consumption and production
allowances from § 84.9(c) and § 84.11(c)
are available in the form of applicationspecific allowances to entities that
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75941
request them no later than April 30 of
the calendar year in which the
allowances may be expended that:
(1) qualify for application-specific
allowances under § 84.13;
(2) provide supporting documentation
that verify a need to purchase regulated
substances in the present calendar year
beyond what is reflected by the rates of
growth calculated in § 84.13(c)(1);
(3) are facing a situation that qualifies
as a unique circumstance as defined in
§ 84.13(b)(iii); and
(4) demonstrate to the satisfaction of
the relevant agency official that the
situation described in paragraph (3) was
unknowable at the time the entity made
its request for application-specific
allowances pursuant to § 84.13(b).
■ 9. Amend § 84.17 by:
■ a. In the introductory text, adding the
language ‘‘, except for the export of
regulated substances produced with a
production for export allowance’’ to the
end of the first sentence.
■ b. Revising paragraph (a)(5).
The revision reads as follows:
§ 84.17 Availability of additional
consumption allowances.
*
*
*
*
*
(a) * * *
(5) The source of the regulated
substances and whether the date
purchased was before or after January 1,
2022;
*
*
*
*
*
■ 10. Add § 84.18 to read as follows:
§ 84.18 Authorization of production for
export allowances.
(a) EPA will allocate 3,000.0 MTEVe
of production for export allowances to
Iofina Chemical by October 1 of the
calendar year prior to the year in which
the allowances may be used for calendar
years 2026, 2027, 2028, 2029, and 2030.
(b) Production for export allowances
cannot be transferred.
(c) Any regulated substances
produced with production for export
allowances must be exported in the
same calendar year it was produced.
■ 11. Amend § 84.31 by:
■ a. In the introductory text of
paragraph (a), removing the phrase ‘‘in
the six applications listed in subsection
(e)(4)(B)(iv) of the AIM Act’’.
■ b. Redesignating paragraphs (d)(1)(vii)
and (d)(1)(viii) as paragraphs (d)(1)(viii)
and (d)(1)(ix), respectively.
■ c. Adding new paragraph (d)(1)(vii).
■ d. In paragraph (h)(1)(i), adding ‘‘,
including a copy of the sales records,
invoices, or other records documenting
that quantity’’ after the word ‘‘months’’.
■ e. In paragraph (h)(1)(ii), adding ‘‘,
including a copy of the sales records,
invoices, or other records documenting
that quantity’’ after the word ‘‘months’’.
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f. In paragraph (h)(1)(iii), adding ‘‘,
including a copy of the sales records,
invoices, or other records documenting
that quantity’’ after the parenthetical
‘‘(i.e., from the open market)’’.
■ g. In paragraph (h)(1)(iv), adding ‘‘,
including a copy of inventory records
documenting that quantity;’’ after the
word ‘‘use’’.
■ h. In paragraph (h)(1)(viii), removing
the last ‘‘and’’ after the phrase
‘‘additional need’’.
■ i. In paragraph (h)(1)(ix), removing
‘‘allowances.’’ and adding in its place
‘‘allowances; and’’.
■ j. Adding paragraph (h)(1)(x).
■ k. In paragraph (h)(2)(iv), adding ‘‘,
including a copy of inventory records
documenting that quantity;’’ after the
phrase ‘‘current year’’.
■ l. In the introductory text of paragraph
(h)(4), removing ‘‘, except for the
conferral of allowances for missioncritical military end uses,’’.
■ m. In paragraph (h)(7)(i), removing
‘‘annual’’ and adding in its place
‘‘biannual’’.
■ n. Redesignating paragraphs (h)(7)(iii)
through (h)(7)(vi) as paragraphs
(h)(7)(iv) through (h)(7)(vii),
respectively.
■ o. Adding new paragraph (h)(7)(iii).
■ p. Redesignating paragraph (l) as
paragraph (n).
■ q. Adding new paragraphs (l) and (m).
The revision and additions read as
follows:
■
§ 84.31
Recordkeeping and reporting.
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*
*
*
*
*
(d) * * *
(1) * * *
(vii) Internal Transaction Numbers for
all shipments, except shipments where
an exemption from the requirements for
the filing of Electronic Export
Information (EEI) is provided in 15 CFR
part 30 Subpart D;
*
*
*
*
*
(h) * * *
(1) * * *
(x) If allowances are allocated for a
unique circumstance under
§ 84.13(b)(1)(v), the quantity (in
kilograms) of each regulated substance
purchased with the intent to build
inventory during the prior six-month
period, including a copy of records
documenting that quantity.
*
*
*
*
*
(7) * * *
(iii) A copy of confirmation notices
when conferring allowances for
application-specific use;
*
*
*
*
*
(l) Holders of production for export
allowances. Any person allocated
production for export allowances must
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comply with the following
recordkeeping and reporting
requirements:
(1) Quarterly Reporting. Within 45
days after the end of each quarter, each
holder of production for export
allowances must submit to the relevant
Agency official a report containing the
following information:
(i) The quantity (in exchange value
equivalent) of production for export
allowances expended for each regulated
substance and the quantity (in
kilograms) of each regulated substance
produced for export;
(ii) The quantity (in kilograms) of
each regulated substance produced
using production for export allowances
that was exported;
(iii) The quantity (in kilograms) of
each regulated substance produced with
production for export allowances held
in inventory at the end of the quarter;
(iv) Internal Transaction Numbers for
all exports of regulated substances
produced with production for export
allowances;
(v) The country or countries to which
regulated substances produced using
production for export allowances were
exported.
(2) Annual Reporting. Within 45 days
after the end of the fourth quarter, each
holder of production for export
allowances must submit to the relevant
Agency official a report containing the
following information:
(i) Signed certifications by a
responsible corporate officer from all
foreign customers and supply
intermediaries attesting that any
regulated substances produced using
production for export allowances will
only be used in an application as listed
in § 84.13(a). Each certification must
include the name and address of the
foreign entity, and a contact person’s
name, email address, and phone
number;
(ii) A description of how the use
identified in the signed certifications
provided pursuant to paragraph (i)
aligns with the applications as listed in
§ 84.13(a).
(3) Recordkeeping. Entities who
receive production for export
allowances must maintain the following
records for three years:
(i) A copy of all certifications reported
pursuant to paragraph (2)(i); and
(ii) Records demonstrating due
diligence undertaken to verify and
ensure that all regulated substances
produced with production for export
allowances and exported are being used
in an application as listed in § 84.13(a).
(m) Purchasers of HFCs at a
government auction. Any entity
purchasing regulated substances at a
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government auction authorized by the
United States Customs and Border
Protection must report such purchase as
if they were an import consistent with
the applicable provisions under this
section, except for the following
adjustments.
(1) Quarterly reporting. The date that
filing for that entry was accepted by a
United States Customs and Border
Protection-authorized electronic data
interchange system, such as the
Automated Broker Interface, must be
reported as the date on which the
regulated substances were imported for
purposes of paragraph (c)(1)(v). Unless
otherwise unavailable, all requirements
of paragraph (c)(1) must be reported. If
a data element is unavailable, the
auction purchaser must contact EPA
and state that fact in writing by the time
they make their filed report.
(2) Recordkeeping. In addition to the
records specified in paragraph (c)(2), the
auction purchaser must maintain
records of the auction purchase,
including the accepted bid,
confirmation of payment, certification
by the entity that they expended
allowances, container composition
testing to verify the regulated substances
contained within the cylinder, and all
other final documentation of the auction
purchase. Unless otherwise unavailable,
all requirements of paragraph (c)(2)
must be met. If a data element is
unavailable, the auction purchaser must
contact EPA and state that fact in
writing by the time they make their filed
report.
(3) Advance notification. The auction
purchaser must report the information
specified in paragraph (c)(7) prior to the
HFCs entering U.S. commerce. The
requirement in paragraph (c)(7)(xvi)
does not apply if a certificate of analysis
is not available at the time of submitting
the information in paragraph (c)(7). The
entity must complete all required
sampling and testing required in this
subpart prior to sale in U.S. commerce
and maintain such records consistent
with 84.31.
*
*
*
*
*
■ 12. Amend § 84.54 by revising
paragraph (a)(16)(i)(O) and adding
paragraph (a)(16)(i)(P) to read as
follows:
§ 84.54 Restrictions on the use of
hydrofluorocarbons.
(a) * * *
(16) * * *
(i) * * *
(O) Products for removing bandage
adhesives from skin; and
(P) Defense sprays as defined at
§ 84.3.
*
*
*
*
*
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13. Amend § 84.60 by adding
paragraphs (a)(7) and (b)(3) to read as
follows:
■
§ 84.60
Recordkeeping and reporting.
(a) * * *
(7) Effective [DATE], this paragraph
shall apply to defense sprays as defined
at § 84.3 and structural composite
preformed polyurethane foam as
defined at § 84.3.
(b) * * *
(3) Effective [DATE], this paragraph
shall apply to defense sprays as defined
at § 84.3 and structural composite
preformed polyurethane foam as
defined at § 84.3.
[FR Doc. 2024–20602 Filed 9–13–24; 8:45 am]
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Agencies
[Federal Register Volume 89, Number 179 (Monday, September 16, 2024)]
[Proposed Rules]
[Pages 75898-75943]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2024-20602]
[[Page 75897]]
Vol. 89
Monday,
No. 179
September 16, 2024
Part VII
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Part 84
Phasedown of Hydrofluorocarbons: Review and Renewal of Eligibility for
Application-Specific Allowances; Proposed Rule
Federal Register / Vol. 89 , No. 179 / Monday, September 16, 2024 /
Proposed Rules
[[Page 75898]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 84
[EPA-HQ-OAR-2024-0196; FRL-10782-01-OAR]
RIN 2060-AV98
Phasedown of Hydrofluorocarbons: Review and Renewal of
Eligibility for Application-Specific Allowances
AGENCY: Environmental Protection Agency (EPA).
ACTION: Notice of proposed rulemaking.
-----------------------------------------------------------------------
SUMMARY: The U.S. Environmental Protection Agency is undertaking this
rulemaking to assess the eligibility of six applications to receive
priority access to allowances allocated pursuant to the American
Innovation and Manufacturing Act of 2020. This rulemaking proposes the
framework for how EPA will assess whether to renew the eligibility of
applications to receive application-specific allowances; decisions to
renew or not renew each of the six applications that currently receive
application-specific allowances; revisions to the Technology
Transitions regulations as relevant to the specific applications under
review; a procedural process for submitting a petition to designate a
new application as eligible for priority access to allowances; narrow
revisions to the methodology used to allocate allowances to
application-specific allowance holders for calendar years 2026 and
beyond; and limited revisions to existing regulations. EPA is also
proposing to authorize an entity to produce regulated substances for
export. Lastly, EPA is proposing certain confidentiality determinations
for newly reported information if this rulemaking is finalized as
proposed.
DATES: Comments must be received on or before October 31, 2024. Any
party requesting a public hearing must notify the contact listed below
under FOR FURTHER INFORMATION CONTACT by 5 p.m. Eastern Daylight Time
on September 23, 2024. If a virtual public hearing is held, it will
take place on or before October 1, 2024 and further information will be
provided at https://www.epa.gov/climate-hfcs-reduction.
ADDRESSES: The U.S. Environmental Protection Agency (EPA) has
established a docket for this action under Docket ID No. EPA-HQ-OAR-
2024-0196. All documents in the docket are listed on the https://www.regulations.gov website. Although listed in the index, some
information is not publicly available, e.g., Confidential Business
Information (CBI) or other information whose disclosure is restricted
by statute. Certain other material, such as copyrighted material, is
not placed on the internet and will be publicly available only in hard-
copy form. Publicly available docket materials are available
electronically through https://www.regulations.gov or in hard copy at
the EPA Docket Center, Room 3334, WJC West Building, 1301 Constitution
Avenue NW, Washington, DC. The Public Reading Room is open from 8:30
a.m. to 4:30 p.m., Monday through Friday, excluding legal holidays. The
telephone number for the Public Reading Room is (202) 566-1744, and the
telephone number for the EPA Docket Center is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: Michelle Graff, U.S. Environmental
Protection Agency, Stratospheric Protection Division, telephone number:
202-564-5387; or email address: [email protected]. You may also
visit EPA's website at https://www.epa.gov/climate-hfcs-reduction for
further information.
SUPPLEMENTARY INFORMATION: Throughout this document, whenever ``we,''
``us,'' ``the Agency,'' or ``our'' is used, we mean EPA. Acronyms and
abbreviations that are used in this rulemaking that may be helpful
include:
2-BTP--2-bromo-3,3,3-trifluoropropene
AAGR--Average Annual Growth Rate
AES--Automated Export System
AIM Act--American Innovation and Manufacturing Act of 2020
AHRI--Air-Conditioning, Heating, and Refrigeration Institute
APU--Auxiliary Power Unit
ASHRAE--American Society for Heating, Refrigerating, and Air-
Conditioning Engineers
ASA--Application-Specific Allowance
CAA--Clean Air Act
CBI--Confidential Business Information
CBP--U.S. Customs and Border Protection
CF3I--Trifluoroiodomethane
CFR--Code of Federal Regulations
CGMP--Current Good Manufacturing Practice
CHIPS Act--Creating Helpful Incentives to Produce Semiconductors Act
of 2022
ClF3--Chlorine Trifluoride
CO2--Carbon Dioxide
COVID--Coronavirus Disease
CVD--Chemical Vapor Deposition
DFARS--Defense Federal Acquisition Regulation Supplement
DOD--U.S. Department of Defense
DOJ--U.S. Department of Justice
EEI--Electronic Export Information
EV--Exchange Value
EVe--Exchange Value Equivalent
EPA--U.S. Environmental Protection Agency
FAA--Federal Aviation Administration
FAR--Federal Acquisition Regulation
FDA--U.S. Food and Drug Administration
FIFRA--Federal Insecticide, Fungicide, and Rodenticide Act
FSTOC--Fire Suppression Technical Options Committee
FTOC--Flexible and Rigid Foams Technical Options Committee
FR--Federal Register
GHG--Greenhouse Gas
GWP--Global Warming Potential
HCFO--Hydrochlorofluoroolefin
HFC--Hydrofluorocarbon
HFIB--Hexafluoroisobutylene
HFO--Hydrofluoroolefin
ICAO--International Civil Aviation Organization
ICR--Information Collection Request
IPCC--Intergovernmental Panel on Climate Change
ITN--Internal Transaction Number
Kg--Kilogram
MCMEU--Mission-Critical Military End Uses
MCTOC--Medical and Chemicals Technical Options Committee
MDI--Metered Dose Inhaler
MT--Metric Ton
MTEVe--Metric Tons of Exchange Value Equivalent
NAICS--North American Industry Classification System
NF3--Nitrogen Trifluoride
ODP--Ozone Depletion Potential
ODS--Ozone-Depleting Substances
OMB--U.S. Office of Management and Budget
PFC--Perfluorocarbon
PII--Personally Identifiable Information
PRA--Paperwork Reduction Act
PU--Polyurethane
RACA--Requests for Additional Consumption Allowance
RFA--Regulatory Flexibility Act
RIA--Regulatory Impact Analysis
RSV--Respiratory Syncytial Virus
SCPPU--Structural Composite Preformed Polyurethane
SF6--Sulfur Hexafluoride
SiN--Silicon Nitride
SiO2--Silicon Dioxide
SNAP--Significant New Alternatives Policy
SISNOSE--Significant Economic Impact on a Substantial Number of
Small Entities
TCE--Trichloroethylene
TEAP--Technology and Economic Assessment Panel
TSCA--Toxic Substances Control Act
TSD--Technical Support Document
UMRA--Unfunded Mandates Reform Act
Table of Contents
I. Executive Summary
A. Purpose of the Proposed Regulatory Action
B. Summary of Proposed Actions
II. General Information
A. Does this action apply to me?
B. What is EPA's authority for taking this action?
III. Background
IV. How is EPA assessing whether to extend eligibility for
application-specific allowances?
A. How is EPA interpreting the ``no safe or technically
achievable substitute will be available'' criterion?
B. How is EPA interpreting the insufficient supply of regulated
substances criterion?
C. What is EPA's proposed framework for renewing applications?
[[Page 75899]]
V. Review of the Six Applications Listed in the AIM Act
A. Overview of Total U.S. HFC Consumption
B. Propellants in Metered Dose Inhalers
1. Availability of Safe and Technically Achievable Substitutes
2. Supply
3. What is EPA proposing regarding eligibility for application-
specific allowances?
C. Defense Sprays
1. Availability of Safe and Technically Achievable Substitutes
2. Supply
3. What is EPA proposing regarding eligibility for application-
specific allowances?
4. Proposed Restriction Under EPA's Technology Transitions
Program
D. Structural Composite Preformed Polyurethane Foam for Marine
Use and Trailer Use
1. Availability of Safe and Technically Achievable Substitutes
2. Supply
3. What is EPA proposing regarding eligibility for application-
specific allowances?
4. Proposed Restriction Under EPA's Technology Transitions
Program
E. Etching of Semiconductor Material or Wafers and the Cleaning
of Chemical Vapor Deposition Chambers Within the Semiconductor
Manufacturing Sector
1. Availability of Safe and Technically Achievable Substitutes
2. Supply
3. What is EPA proposing regarding eligibility for application-
specific allowances?
F. Mission-Critical Military End Uses
1. Availability of Safe and Technically Achievable Substitutes
2. Supply
3. What is EPA proposing regarding eligibility for application-
specific allowances?
G. Onboard Aerospace Fire Suppression
1. Availability of Safe and Technically Achievable Substitutes
2. Supply
3. What is EPA proposing regarding eligibility for application-
specific allowances?
VI. What are the proposed requirements associated with a petition to
be listed as an application that will receive application-specific
allowances?
VII. Proposed Revisions to Existing Regulations
A. Expected Total HFC Purchases
B. Unique Circumstances
C. Methodology for Entities With Irregular Purchasing History
and Very Small Users
D. Average Annual Growth Rate Calculations
E. Inventory
F. Department of Defense Conferrals
G. Limited Set-Aside for Unique Circumstances Related to MDIs
H. Return of Unneeded Allowances
I. Enabling Auctions of Illegally Imported HFCs
J. Quarterly Exporter Reporting of Internal Transaction Numbers
K. Date of Purchase for Requests for Additional Consumption
Allowances (RACAs)
VIII. Authorization To Produce for Export
A. To what entities is EPA proposing to allocate production for
export allowances?
B. How many production for export allowances is EPA proposing to
issue to Iofina on an annual basis, and for how many years is EPA
proposing to issue these allowances?
C. Would Iofina need to expend consumption allowances for
materials produced with production for export allowances and
subsequently exported?
D. How will this process affect the issuance of other types of
allowances?
E. What are the proposed recordkeeping and reporting
requirements for production for export allowances?
1. Annual Certifications
2. Quarterly Export and Inventory Reporting
3. Recordkeeping
IX. How will EPA handle confidentiality for newly reported
information?
A. Background on Determinations of Whether Information Is
Entitled to Treatment as Confidential Information
B. Data Elements Associated With a Petition To Be Listed as an
Application That Will Receive Application-Specific Allowances
C. Data Elements Related to Proposed Revisions to Existing
Regulations
D. Data Elements Reported to EPA Related to Production for
Export
X. What are the costs and benefits of this action?
XI. Statutory and Executive Order Review
A. Executive Order 12866: Regulatory Planning and Review and
Executive Order 14094: Modernizing Regulatory Review
B. Paperwork Reduction Act (PRA)
C. Regulatory Flexibility Act (RFA)
D. Unfunded Mandates Reform Act (UMRA)
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 Risks and Safety Risks
H. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution or Use
I. National Technology Transfer and Advancement Act
J. Executive Order 12898: Federal Actions To Address
Environmental Justice in Minority Populations and Low-Income
Populations and Executive Order 14096: Revitalizing Our Nation's
Commitment to Environmental Justice for All
I. Executive Summary
A. Purpose of the Proposed Regulatory Action
The U.S. Environmental Protection Agency (EPA) is undertaking this
action to implement certain provisions of the American Innovation and
Manufacturing Act of 2020, codified at 42 U.S.C. 7675 (AIM Act or the
Act). The Act directs EPA to implement the phasedown of
hydrofluorocarbons (HFCs) by issuing a limited quantity of
transferrable production and consumption allowances, which entities
must expend to produce or import HFCs. In addition, subsection
(e)(4)(B) of the Act authorizes EPA to allocate allowances exclusively
for the use in specific applications for which there is: (1) no safe or
technically achievable substitute and (2) an insufficient supply of the
HFCs used in the application that can be secured from chemical
manufacturers. The Act listed six applications that would receive
priority access to allowances for a five-year period beginning on
December 27, 2020: propellants in metered dose inhalers (MDIs), defense
sprays, structural composite preformed polyurethane (SCPPU) foam for
marine use and trailer use (hereafter referred to as SCPPU foam for
marine and trailer uses), the etching of semiconductor material or
wafers and the cleaning of chemical vapor deposition (CVD) chambers
within the semiconductor manufacturing sector, mission-critical
military end uses (MCMEU), and onboard aerospace fire suppression. EPA
intends to finalize this proposed rule ahead of the allocation of
calendar year 2026 allowances. Without finalization of this proposed
rule, all applications would be ineligible for allowances for calendar
year 2026.\1\ EPA has created a category of allowances to provide this
priority access, which EPA refers to as application-specific allowances
(ASAs). ASAs are allocated ahead of general pool allowances based on a
methodology intended to determine eligible entities' needs for
regulated substances (see Section VII of this preamble and the
Allocation Framework Rule (86 FR 55116, October 5, 2021) for more
information). After the total ASA quantity is determined, the remaining
allowances are distributed to general pool allowance recipients using a
different methodology.
---------------------------------------------------------------------------
\1\ EPA first codified the allocation methodology for general
pool and ASA holders in ``Phasedown of Hydrofluorocarbons:
Establishing the Allowance Allocation and Trading Program Under the
American Innovation and Manufacturing Act'' (hereafter referred to
as the ``Allocation Framework Rule'') (86 FR 55116, October 5,
2021). The methodology for general pool allowance holders was
subsequently updated in ``Phasedown of Hydrofluorocarbons: Allowance
Allocation Methodology for 2024 and Later Years'' (hereafter
referred to as the ``2024 Allocation Rule'' (88 FR 46836, July 20,
2023); the ASA methodology was not updated in the 2024 Allocation
Rule.
---------------------------------------------------------------------------
[[Page 75900]]
Subsection (e)(4)(B)(v) of the AIM Act directs EPA to review
applications receiving priority access to allowances not less
frequently than once every five years, and, if the application meets
the criteria above, authorize the eligibility of the application to
receive priority access to allowances for a period of not more than
five years. EPA is proposing how the Agency will interpret these two
criteria to review applications receiving ASAs. EPA is also proposing
decisions to renew or not renew each of the six applications that
currently receive ASAs.
Separately, subsection (i) of the Act authorizes EPA, by
rulemaking, to restrict the use of HFCs in sectors or subsectors where
the regulated substances are used. Under the authority of this
provision, EPA finalized the rule ``Phasedown of Hydrofluorocarbons:
Restrictions on the Use of Certain Hydrofluorocarbons Under the
American Innovation and Manufacturing Act of 2020'' (hereafter referred
to as the ``2023 Technology Transitions Rule''; 88 FR 73098, October
24, 2023), which established restrictions for three sectors and 39
subsectors. The rule exempted applications with a current qualification
for ASAs. As such, if an application is no longer eligible to receive
ASAs, it would become subject to the restrictions established in the
2023 Technology Transitions Rule. EPA is therefore proposing how the
Technology Transitions regulations would apply to applications if EPA
were to determine that those applications are not eligible for renewal
for the full five-year period.
The Act also includes a provision for the public to petition EPA to
designate an application as eligible for priority access to allowances.
EPA is proposing a procedural process for submitting a petition under
this provision and to define minimum required elements of such a
petition. In addition, this rulemaking proposes narrow revisions to the
methodology used to allocate allowances to ASA holders for calendar
years 2026 and beyond as well as other limited revisions to the
existing 40 CFR part 84 regulations. EPA is also proposing to authorize
an entity to produce regulated substances for export for application-
specific uses pursuant to subsection (e)(5). Lastly, EPA is proposing
certain confidentiality determinations for newly reported information
if this rulemaking is finalized as proposed.
B. Summary of Proposed Actions
Application-specific allowance holder review: EPA is describing how
it proposes to interpret the criteria under subsection (e)(4)(B) of the
AIM Act and evaluate the six categories of ASA holders listed in
subsection (e)(4)(B)(v) of the Act. EPA is proposing to renew the
following applications for the full five-year period from 2026-2030:
propellants in MDIs, the etching of semiconductor material or wafers
and the cleaning of CVD chambers within the semiconductor manufacturing
sector, MCMEU, and onboard aerospace fire suppression. EPA is co-
proposing two options for defense sprays: do not renew or renew for a
two-year period through 2027. EPA is co-proposing three options for
SCPPU foams for marine and trailer uses: do not renew, renew for a two-
year period through 2027, or renew for the full five-year period from
2026-2030 with allowance amounts determined based on the exchange value
(EV) of a substitute HFC. In cases where EPA is proposing to change the
status of ASA holders, this proposal also details how the Technology
Transitions regulations would apply to those applications.
Application-specific allowance holder petitions: EPA is proposing
the process and information requirements for submitting petitions under
subsection (e)(4)(B) of the AIM Act which seek the designation of an
application as an essential use.
Application-specific allowance methodology: EPA is proposing
targeted revisions to the existing ASA methodology: to require
companies to provide a total request for allowances for the calendar
year, to expand permissible scenarios that could qualify as unique
circumstances, to use a different allocation methodology for certain
very small users of HFCs and entities with irregular purchasing
history, how to account for inventory in allocation decisions, to
establish a set-aside of allowances for situations that meet the
criteria for unique circumstances related to medical conditions treated
by MDIs, and to allow ASA holders to return a portion of their
allowances voluntarily if they do not intend to use them. EPA is also
proposing new requirements for conferrals of MCMEU allowances and an
opportunity to return unneeded ASAs.
Other regulatory revisions: EPA is proposing other specific
regulatory changes to: clarify the ability of the Federal government to
pursue, if appropriate, auctioning illegally imported HFCs that are
seized by enforcement officials, require exporting companies to report
``Internal Transaction Numbers'' (ITNs) quarterly, and simplify the
reporting on ``date of purchase'' for a Request for Additional
Consumption Allowances (RACA).
Authorization of production for export: EPA is proposing to
authorize an entity to produce for export for application-specific uses
abroad.
Handling of confidentiality for newly reported information: EPA is
proposing certain confidentiality determinations for newly reported
information if this rulemaking is finalized as proposed.
II. General Information
A. Does this action apply to me?
You may be potentially affected by this proposal if you use HFCs in
one of the six applications eligible for an allocation under section
(e)(4)(B)(iv) of the AIM Act. You may also potentially be affected if
you produce, import, export, purify, destroy, reclaim, package, or
otherwise distribute HFCs for end users in one of these six
applications or are a current HFC allowance holder. Potentially
affected categories, North American Industry Classification System
(NAICS) codes, and examples of potentially affected entities are
included in Table 1.
Table 1--NAICS Classification of Potentially Affected Entities
------------------------------------------------------------------------
NAICS code NAICS industry description
------------------------------------------------------------------------
325120....................... Industrial Gas Manufacturing.
325199....................... All Other Basic Organic Chemical
Manufacturing.
325211....................... Plastics Material and Resin
Manufacturing.
325412....................... Pharmaceutical Preparation Manufacturing.
325414....................... Biological Product (except Diagnostic)
Manufacturing.
325998....................... All Other Miscellaneous Chemical Product
and Preparation Manufacturing.
326220....................... Rubber and Plastics Hoses and Belting
Manufacturing.
326150....................... Urethane and Other Foam Product.
326299....................... All Other Rubber Product Manufacturing.
[[Page 75901]]
333415....................... Air-Conditioning and Warm Air Heating
Equipment and Commercial and Industrial
Refrigeration Equipment Manufacturing.
333511....................... Industrial Mold Manufacturing.
334413....................... Semiconductor and Related Device
Manufacturing.
334419....................... Other Electronic Component Manufacturing.
334510....................... Electromedical and Electrotherapeutic
Apparatus Manufacturing.
336212....................... Truck Trailer Manufacturing.
336214....................... Travel Trailer and Camper Manufacturing.
336411....................... Aircraft Manufacturing.
336611....................... Ship Building and Repairing.
336612....................... Boat Building.
336992....................... Military Armored Vehicle, Tank, and Tank
Component Manufacturing.
SIC 373102................... Military Ships, Building, and Repairing.
339112....................... Surgical and Medical Instrument
Manufacturing.
423720....................... Plumbing and Heating Equipment and
Supplies (Hydronics) Merchant
Wholesalers.
423730....................... Warm Air Heating and Air-Conditioning
Equipment and Supplies Merchant
Wholesalers.
423740....................... Refrigeration Equipment and Supplies
Merchant Wholesalers.
423830....................... Industrial Machinery and Equipment
Merchant Wholesalers.
423840....................... Industrial Supplies Merchant Wholesalers.
423860....................... Transportation Equipment and Supplies
(except Motor Vehicle) Merchant
Wholesalers.
424690....................... Other Chemical and Allied Products
Merchant Wholesalers.
488510....................... Freight Transportation Arrangement.
541380....................... Testing Laboratories.
541714....................... Research and Technology in Biotechnology
(except Nanobiotechnology).
562111....................... Solid Waste Collection.
562211....................... Hazardous Waste Treatment and Disposal.
562920....................... Materials Recovery Facilities.
922160....................... Fire Protection.
------------------------------------------------------------------------
This table is not intended to be exhaustive, but rather provide a
guide for readers regarding entities likely to be affected by this
action. Other types of entities not listed in this section could also
be affected. If you have any questions regarding the applicability of
this action to a particular entity, consult the person listed under FOR
FURTHER INFORMATION CONTACT.
B. What is EPA's authority for taking this action?
On December 27, 2020, the AIM Act was enacted as section 103 in
Division S, Innovation for the Environment, of the Consolidated
Appropriations Act, 2021 (codified at 42 U.S.C. 7675). In subsection
(k)(1)(A), the AIM Act provides EPA with the authority to promulgate
necessary regulations to carry out EPA's functions under the Act,
including its obligations to ensure that the Act's requirements are
satisfied (42 U.S.C. 7675(k)(1)(A)). Subsection (k)(1)(C) of the Act
also provides that Clean Air Act (CAA) sections 113, 114, 304, and 307
apply to the AIM Act and any regulations EPA promulgates under the AIM
Act as though the AIM Act were part of title VI of the CAA.
Accordingly, this rulemaking is subject to CAA section 307(d) (see 42
U.S.C. 7607(d)(1)(I)) (CAA section 307(d) applies to ``promulgation or
revision of regulations under subchapter VI of this chapter (relating
to stratosphere and ozone protection)'').
The AIM Act authorizes EPA to address HFCs in three main ways:
phasing down HFC production and consumption through an allowance
allocation program, facilitating the transition to next-generation
technologies by restricting use of these HFCs in the sector or
subsectors in which they are used, and promulgating certain regulations
for purposes of maximizing reclaiming and minimizing releases of HFCs
from equipment and ensuring the safety of technicians and consumers.
This proposal relates to the first area and addresses restrictions in
the second area for impacted subsectors.
The Act required EPA, for the five-year period beginning on
December 27, 2020, to allocate the full quantity of allowances
necessary, based on projected, current, and historical trends, for the
production or consumption of regulated substances for the exclusive use
in six applications: propellants in MDIs, defense sprays, SCPPU foam
for marine and trailer uses, the etching of semiconductor material or
wafers and the cleaning of CVD chambers within the semiconductor
manufacturing sector, MCMEU, and onboard aerospace fire suppression (42
U.S.C. 7675(e)(4)(B)(iv)(I)). EPA has defined these allowances as ASAs.
EPA intends to finalize this rulemaking ahead of the allocation of
calendar year 2026 allowances. Without finalization of this rulemaking,
all applications would be ineligible for application-specific
allowances for calendar year 2026.
Subsection (e)(4)(B)(v) of the AIM Act requires EPA to review
applications receiving allocations pursuant to subsection (e)(4)(B)(iv)
at least every five years. If pursuant to this review EPA determines
that the requirements of two statutory criteria are met, EPA shall
authorize production or consumption, as applicable, of the exclusive
use of regulated substances in the application for renewable periods of
not more than five years. Specifically, EPA must determine whether: (1)
no safe or technically achievable substitute will be available during
the applicable period for the application; and (2) the supply of the
regulated substance that manufacturers or users of the regulated
substance for that application are capable of securing from chemical
manufacturers is insufficient to accommodate the application.
Separately, an entity may file a petition for an application to
receive ASAs. The AIM Act outlines timeframes and deadlines for EPA to
act on such a petition and how the Agency should assess such a petition
(42 U.S.C. 7675(e)(4)(B)(ii)). Specifically, not later than 180 days
after receiving a petition, EPA must propose and seek public comment on
whether to provide ASAs for the application. Not later than 270
[[Page 75902]]
days after EPA receives a petition, the Agency must take final action
on the petition. Any application determined to be eligible for ASAs
would also be subject to the review requirements in subsection
(e)(4)(B)(v).
Subsection (i) of the AIM Act, ``Technology Transitions,'' provides
that ``the Administrator may by rule restrict, fully, partially, or on
a graduated schedule, the use of a regulated substance in the sector or
subsector in which the regulated substance is used'' (42 U.S.C.
7675(i)(1)). However, rules promulgated under subsection (i) ``shall
not apply to . . . an essential use under clause (i) or (iv) of
subsection (e)(4)(B), including any use for which the production or
consumption of the regulated substance is extended under clause (v)(II)
of that subsection'' (42 U.S.C. 7675(i)(7)(B)(i)). Therefore, per
subsection (i)(7)(B)(i), the restrictions promulgated under the
Technology Transitions Program are not currently applicable to any
application receiving an ASA (40 CFR 84.56(a)(2)). To the extent that
this proposal would result in an application no longer receiving an
ASA, this action also proposes the Technology Transitions Program
restrictions that would apply to that application, if any, based on
EPA's consideration of the factors listed in subsection (i)(4) of the
AIM Act, should EPA finalize a determination that an application can no
longer receive an ASA.
Prior to proposing a rule, subsection (i)(2)(A) of the Act directs
EPA to consider negotiating with stakeholders in the sector or
subsector subject to the potential rule in accordance with negotiated
rulemaking procedures established under subchapter III of chapter 5 of
title 5, United States Code (commonly known as the ``Negotiated
Rulemaking Act of 1990''). If EPA makes a determination to use the
negotiated rulemaking procedures, subsection (i)(2)(B) requires that
EPA, to the extent practicable, give priority to completing that
rulemaking over completing rulemakings under subsection (i) that are
not using that procedure. If EPA does not use the negotiated rulemaking
process, subsection (i)(2)(C) requires the Agency to publish an
explanation of the decision not to use that procedure before
commencement of the rulemaking process. The Negotiated Rulemaking Act
of 1990 (5 U.S.C. 563) provides seven criteria that the head of an
agency should consider when determining whether a negotiated rulemaking
is in the public interest, namely, whether: (1) there is a need for a
rule; (2) there are a limited number of identifiable interests that
will be significantly affected by the rule; (3) there is a reasonable
likelihood that a committee can be convened with a balanced
representation of persons who can adequately represent the identified
interests and are willing to negotiate in good faith to reach a
consensus on the proposed rule; (4) there is a reasonable likelihood
that a committee will reach a consensus on the proposed rule within a
fixed period of time; (5) the negotiated rulemaking procedure will not
unreasonably delay the notice of proposed rulemaking and the issuance
of the final rule; (6) the agency has adequate resources and is willing
to commit such resources, including technical assistance, to the
committee; and (7) the agency, to the maximum extent possible
consistent with the legal obligations of the agency, will use the
consensus of the committee with respect to the proposed rule as the
basis for the action proposed by the agency for notice and comment.
If a head of agency determines that the use of the negotiated
rulemaking procedure is in the public interest, an agency may convene a
federally chartered advisory committee, and may rely on an appointed
convener under 5 U.S.C. 563(b) to assist with ascertaining the names of
persons who are willing and qualified to represent interests that will
be significantly affected by the proposed rule. If the agency decides
to establish a negotiated rulemaking committee, the agency must publish
in the Federal Register and in relevant publications a notice
announcing the agency's intention to establish a negotiated rulemaking
committee, a description of the subject and scope of the rule, a list
of the interests which are likely to be significantly affected by the
rule, a list of the persons proposed to represent such interests and
the proposed agency representatives, a proposed agenda and schedule for
completing the committee's work, a description of the administrative
and technical support to be provided to the committee by the agency, a
solicitation for comments on the proposal to establish the committee
and on the proposed membership of the committee, and an explanation of
how a person may apply or nominate another person for membership on the
committee. The agency must provide at least 30 calendar days for the
submission of comments and applications related to the membership of
the committee. In establishing and administering such a committee, the
agency shall comply with the Federal Advisory Committee Act, unless an
exception applies. If the committee reaches consensus on a proposed
rule, the committee shall transmit a report containing the proposed
rule to the Federal agency. If the committee does not reach a consensus
on a proposed rule, the committee may transmit a report specifying any
areas upon which consensus was reached. The proposed rule is still
subject to public comment, and for purposes of a rulemaking developed
under the AIM Act, the requirements of CAA section 307(d).
Before proposing the 2023 Technology Transitions Rule, consistent
with AIM Act subsection (i)(2)(A) and (C), EPA considered whether to
negotiate with stakeholders using the negotiated rulemaking procedure
provided for in the Negotiated Rulemaking Act of 1990, decided not to
use such procedures, and published its explanation of that decision in
the Federal Register (86 FR 74080, December 29, 2021).
EPA noted in the final 2023 Technology Transitions Rule that, where
appropriate, EPA will consider recent Agency actions and decisions
related to restrictions on the use of HFCs in sectors and subsectors
for its consideration on using negotiated rulemaking procedures. EPA
did not, for example, separately consider using negotiated rulemaking
for four petitions that were received after a rulemaking process had
already been commenced regarding the same sectors and subsectors, nor
did EPA consider anew whether or not to use negotiated rulemaking in an
interim final rule (88 FR 88825, December 26, 2023) that amended one
provision of the 2023 Technology Transitions Rule for one subsector.
Similarly, the proposed changes to the Technology Transitions
regulations contemplated in this action would be targeted at a subset
of applications within a subsector subject to those restrictions. EPA
is not addressing a new subsector in this proposal, nor even proposing
a different level of stringency from already promulgated restrictions;
rather, this action proposes only to establish deadlines by which
applications would need to comply with Technology Transitions
regulations in the event that those applications no longer receive
ASAs. EPA does not believe that the public interest would be served by
using the negotiated rulemaking procedure for this limited adjustment
to the Technology Transitions regulations, especially because
timeliness is a concern.
[[Page 75903]]
III. Background
HFCs are anthropogenic \2\ fluorinated chemicals that have no known
natural sources. HFCs are used in a variety of applications such as
refrigeration and air conditioning, foam blowing agents, solvents,
aerosols, and fire suppression. HFCs are potent greenhouse gases (GHGs)
with 100-year global warming potentials (GWPs) (a measure of the
relative climatic impact of a GHG) that can be hundreds to thousands of
times that of carbon dioxide (CO2).
---------------------------------------------------------------------------
\2\ While the overwhelming majority of HFC production is
intentional, EPA is aware that HFC-23 can be a byproduct associated
with the production of other chemicals, including but not limited to
hydrochlorofluorocarbon (HCFC)-22 and other fluorinated gases.
---------------------------------------------------------------------------
HFC use and emissions have been growing worldwide due to the global
phaseout of ozone-depleting substances (ODS) under the Montreal
Protocol on Substances that Deplete the Ozone Layer (Montreal
Protocol), and the increasing use of refrigeration and air-conditioning
equipment globally. HFC emissions had previously been projected to
increase substantially over the next several decades. In 2016, in
Kigali, Rwanda, countries agreed to adopt an amendment to the Montreal
Protocol, known as the Kigali Amendment, which provides for a global
phasedown of the production and consumption of HFCs. The United States
ratified the Kigali Amendment on October 31, 2022. Global adherence to
the Kigali Amendment would substantially reduce future emissions,
leading to a peaking of HFC emissions before 2040.
There are hundreds of possible HFC compounds. The 18 HFCs listed as
regulated substances by the AIM Act are some of the most commonly used
HFCs (neat and in blends) and have high impacts as measured by the
quantity of each substance emitted multiplied by their respective GWPs.
These 18 HFCs are all saturated, meaning they have only single bonds
between their atoms, and therefore have longer atmospheric lifetimes
than fluorinated compounds that are unsaturated. More detailed
information on HFCs, their uses, and their impacts is available in the
Allocation Framework Rule (86 FR 55116, October 5, 2021).
IV. How is EPA assessing whether to extend eligibility for application-
specific allowances?
As noted in Section II.B of this preamble, the AIM Act directs EPA
to undertake a review of applications receiving allowances pursuant to
subsection (e)(4)(B)(iv) at least every five years. The statute says
that access to ASAs shall be authorized for a renewed period if two
statutory criteria are met. Specifically: (1) ``no safe or technically
achievable substitute will be available during the applicable period
for that application; and'' (2) ``the supply of the regulated substance
that manufacturers or users of the regulated substance for that
application are capable of securing from chemical manufacturers . . .
including any quantities of a regulated substance available from
production or import, is insufficient to accommodate the application''
(42 U.S.C. 7675(e)(4)(B)(1)). In this section, we outline how EPA
interprets these criteria, what information the Agency will consider in
assessing these criteria, and a proposed framework for evaluating if an
application is eligible for renewal for up to five years. EPA notes
that under the statute, these criteria also apply to new applications
that may be listed, but, aside from Section VI addressing the petition
process, this proposed rulemaking is primarily focused on the renewal
of existing applications. However, EPA's interpretations of the
criteria discussed in this section would apply to future actions to add
new applications. The AIM Act includes additional evaluation
considerations for new applications in subsection (e)(4)(B)(i), but the
Agency is not addressing their interpretation in this rulemaking.
A. How is EPA interpreting the ``no safe or technically achievable
substitute will be available'' criterion?
In order for an application to continue to be eligible to receive
ASAs, EPA must determine ``no safe or technically achievable substitute
will be available'' for the application during the time period under
review (42 U.S.C. 7675(e)(4)(B)(i)(I)). EPA is proposing that the best
interpretation of this criterion is that if there is an available
substitute that is both safe and technically achievable, an application
would not meet this criterion for renewal. EPA acknowledges that the
statutory language could be ambiguous as to whether a substitute must
be both safe and technically achievable. However, reading the statutory
language differently than proposed would seem to create a perverse
outcome. In such a scenario, an application would become ineligible for
ASAs if EPA identified a substitute that was technically achievable,
but not safe. EPA reads the context of subsection (e)(4) as indicating
that Congress intended that listed applications continue to receive
priority access to allowances as long as the application needed to use
regulated substances. In a situation where an identified substitute is
not safe, EPA believes that it would be Congress's intent to continue
to provide priority access to allowances such that the application was
not prematurely forced to transition to an unsafe substitute.
Similarly, it does not seem reasonable to take away access to ASAs when
an identified substitute is safe, but not technically achievable. If
the application cannot technically implement the transition to a
substitute, it seems unrealistic to think that there could be a
transition away from regulated substances. Accordingly, EPA proposes to
interpret the statutory text and surrounding framework such that if EPA
determines there is no safe substitute that is technically achievable
for an application, or a technically achievable substitute is not safe,
the application would meet the first criterion for renewal.
In looking at potential substitutes for an application under
subsection (e)(4)(B)(i)(I), EPA is proposing to consider regulated
substances (i.e., other HFCs), alternative substances (e.g.,
hydrofluoroolefins (HFOs), hydrocarbons), and blends of HFCs and/or HFC
alternatives that can perform the same general function as the current
HFC in use. EPA is proposing that such an interpretation of the term
``substitute'' is most consistent with the statutory language of
subsection (e)(4)(B) as a whole. Specifically, in its direction to EPA
to review applications receiving ASAs every five years, Congress
directed EPA to ``review the availability of substitutes, including any
quantities of the regulated substance available.'' This sentence
structure, indicating that examination of quantities of regulated
substances available would be included as part of analyzing what
substitutes are available, suggests that regulated substances are part
of the universe of substitutes that Congress intended EPA to include in
its review. In addition to EPA's determination that such an approach is
more consistent with the statutory language than an approach of only
looking at non-regulated substances as substitutes, EPA has also
identified other benefits of this interpretation. For example, it would
seem to be a perverse outcome if EPA renewed an application's
eligibility for ASAs at historic quantities where there was an
available substitute that did not require any or required fewer
allowances to procure. Non-HFCs may be able to fill the same role as
the HFC, often functioning as a chemical-for-chemical
[[Page 75904]]
replacement or requiring limited design changes.
EPA is proposing, as part of its assessment of what chemicals may
be determined to be safe as a substitute for applications under review,
to only include substances, including blends of substances, with a
lower GWP than the regulated substance currently in use. As explained
in the Allocation Framework Rule (86 FR 55116, October 5, 2021), the
HFC phasedown's significant benefits are derived from the reduction of
production and consumption of certain chemicals on a GWP-weighted
basis.\3\ Considering higher-GWP substances or blends of substances
would run against this overall objective and could reduce the benefits
of the HFC phasedown, especially if this rulemaking led to the uptake
of higher-GWP non-HFC technologies (e.g., semiconductor manufacturers
transitioning back to using higher-GWP perfluorocarbons (PFCs)). In
addition, this proposed interpretation aligns with the approach under
the 2023 Technology Transitions Rule (88 FR 73098, October 24, 2023),
which established GWP limits for subsectors and considered substitutes
as only those with lower GWPs. Further discussion regarding the sources
EPA is relying on to determine if a substitute is safe (e.g., listed by
EPA's Significant New Alternatives Policy (SNAP) Program) can be found
below.
---------------------------------------------------------------------------
\3\ While the AIM Act calls for reduction of HFC production and
consumption on an EV-weighted basis, EV and GWP are numerically
equal. Lower GWP is an important consideration for whether a
substitute is safe, so EPA is using GWP instead of EV in the
discussion in this section of the rule.
---------------------------------------------------------------------------
In addition to looking at chemicals that could serve as
substitutes, EPA is also including in its analysis any potentially
available not-in-kind technologies (e.g., finger-pump bottles that
would not use any chemical propellant in lieu of aerosol cans) for
purposes of subsection (e)(4)(B)(i)(I). Such an approach is consistent
with the common understanding of the plain language definition of
``substitute.'' For example, Merriam Webster defines substitute as a
thing that ``takes the place of function of another'' and the Oxford
dictionary similarly notes a substitute is a ``thing acting or serving
in place of another.'' In general, not-in-kind technologies can serve
the need of some applications, so it is appropriate to include them
within the scope of assessing safe and technically achievable
substitutes. It would be unnecessarily limiting to exclude from the
scope of the analysis a technology that performs the same general
function for the application as the current HFC in use does. EPA also
acknowledges that market pressure from the HFC phasedown may encourage
a transition into not-in-kind technologies (and non-HFCs) by limiting
the supply of HFCs on a GWP-weighted basis, while the Technology
Transitions Program prohibits the use of certain HFCs in certain
sectors and subsectors. There is also precedent for considering not-in-
kind technologies under CAA Title VI, such as the SNAP Program and
Nonessential Product Bans, and the AIM Act Technology Transitions
Program, all of which also evaluate not-in-kind substitutes as possible
alternatives to ODS and HFCs, respectively.
EPA is aware that a transition to certain substitutes will require
changes to how the HFCs are used in the application (e.g.,
accommodating a flammable HFC in the manufacturing process). Shifts to
not-in-kind technologies will inherently require a change in
manufacturing and/or the product, so it would be a consistent approach
to also not outright exclude substitute chemicals that would similarly
require a change in manufacturing process or the product.
EPA does not want to unnecessarily limit the scope of the
substitute analysis at this point in time, and therefore is considering
a wide range of possible safe and technically achievable substitutes.
The phasedown of HFCs is still nascent, and, at this point, we cannot
know the full breadth of technologies that will be developed as
replacements for the current HFCs in use.
The Agency is proposing to assess this criterion, specifically that
a substitute is safe, technically achievable, and available, on an
application-wide basis. For applications that use multiple HFCs, a
substitute would need to be able to replace all HFCs used (or multiple
substitutes that replace all individual HFCs would need to be
available). For applications that have sub-applications (e.g., defense
sprays include those intended for humans and those intended for
animals), there would need to be a viable substitute for known sub-
applications. EPA's interpretation is that it would be unreasonable to
consider an application as having met this criterion and thereby
ineligible for renewal unless all known sub-applications can
successfully transition away from their currently used HFC(s).
EPA's evaluation of each application is not intended to be a
company-specific review; the commercialization \4\ of a substitute by
one sub-application suggests the substitute is safe or technically
achievable for the entire application barring evidence, such as testing
data, to the contrary. However, there are additional barriers to
commercialization, which are considered when assessing if the
identified substitute is available for an entire application. In
addition, EPA's interpretation of the statutory language is that
applications are intended to be viewed as a whole and not necessarily
renewed by sub-application. Specifically, the listing of the
applications in subsection (e)(4)(B)(iv)(I) does not break down the
application into sub-applications (e.g., ``defense sprays'' is not
listed as multiple separate applications, e.g., ``personal defense
sprays,'' ``law enforcement defense sprays,'' and ``bear defense
sprays''). Similarly, for applications that use multiple HFCs and have
specific uses for the individual HFCs, it would not be reasonable to
assess this criterion as being met if an application does not have an
available safe and technically achievable substitute for each HFC. It
is EPA's opinion that Congress did not intend for an application to
lose its eligibility for ASAs if it could only transition some, but not
all, of the HFCs currently used in the application.
---------------------------------------------------------------------------
\4\ EPA is using the term ``commercialization'' to mean that the
substitute is commercially available and actively being used in an
application's equipment or sold on the market (domestically or
internationally) for use in the application. ``Commercialization''
is not intended to be equated with ``available,'' as explained in
more detail in the main text.
---------------------------------------------------------------------------
EPA reviewed a range of sources in developing its assessment of the
availability of safe, technically achievable substitutes for each
application at issue here. Sources include, but are not limited to:
manufacturer announcements; information provided by stakeholders under
part 84 reporting requirements and other communications; relevant
Federal and State regulations; evaluations carried out under the 2023
Technology Transitions Rule (88 FR 73098, October 24, 2023) and the
SNAP Program; standards from industry, standard-setting bodies (e.g.,
American Society for Heating, Refrigerating, and Air-Conditioning
Engineers (ASHRAE)), and the U.S. Government (e.g., the U.S. Food and
Drug Administration's (FDA) standards for MDIs); and peer-reviewed
technical reports. The Technical Support Document (TSD) ``Draft Review
of Applications in the American Innovation and Manufacturing (AIM) Act
Section (e)(4)(B)(4)'' contains a comprehensive array of sources we
looked at for each application, and EPA is taking comment on other
relevant sources that should be considered.
[[Page 75905]]
As noted, EPA is considering the listings under the SNAP Program as
part of its assessment. The SNAP Program has an established history
evaluating substitutes for ODS, many of which are also possible
substitutes for HFCs. Where relevant, in its assessment of the
availability of safe substitutes, EPA considered information from the
SNAP Program, including the listings themselves and the information
underlying SNAP Program decisions. The SNAP Program does not evaluate
substitutes for semiconductor etching and cleaning of CVD chambers.
Some military applications are covered under the SNAP Program. In other
cases, such as MDIs and SCPPU foams, while these applications are
within the scope of the SNAP Program, there may be other sources of
information (e.g., the FDA, company information) that may be more
appropriate.
In its evaluation of substitutes and related decisions (e.g., to
list as acceptable or unacceptable), the SNAP Program carries out a
comparative risk evaluation and considers whether a substitute to an
ozone-depleting substance presents human health and environmental risks
that are lower than or comparable to such risks from other substitutes
that are currently or potentially available for the same uses. The
human health risks analyzed include safety, and in particular,
flammability, toxicity, and exposure (of workers, consumers, and the
general population) to chemicals with direct toxicity; environmental
risks include ozone depletion potential (ODP) and GWP. Information and
data relied upon in the SNAP Program are directly relevant to EPA's
assessment of substitutes in this rulemaking, and therefore EPA has
pulled from and relied upon SNAP Program assessments as appropriate.
EPA evaluates substitutes under the SNAP Program on an ongoing
basis and over time has listed numerous substances as ``acceptable,''
``acceptable, subject to use conditions,'' or ``acceptable, subject to
narrowed use limits.'' ``Acceptable subject to use conditions''
indicates that a substitute is acceptable only if used in a certain
way. Use conditions can include, but are not limited to, warning
labels, compliance with relevant safety standards, and restrictions on
where a substitute is used (e.g., HFC-134a is acceptable for FDA-
approved MDIs for medical purposes but is not acceptable for a majority
of aerosol uses, and some fire suppression substitutes may only be used
in typically unoccupied spaces). EPA can also list substitutes as
``acceptable subject to narrowed use limits'' under SNAP, indicating
that a substitute may be used only within certain specialized
applications within an end use and may not be used for other
applications within that end use (e.g., SNAP has previously listed some
substitutes as acceptable for only narrowed use limits for military or
space- and aeronautics-related applications). In listing of a chemical
as acceptable or acceptable subject to use conditions directly relevant
to the application, the SNAP Program makes an assessment that the
benefits outweigh the risks relative to other alternatives; these
listings are relevant data to support EPA's determination under AIM Act
subsection (e)(4)(B) on whether a substitute is ``safe'' under the
interpretation proposed in this rulemaking.
EPA lists substitutes as ``unacceptable'' under SNAP if the Agency
determines that they may increase overall risk to human health and the
environment, compared to other alternatives that are available or
potentially available for the same use. EPA has listed substitutes as
unacceptable considering the human health criteria described above, as
well as the environmental factors considered under SNAP. For example,
SNAP has listed certain substitutes as unacceptable due to unusually
high ODP, GWP, toxicity and exposure, and flammability (where it is not
clear how to mitigate risks sufficiently). Substitutes listed as
unacceptable in an end use are prohibited for that use and therefore
would not be an available safe or technically achievable substitute for
an application under our proposed interpretation of this criterion.
The Agency is also reviewing the evaluations carried out for the
2023 Technology Transitions Rule (88 FR 73098, October 24, 2023) and
relying on information and assessments done in that rulemaking, as
appropriate. In establishing restrictions, the Technology Transitions
Program factored in the availability of substitutes, considering both
safety and technological achievability, among other factors. The
Technology Transitions Program relied on information from a wide range
of sources when assessing availability, including but not limited to,
SNAP, the Montreal Protocol's Technology and Economic Assessment Panel
(TEAP), standards bodies, and information provided by industry, States,
and environmental non-governmental organizations. Though the Technology
Transitions Program looked subsector-wide, not at specific end uses,
and did not specifically analyze the applications currently receiving
ASAs under subsection (e)(4)(B)(iv), some of these applications (e.g.,
defense sprays and SCPPU foams for marine and trailer uses) have
similarities with the subsectors currently subject to restrictions. As
a result, in carrying out the assessments undertaken in this
rulemaking, EPA is considering relevant information from the Technology
Transition Program's evaluations.
In the assessment undertaken in this rulemaking, EPA is also taking
into account other Federal standards and regulations, both within EPA
and from other U.S. Government agencies. For many applications under
review in this rulemaking, there are applicable regulations and
standards that outline requirements related to the chemicals or
technologies used within an application. In these situations, such
standards and regulations may in some instances limit use of possible
substitutes. In some instances, it may not be possible for a substitute
to ever be used. In other instances, applicable regulations may require
entities to go through a regulatory approval process that would affect
when an application can transition to a substitute. Some examples of
regulations and standards we are considering as part of our proposed
evaluations include EPA's regulations covering pesticides such as bear
spays and dog sprays (sub-applications of defense sprays) under the
Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA; 7 U.S.C.
136-136y), the FDA's requirements for MDIs, and the U.S. Federal
Aviation Administration's (FAA) requirements for onboard aerospace fire
suppression. Additional standards and regulations for each application
are discussed further in the relevant chapter of the TSD. EPA invites
comment on any other standards or regulations that entities think EPA
should consider in determining an application's ability to transition
to a substitute.
EPA also considered the work undertaken by the Montreal Protocol's
TEAP in the proposed application assessment given the TEAP's analytical
work on substitutes and alternative technologies to substances
controlled under the Montreal Protocol, including HFCs. TEAP assesses
technical and economic information that serves as the basis for
parties' assessment of control measures of substances under the purview
of the Montreal Protocol. Such information is related to substitutes
that may replace the substances controlled under the Montreal Protocol
and alternative technologies that may be used without adverse impact on
the ozone layer and climate, production and consumption of controlled
substances,
[[Page 75906]]
emissions of controlled substances, potential alternatives for exempted
uses and others, as mandated by the parties. This assessment includes
applications listed in AIM subsection (e)(4)(B)(iv). In addition, TEAP
develops assessments in response to decisions taken by the parties to
the Montreal Protocol, including but not limited to Decision XXVIII/2,
which call for an assessment of alternatives to HFCs every five years.
EPA particularly looked at the 2022 Assessment Reports by the Medical
and Chemical Technical Options Committee, concerning semiconductors,
aerosols, and MDIs; the Flexible and Rigid Foams Technical Options
Committee (FTOC); and the Fire Suppression Technical Options Committee
(FSTOC). TEAP reports have included information on technical
achievability and safety. TEAP reports are developed by experts around
the world and provide insight into the HFC substitutes currently in use
and under development in the United States and globally. As such, EPA
is considering relevant information from these reports when carrying
out the assessment of available safe or technically achievable
substitutes undertaken in this rulemaking.
As described throughout this section, EPA is considering
information from a wide range of sources in its assessment of the
availability of safe or technically achievable substitutes for the
applications receiving ASAs under subsection (e)(4)(B)(iv)(I), and no
one source will be determinative for this criterion. Further
information about sources consulted for each application can be found
in Section V of this preamble and the TSD. EPA invites comment on its
interpretation of ``no safe or technically achievable substitute will
be available'' and the sources it is considering in its assessment of
this criterion.
B. How is EPA interpreting the insufficient supply of regulated
substances criterion?
Under the second criterion for renewal of an application's
eligibility to receive ASAs, EPA must determine that ``the supply of
the regulated substance that manufacturers or users of the regulated
substance for that application are capable of securing from chemical
manufacturers . . . , including any quantities of a regulated substance
available from production or import, is insufficient to accommodate the
application'' (42 U.S.C. 7675(e)(4)(B)(i)(II)). As described here and
in the sections of the proposed rule discussing each of the six
applications, a determination that there is insufficient supply could
be based on a number of different factors, including the available
domestic supply of the HFC(s) at issue, demand for said HFC(s), and
supply chain constraints particular to a given application (e.g.,
federally required purity specifications). Priority access to
allowances through ASAs has the potential to address insufficient
supply of HFCs by allowing entities that use HFCs in an eligible
application to more easily procure HFCs from a domestic supplier by
conferring allowances to authorize production or import or to import
the HFCs themselves.
In this proposed rulemaking, EPA is interpreting this criterion as
requiring an assessment related to the supply of the HFC(s) currently
used in an application's equipment or to manufacture the application's
products for use. Under this proposed interpretation, EPA would not
evaluate HFC(s) currently used exclusively for research and development
in assessing whether there is insufficient supply. EPA recognizes that
the research and development process may find various alternatives to
be unsuitable for an application. Therefore, it would be premature to
consider supply of potentially unsuitable HFC alternatives until such
time as they have been commercialized or are close to
commercialization. Further, it could also have the perverse effect of
limiting research into alternatives if an application's initial
research could prematurely contribute to removal from eligibility for
ASAs.
EPA is proposing to consider regulated substances supplied by
chemical manufacturers in its assessment of supply. EPA interprets the
reference to regulated substances ``from chemical manufacturers'' in 42
U.S.C. 7675(e)(4)(B)(i)(II) as direction from Congress to assess supply
from chemical manufacturers only, and that this direction could cover
both virgin and recovered and reprocessed HFCs. EPA is proposing to
include HFCs produced domestically and those that are produced abroad
and imported in its assessment of supply under this criterion. Congress
directed EPA to consider regulated substances ``from chemical
manufacturers . . . , including any quantities of a regulated substance
available from production or import'' in its assessment under 42 U.S.C.
7675(e)(4)(B)(i)(II). Because of Congress's reference to production and
import of regulated substances, and the lack of any language suggesting
that chemical manufacturers should be read as limited to only U.S.
producers, EPA intends to consider imported material from foreign HFC
producers in addition to regulated substances from domestic producers.
As a result, EPA is proposing not to consider HFC supply held by and
available to entities that do not produce or import HFCs in its
assessment of this criterion. This would exclude quantities of HFCs
held by entities that do not produce or import HFCs with allowances,
potentially including reclaimers, distributors, HFC blenders,\5\ and
HFC repackagers. EPA considers this proposed interpretation to be most
consistent with the statutory language in 42 U.S.C.
7675(e)(4)(B)(i)(II).
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\5\ For a discussion on the difference between producing HFCs
consistent with the AIM Act and blending HFCs to make various
refrigerant blends, see ``Response to Comments'', pg. 193, Docket ID
No. EPA-HQ-OAR-2021-0044, associated with the Allocation Framework
Rule (86 FR 55116) and the discussion in the 2024 Allocation Rule
(88 FR 46863).
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The Agency is proposing to consider multiple sources of data in its
evaluation of whether supply of a regulated substance is insufficient
to accommodate an application. Specifically, in developing the analysis
for each application, EPA has drawn information regarding the total
expected HFC consumption in the United States, global production of
individual HFCs used in the applications, manufacturer announcements
regarding production of specific HFCs, past and projected market trends
for an application that can inform projected demand for the HFC(s) it
uses, and allowance usage by application to date, including conferrals,
imports, and open market purchases by ASA holders, as well as
expenditures of conferred allowances by suppliers to ASA holders. EPA
is intending to consider data from all of these sources collectively in
order to gain a more complete picture of projected supply for the
relevant individual HFC(s), rather than relying on one data point. EPA
is taking comment on these and any other sources the agency should
consider when assessing insufficient supply.
EPA is proposing to assess insufficient supply on an application-
wide basis. If an application uses multiple HFCs, and the supply of at
least one of those HFCs is insufficient to accommodate the application,
EPA would consider the criterion met for the application. EPA
interprets 42 U.S.C. 7675(e)(4)(B)(i)(II) to require the Agency to
review the supply of the regulated substance for each regulated
substance an application uses. If there is an insufficient supply for
one HFC, EPA would determine that this criterion is met, and the
application would continue to be eligible for ASAs, assuming the first
criterion regarding substitutes is also met. EPA is proposing
[[Page 75907]]
that such an approach is the best interpretation of the AIM Act
direction in 42 U.S.C. 7675(e)(4)(B)(i)(II) that if both criteria are
met, ``the Administrator shall authorize the production or consumption,
as applicable, of any regulated substance used in the application.'' A
converse approach would result in EPA not renewing the ASA eligibility
of an application that has no available substitutes and there is an
insufficient supply available of a regulated substance used by that
application. EPA is interpreting the AIM Act to provide ASAs to an
application where at least one regulated substance that manufacturers
are capable of securing is insufficient to accommodate the application,
even if the supply of a different regulated substance is not
insufficient.
In addition to looking generally at the supply of HFCs, EPA is also
considering relevant restrictions, if any, on the type of HFC or
supplier of HFCs that would further limit supply to a particular
application. For example, FDA regulations govern use of pharmaceutical-
grade HFCs by MDI manufacturers. Facilities manufacturing the regulated
substances must comply with FDA regulations, and there are a limited
number of purifiers. EPA is considering any applicable relevant Federal
regulations and standards (examples listed above in Section IV.A.),
including required regulatory approvals and purity levels, that could
limit the supply of the HFC(s) used within an application.
C. What is EPA's proposed framework for renewing applications?
In outlining the requirement that EPA review the applications
eligible for ASAs at least every five years, the AIM Act states that if
EPA determines ``that the requirements described in subclauses (I) and
(II) of clause (i) are met'' then the EPA will renew the application's
eligibility to continue to receive ASAs (42 U.S.C.
7675(e)(4)(B)(v)(II)) (emphasis added). Accordingly, EPA interprets the
statutory language to mean that both criterion (I) of clause (i) (that
a substitute is not available) and criterion (II) (that supply is
insufficient) must be met for an application to be renewed as eligible
for ASAs. If either or both criteria are not met as of January 1, 2026,
EPA proposes to not renew an application's eligibility to receive ASAs.
Put another way, if EPA determines, for example, that supply is not
insufficient to accommodate an application as of January 1, 2026, EPA
would propose to not renew that application's eligibility for ASAs,
regardless of whether a substitute is available.
If both statutory criteria are met as of January 1, 2026, EPA
intends to assess whether an application's fulfillment of a criterion
may change over the following five-year period. The outcome of this
assessment would be determinative of how long EPA will deem an
application eligible to receive ASAs. For example, if EPA determines
that there is no substitute available as of January 1, 2026, but a
substitute will be available by January 1, 2028, EPA would renew the
application's eligibility to receive ASAs for only two years (i.e.,
calendar years 2026 and 2027). Similarly, if supply is deemed
insufficient to accommodate the application as of January 1, 2026, but
the market will change such that supply will not be insufficient to
accommodate the application as of January 1, 2028, EPA would renew the
application's eligibility to receive ASAs for only two years (i.e.,
calendar years 2026 and 2027).
If EPA determines that an application has a safe or technically
achievable substitute available that is a regulated substance, EPA
proposes to evaluate the supply of the substitute HFC and assess if
supply of the substitute HFC is insufficient to accommodate the
application. If the Agency did not do this, the application would not
be eligible for renewal because it had met the substitute criterion,
regardless of the supply of this substitute HFC; EPA sees this as
counter to Congress's intent when it established priority access to
allowances for these applications. Further, it is EPA's assessment that
it would be counterproductive to an application's efforts to transition
away from the currently used HFC(s) if EPA did not consider the supply
of the HFC substitute when assessing eligibility for renewal for ASAs
(i.e., if an application had insufficient supply of the substitute HFC,
an entity may be forced to return to using its original HFC). Under the
framework proposed in this rulemaking, if EPA determines there is an
HFC substitute, but there is insufficient supply of that HFC
substitute, EPA would continue to list the application as eligible for
ASAs. This approach would allow an entity transitioning to a lower-GWP
HFC to remain eligible to receive allowances until supply of that
lower-GWP HFC is no longer insufficient (or a non-HFC substitute is
identified).
EPA is also proposing that if an application is eligible to be
renewed for ASAs for less than five years, the application will not be
reviewed for eligibility for ASAs ahead of the next five-year renewal
period. The direction in the statute under AIM subsection (e)(4)(B)(v)
is to review each ``application receiving an allocation of allowances
under clause (i) or (iv) . . . not less frequently than once every 5
years,'' and, if the criteria are met, EPA shall renew the application
``for renewable periods of not more than 5 years.'' EPA interprets this
language, coupled with the lack of language in the statute directing
EPA to do another review of an application that is no longer eligible
for allowances at the end of its renewal period, as direction that EPA
is not required to re-review this application for eligibility for ASAs
ahead of the next five-year period. Congress's direction to undertake a
renewal is specific to applications receiving ASAs under 42 U.S.C.
7675(e)(4)(B)(i) and (iv). If an application is renewed for only two of
five years at this stage, when the next renewal period arises, it would
not be receiving ASAs under 42 U.S.C. 7675(e)(4)(B)(i) or (iv).
Therefore, EPA is proposing that the best interpretation of the AIM Act
language is that once EPA determines that an application is no longer
eligible for ASAs, EPA would not re-review that application at any
future time. If an application is determined to no longer be eligible
for ASAs and an entity is interested in being considered for
eligibility for ASAs again, the entity would need to petition the
Agency to be evaluated for eligibility, and the Agency would then
undertake the relevant petition review process; see Section VI of this
preamble for further discussion of the petition process requirements.
V. Review of the Six Applications Listed in the AIM Act
EPA reviewed the six applications listed in AIM Act subsection
(e)(4)(B)(iv)(I)--propellant in MDIs; defense sprays; SCPPU foam for
marine use and trailer use; the etching of semiconductor material or
wafers and the cleaning of CVD chambers within the semiconductor
manufacturing sector; MCMEU; and onboard aerospace fire suppression--as
required under 42 U.S.C. (e)(4)(B)(v)(I). Pursuant to that review, in
this rulemaking EPA is proposing and seeking comment on whether the
criteria for renewal described in Section IV of this preamble are met
for any part, or the entirety, of the 2026-2030 time period. This
section begins with an overview of total projected U.S. HFC consumption
and then proceeds into EPA's assessment of the criteria for each
application and proposed decision regarding whether to renew each
application's eligibility to receive ASAs. EPA provides additional
[[Page 75908]]
information in the TSD available in the docket for this rulemaking.
A. Overview of Total U.S. HFC Consumption
This section contains a summary of total projected U.S. HFC
consumption. We assess specific HFC supply considerations on an
application-by-application basis below. EPA provides additional
information regarding this analysis in the TSD.
The global and domestic HFC markets have been rapidly changing
since agreement to the Kigali Amendment to the Montreal Protocol in
2016.\6\ The domestic HFC market has been further changing since the
passage of the AIM Act in 2020 and the subsequent promulgation of
domestic regulations. In 2021, EPA promulgated regulations to implement
the required phasedown of HFC production and consumption in the United
States. Additional regulations coming into effect, as early as January
1, 2025, will also further alter this overall market and impact demand
for certain HFCs. EPA anticipates the market will be dynamic as it
responds to these additional regulations and continues adapting to the
global phasedown of HFCs.
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\6\ The United States ratified the Kigali Amendment in October
2022.
---------------------------------------------------------------------------
In the addendum to the HFC Phasedown Regulatory Impact Analysis
(RIA) updated for the 2023 Technology Transitions Rule (88 FR 73098,
October 24, 2023), EPA modeled total HFC consumption to be
significantly lower than the limit established by the statutory
phasedown cap for all years of the phasedown, assuming compliance with
the restrictions. The 2023 Technology Transitions Rule established
subsector-level GWP limits and restrictions on the use of certain
regulated substances. These requirements take effect as early as
January 1, 2025, and as late as January 1, 2028. While some subsectors
already use either HFCs that are below the GWP limit or non-HFC
substitutes, other subsectors will need to transition away from their
currently used HFC to comply with these regulations. In addition, the
proposed rulemaking ``Phasedown of Hydrofluorocarbons: Management of
Certain Hydrofluorocarbons and Substitutes Under Subsection (h) of the
American Innovation and Manufacturing Act of 2020'' (88 FR 72216,
October 19, 2023) (hereafter ``Emissions Reduction and Reclamation
Rule'') has proposed requirements that reclaimed and recycled HFCs be
used for certain equipment in the refrigeration, air-conditioning, and
heat pump sector and fire suppression sector (onboard aerospace fire
suppression, as an application eligible for ASAs, is currently exempt)
as early as early as January 1, 2028. If finalized as proposed, these
requirements are also expected to limit use of virgin HFCs for specific
activities (e.g., servicing for certain refrigeration and air
conditioning subsectors).\7\ In general, there is uncertainty
associated with these estimates, as they are based on expected industry
transitions in response to AIM Act rulemakings and predicted market
dynamics. If HFC consumption is lower than the amount allowed under the
AIM Act in a given year, the result may be that there are more
allowances than are needed to meet market demand in that year.\8\ If
demand for HFCs is lower than the cap, it is possible that general pool
consumption and production allowances, which are currently used to
produce or import HFCs for entities that do not hold allowances and
entities that use HFCs in an application-specific use, would be
available to allow for the production or import of HFCs for use by
entities that historically have relied upon ASAs. While current ASA
holders can access material produced using general pool allowances or
purchase HFCs on the open market, if demand by non-ASA entities is
lower than the cap, it is possible that the ``leftover'' allowances
could be used to supply ASA holders and therefore decrease the need for
ASAs. It is also possible that all allowances are used, and the HFCs
that are not sold in that year are stockpiled in anticipation of future
needs.
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\7\ See Emissions Reduction and Reclamation Rule (88 FR 72216,
72292, October 19, 2023).
\8\ The actions taken pursuant to subsection (h) and (i) of the
AIM Act did not propose to and did not accelerate the HFC phasedown.
The RIAs associated with those actions did not analyze an
acceleration of the HFC phasedown. Rather, HFCs will continue to be
available consistent with the phasedown codified at 40 CFR part 84,
subpart A, and this action does not propose to change that phasedown
schedule. Even if the requirements finalized pursuant to subsections
(h) and (i) in effect reduce the production or consumption of HFCs
used in particular sectors or subsectors faster than the scheduled
reductions under the AIM Act, that does not make those rules an
acceleration under subsection (f).
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The Agency cannot fully predict shifts in chemical production,
domestically and internationally, that may occur. As the HFC phasedown
progresses, EPA anticipates suppliers may focus their business on
supplying lower-GWP HFCs, since production and consumption of these
lower-GWP HFCs requires the expenditure of fewer allowances for the
same volume of substance.\9\ At the same time, sectors that are not yet
ready to transition and are not covered by the 2023 Technology
Transitions Rule (88 FR 73098, October 24, 2023) may continue to use
higher-GWP HFCs and could grow in size.
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\9\ In the Allocation Framework Rule, EPA established a system
whereby allowances are measured on an EV equivalent basis. 86 FR at
55142. To determine the total number of allowances needed, producers
and importers multiply the quantity of the HFC they seek to produce
or import by its EV. For example, an importer would need to expend
143 consumption allowances to import 100 kilograms (kg) of HFC-134a.
Given the variation in EVs, one would need to expend 5.3 allowances
to import 100 kg of HFC-152a.
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EPA also does not yet have data on how the market is reacting to
the 2024 stepdown in HFC allowances (from 90 percent of the HFC
consumption baseline to 60 percent of baseline); at the time of this
proposal the market is only a few months into adjusting to the 2024 HFC
stepdown, and EPA has received only one set of quarterly reports. Among
other things, data on market reactions could inform how the market will
react to the next large stepdown in 2029 (from 60 percent of baseline
to 30 percent of baseline). For example, the decrease in available
consumption allowances could encourage users of HFCs to transition
faster than projected. However, given the significant amount of HFCs in
inventory at the end of 2022, the transition away from HFCs could also
be slower than projected. Though it seems likely that demand could be
below the cap for the 2025-2028 period based on existing regulations,
it is uncertain if 2029 (the fourth year of the five-year renewal
period) will see similar space between consumption and allowed
consumption under the cap. EPA also notes the 2024 stepdown in
permissible production and consumption is unique given its scale and
that it is occurring early in the overall AIM Act implementation. There
will be significantly more information regarding the state of the HFC
market after the January 1, 2024, stepdown at the time EPA is
finalizing this proposal, and EPA intends to analyze available data to
inform its decisions regarding whether supply of individual HFCs is
insufficient to accommodate the individual applications.
In addition, there are also other constraints on supply of specific
HFCs used in the six applications that EPA is taking into consideration
(e.g., purity specifications required by Federal standards and
regulations and limited number of producers), as explained in more
detail in Sections V.B through V.G. of this preamble. Supply chain
dynamics for each of the six
[[Page 75909]]
applications could affect whether general pool allowances would be able
to be used to provide HFCs for each application.
B. Propellants in Metered Dose Inhalers
EPA has been allocating ASAs for regulated substances used for
propellants in MDIs in accordance with subsection (e)(4)(B)(iv)(I)(ff)
of the AIM Act. In the Allocation Framework Rule, EPA defined a
``metered dose inhaler'' as ``a handheld pressurized inhalation system
that delivers small, precisely measured therapeutic doses of medication
directly to the airways of a patient. MDIs treat health conditions such
as asthma and chronic obstructive pulmonary disease and are approved
for such use by the U.S. Food and Drug Administration (FDA)'' (40 CFR
84.3). Patients using MDIs to treat pulmonary conditions work closely
with their healthcare provider to identify the right treatment for
their condition. Pharmaceutical grade HFC-227ea and HFC-134a, purified
from technical grade HFC-227ea and HFC-134a, respectively, are both
used in MDIs as a propellant.
EPA is proposing to determine that no safe or technically
achievable substitute will be available for propellants in MDIs and
that supply of the regulated substance that manufacturers and users are
capable of securing from chemical manufacturers is insufficient to
accommodate this application through calendar year 2030. Therefore, EPA
proposes to renew the eligibility of entities using regulated
substances for propellants in MDIs to receive ASAs for the five-year
period of calendar years 2026 through 2030.
1. Availability of Safe and Technically Achievable Substitutes
EPA has not identified substitutes that it would propose to deem
safe and technically achievable that are available for propellants in
the metered-dose inhalers application at this time. In assessing the
availability of substitutes for MDIs, EPA reviewed information from
sources such as the FDA, the EPA SNAP Program, the TEAP's Medical and
Chemicals Technical Options Committee (MCTOC), industry, scientific
journal articles, and more, which is described in greater detail in the
TSD included in the docket for this proposed action. After reviewing
relevant information and analyses, EPA is aware of two potential
replacements for HFC-134a and HFC-227ea as propellants in MDIs,
specifically HFO-1234ze(E) and HFC-152a.
MDIs, including those containing an alternative propellant other
than HFC-134a or HFC-227ea, are subject to the approval requirements
under section 505 of the Federal Food, Drug and Cosmetic Act. The
process to develop an MDI with a new propellant is complex and will
take time. A sponsor (i.e., MDI manufacturer) will need to reformulate
the MDI product to use the new alternative propellant and conduct a
development program to obtain data, including clinical data, with the
new MDI product. If the development program is successful, a sponsor
will then need to submit an application to the FDA for approval; the
review timeline for a new drug application is 10 to 12 months. The
overall process to develop an MDI product containing a new alternative
propellant is expected to take years.
EPA regularly consulted with the FDA throughout development of this
proposed rule, and the reformulation of the majority of MDIs with an
alternative propellant may extend beyond the end of the renewal period
of 2030. EPA is aware that a few MDI manufacturers have begun the
development process, some of whom are expecting to soon begin Phase 3
trials and FDA has stated that it is possible that they may receive new
drug applications for a small number of MDI products with alternative
propellants by 2030. However, these new drug applications will need to
undergo FDA review. For new drug applications that receive FDA
approval, the commercialization plans for new MDIs are unknown but is
anticipated to take additional time. Unlike for some of the other uses
receiving ASAs where commercialization of substitutes across the entire
application after those products are first available on the market may
take a few years, for MDIs, EPA anticipates that it will take many
years before alternatives are available across the application. That
is, it will take time for reformulation, approval, and
commercialization to occur for each of the individual MDI products used
to treat pulmonary disease. For example, manufacturers of generic MDIs
may face delay in transitioning to alternative propellants, as generic
drug products must be shown to be a duplicate of, and bioequivalent to,
a previously approved drug product and rely on FDA's finding that the
previously approved product is safe and effective. Applicants request
approval for generic drug products, including MDIs, in Abbreviated New
Drug Applications (ANDAs). FDA provides its recommendations for
establishing bioequivalence in its product-specific guidances, which
for orally inhaled products like MDIs, have generally included some
combination of in vitro and in vivo studies, along with recommendations
related to the formulation and device. FDA committed to review 90% of
standard original ANDAs within 10 months from the date of submission,
but often multiple review cycles are necessitated by application
quality. This review time can be extended if a site/facility is not
ready for inspection. The timing of ANDA approval also depends on,
among other things, the patent and exclusivity protections for the
previously approved product.
According to the MCTOC 2022 Assessment Report, the transition from
HFC-134a and HFC-227ea to HFC-152a and HFO-1234ze(E) in MDIs is
expected to begin in non-Article 5 countries \10\ in 2025 and continue
through at least 2032, and no other feasible, lower-GWP MDI propellants
have been identified in the United States and abroad.\11\ HFO-1234ze(E)
and HFC-152a, along with other aerosol propellants, are listed as
acceptable by EPA's SNAP Program and are commercially available and
currently used in commercial and/or technical aerosol products.
Furthermore, they also have most of the requisite physical properties
to function as a propellant in MDIs with significantly lower GWPs than
the current HFCs in use; however, neither propellant has significant
use in pharmaceuticals today and will require extensive clinical
research and FDA approval before they could replace the current HFCs.
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\10\ Non-Article 5 countries are defined as developed countries
under the Montreal Protocol. For a list of Article 5 and non-Article
5 countries see https://ozone.unep.org/classification-parties.
\11\ See https://ozone.unep.org/system/files/documents/MCTOC-Assessment-Report-2022.pdf.
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In light of the above analysis, it is EPA's assessment that there
is no information before the Agency at the time of this proposal to
suggest that there would be a safe and technically achievable
substitute available prior to the next five-year review.
2. Supply
As previously mentioned, pharmaceutical-grade HFC-134a and HFC-
227ea (also known as HFA-134a and HFA-227ea) are currently used as
propellants in MDIs.
As part of the manufacturing process for MDIs, technical grade HFC-
134a and HFC-227ea are purified into pharmaceutical-grade HFC-134a and
HFC-227ea. Documents the FDA requires as part of the drug approval
process must specify the facility manufacturing the HFC propellant. The
supply of pharmaceutical-grade HFC-
[[Page 75910]]
134a comes from technical grade HFC-134a that is produced at a limited
number of production facilities in other countries, including a single
plant in the United States, and then purified at a single facility in
the United Kingdom and reimported to the United States for consumption
in MDIs. In its analysis of other applications, EPA has noted that HFC-
134a is the most widely available HFC. However, this fact does not
equate to a sizeable supply for the MDI application because MDI
manufacturers are not easily able to switch suppliers of
pharmaceutical-grade HFCs. Unlike other applications, where EPA has
discussed the diverse number of chemical suppliers for HFC-134a
globally, in this instance the options are constrained.
As components of drug products, the use of HFCs in MDIs are subject
to certain FDA requirements. FDA's Current Good Manufacturing Practice
(CGMP) requirements under the statute (21 U.S.C. 351(a)) apply to
drugs, including their components (21 U.S.C. 321(g)(1)), and include
requirements related to methods, facilities, controls, manufacturing,
processing, packing, and holding to assure that drugs meet requirements
for safety, identity, strength, and quality and purity. FDA has also
promulgated CGMP regulations for finished pharmaceuticals in 21 CFR 210
and 211. These CGMP regulations also contain requirements for
manufacturers in their handling, control, storage, and testing of
components used in manufacture of drug products. HFC purification
occurs in dedicated facilities that are subject to FDA CGMP
requirements for drugs and devices, as well as other international
quality standards, as MDI manufacturers may serve markets in addition
to that of the United States. If an MDI manufacturer wanted to change
their supplier of pharmaceutical grade HFC, this would trigger FDA
review. MDI manufacturers who change suppliers of pharmaceutical grade
HFCs would need to provide data to ensure the safety and quality of the
new propellant and submit the data to the FDA for review and approval.
This data may include pharmacology/toxicology data, product quality
data of the new propellant source, and a comparison of the current and
proposed new propellant sources, and quality data that demonstrates the
drug made with the new propellant meets all applicable quality
requirements. Depending upon the comparability of the HFA sources,
additional data may be requested by the FDA (21 CFR 314.70).
There are three suppliers of pharmaceutical-grade HFC-227ea for use
in the United States. One of the suppliers is a producer that purifies
the technical grade HFC-227ea at one of their facilities in the United
States. The second produces and purifies the pharmaceutical-grade HFC-
227ea at their facility in Germany, which is then imported by that
producer for distribution to domestic MDI manufacturers. The third
supplies pharmaceutical-grade HFC-227ea to the United States from their
facility in the United Kingdom. At least two of these facilities also
supply pharmaceutical-grade HFC-227ea globally for MDI manufacture.
Producers of pharmaceutical-grade HFC-227ea must also comply with FDA
requirements as described above, which limits their ability to switch
to other suppliers of HFC-227ea.
3. What is EPA proposing regarding eligibility for application-specific
allowances?
EPA is proposing to renew the eligibility of entities using
regulated substances for propellants in MDIs to receive ASAs for the
five-year period of calendar years 2026 through 2030. EPA is proposing
to determine ``that the requirements described in subclauses (I) and
(II) of clause (i) are met'' in accordance with the requirements of 42
U.S.C. 7675(e)(4)(B)(v)(II). Specifically, for the reasons outlined
earlier in this section, EPA is proposing to determine that no safe or
technically achievable substitute will be available for propellants in
MDIs and that supply of the regulated substance that manufacturers and
users are capable of securing from chemical manufacturers is
insufficient to accommodate propellants in MDIs through calendar year
2030. EPA is proposing to determine that the supply of both HFC-134a
and HFC-227ea is insufficient to accommodate the propellants in MDIs
application.
C. Defense Sprays
Per subsection (e)(4)(B)(iv)(I)(bb) of the AIM Act, EPA has been
allocating ASAs for defense sprays since 2021. EPA defined a ``defense
spray'' as ``an aerosol-based spray used for self-defense, including
pepper spray and animal sprays, and containing the irritant capsaicin
and related capsaicinoids (derived from oleoresin capsicum), an
emulsifier, and an aerosol propellant,'' (40 CFR 84.3). Within this
application, there are four primary uses: bear sprays, dog sprays,
personal defense sprays, and law enforcement sprays. The defense sprays
chapter in the TSD contains more details on these product categories.
HFC-134a is the primary propellant currently used for the majority of
defense sprays and is the only HFC for which EPA has allocated
allowances since 2022. After analyzing information relevant to the
statutory criteria, as outlined in this section and the TSD, EPA is
proposing two options--to not renew the eligibility for entities in
this application to receive ASAs or to renew for two years. EPA is also
taking comment on the possibility of renewing for a full five-year
period.
1. Availability of Safe and Technically Achievable Substitutes
There has already been commercialization of alternatives to HFC-
134a as a propellant in some defense spray uses, and transition is
underway for other parts of the application. Thus, while many defense
sprays currently use HFC-134a as a propellant, EPA is aware of entities
that have already successfully commercialized alternative propellants,
including non-HFCs, in some of their products. The availability of safe
and technically achievable substitutes for this application will
continue to expand, and EPA will take any additional information into
account in the final rulemaking.
All dog defense sprays commercialized in the United States and
registered with EPA under FIFRA use a non-HFC propellant and have never
used an HFC propellant; from company communications, EPA is aware that
at least three dog sprays utilize compressed nitrogen gas. In addition,
EPA is aware from company communications that two bear sprays using
propellants other than HFC-134a are available domestically, one using a
non-HFC, HFO-1234ze(E), and one utilizing a lower-GWP HFC, HFC-152a.
Both products have been available for multiple years. In addition,
there is one bear spray that is manufactured domestically, but sold
into the Canadian market, that also utilizes HFO-1234ze(E). EPA is also
aware of at least one defense spray used on humans available in other
countries, but manufactured in the United States, that uses HFO-
1234ze(E).
The commercialization of defense sprays with alternative
propellants suggests that there are safe and technically achievable
substitutes to HFC-134a available within this application, but it is
not clear that they are immediately available for the entire
application. In other words, there are multiple different uses within
this application, and many of the uses have similar technical
requirements (e.g., large spray volume and distance) and safety
considerations (e.g.,
[[Page 75911]]
flammability). Thus, EPA's assessment is that while there are certain
differences amongst the uses, generally a propellant commercialized for
one use should be safe and technically achievable for another use as
explained in more detail below. It is EPA's understanding that defense
sprays have industry-set technical requirements that differentiate them
from other aerosols, but that outside of FIFRA requirements for bear
sprays,\12\ defense sprays do not need to be certified or comply with
Federal regulatory standards to be sold in the United States. EPA is
aware of some voluntary standards for law enforcement sprays, explained
in more detail in the defense sprays chapter of the TSD, that specify
performance requirements and test methods for the evaluation of these
sprays. EPA's understanding is that defense sprays do not need to be
certified under this standard to be sold into the law enforcement
market.
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\12\ Defense sprays used to deter bears, dogs, and other animals
are considered pesticides under FIFRA, so must comply with related
requirements, including approval for the inert ingredients (e.g.,
the propellant) used in the product. In addition to HFC-134a, both
HFC-152a and HFO-1234ze(E) are approved for use as inert ingredients
for non-food pesticidal use (e.g., animal sprays). Transitioning a
product to another approved propellant is a relatively simple
process that only requires submission of product performance data
(i.e., no tests related to safety, impacts on human health, etc.),
and approval can occur in five to seven months. This action would be
a Pesticide Registration Improvement Act B680 or B681. See https://www.epa.gov/pria-fees/pria-fee-category-table-biopesticides-and-pollution-prevention-division-bppd-amendments for more information.
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While some entities have successfully commercialized alternative
propellants, there are steps other entities will need to undertake in
order to use these alternatives, such as their own research and
development process, approval under FIFRA for bear sprays, and
potentially changes to manufacturing facilities. For example, EPA is
aware of at least two defense spray manufacturers that had made
significant investments to potentially transition to a non-HFC as a
propellant that did not pursue the transition due to performance
concerns.\13\ The multiple defense spray products commercialized using
alternative propellants suggests that past challenges can be overcome,
though EPA acknowledges that commercialization of alternative
propellants across this entire application may take a few years.
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\13\ Written testimony submitted for the record from Safariland
and Security Equipment Corporation for the U.S. Senate Committee on
Environment and Public Works hearing on the AIM Act. https://www.epw.senate.gov/public/index.cfm/2020/3/s-2754-american-innovation-and-manufacturing-act-of-2019-written-testimony-and-questions-for-the-record.
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Outside of what has already been commercialized by some defense
spray companies, EPA is not aware of any other substances under
consideration as safe and technically achievable substitutes for this
application. Multiple propellants, including HFC-152a, HFO-1234ze(E),
and hydrocarbons, have been listed as acceptable under SNAP and
identified as technically and economically feasible alternatives for
propellants in aerosols by the TEAP's MCTOC. However, there are
additional technical demands in the defense spray application that
provide unique challenges as compared to other types of aerosol
applications. For example, given their use for personal protection and
crowd control, defense sprays need to have a larger spray cloud and
longer spray distance, and stakeholders have noted that law
enforcement's use of defense sprays alongside stun guns (e.g., Tasers)
poses specific concerns around flammability. Therefore, alternatives
identified as acceptable for aerosols, such as hydrocarbons, may not be
available for all defense spray uses. SNAP lists substitutes for
aerosols at the end use level, not the application level (e.g., the
Agency has listed substitutes for aerosol propellants, which would
allow for those substitutes in defense sprays), and TEAP's MCTOC has
not specifically discussed or evaluated defense sprays as an individual
use. More information about the specialized nature of defense sprays
can be found in the defense sprays chapter of the TSD.
To inform determinations in this rulemaking, EPA invites comment on
whether the alternatives commercialized for some defense spray uses are
not available for the entire application, including any supporting data
and information; EPA is particularly interested in data regarding
flammability of alternative propellants at the concentrations found in
defense sprays and testing results demonstrating safety risks in the
situations where defense sprays are typically utilized.
2. Supply
The majority of defense sprays currently use HFC-134a as their
propellant. HFC-134a is the most widely produced HFC globally and is
produced in substantial quantities in multiple countries, including the
United States. In 2022, domestic production of HFC-134a was 61,377
metric tons (MT), making up 46 percent of U.S. HFC production on a mass
basis; this production amount is also nearly double the domestic
production amount of the HFC produced in the second highest quantity.
EPA is aware that one domestic producer of HFC-134a is transitioning
its facility to produce a different chemical.\14\ In addition, there
are multiple entities that import HFC-134a. In 2022, 7,363.1 MT of HFC-
134a were imported into the United States. Overall, HFC-134a made up
approximately 32 percent of total U.S. HFC consumption \15\ in 2022 on
a mass basis. This application has very limited demand for HFC-134a in
comparison to U.S. consumption of HFC-134a; allocated ASAs for this
application in 2024 are equivalent to 0.1 percent of calculated
domestic consumption of HFC-134a in 2022, on a metric tons of exchange
value equivalent (MTEVe) basis. In addition, at the end of 2022,
suppliers held 51,902.9 MT of HFC-134a in domestic inventory, which is
equivalent to about 101 percent of calculated consumption of HFC-134a
in 2022, and 1,036.8 MT of HFC-134a was reclaimed; the entities both
holding this material in inventory and reclaiming these HFCs are
broader than EPA's interpretation of chemical manufacturers (see
Section IV.B for more information), so not all of this HFC-134a may be
considered available supply.
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\14\ See https://www.arkema.com/usa/en/media/news/global/corporate/2022/20221006-two-major-steps-develop-supply-forane-1233zd/.
\15\ Consumption = (Total Production + Production for Feedstock
+ Imports [Virgin and Used])-(Exports [Virgin and Used] +
Destruction).
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However, as described in more detail in Section V.A of this
preamble, the overall market for HFCs and for HFC-134a in particular is
likely to continue changing in light of the AIM Act and other
restrictions. There is uncertainty regarding how the market is reacting
to the stepdown of the level of permissible production and consumption
of HFCs that took effect on January 1, 2024, and EPA anticipates
further market changes as a result of the stepdown taking effect on
January 1, 2029. However, global production capacity is expected to
remain substantial over the coming years, given production will
continue in countries on later HFC phasedown schedules, and EPA expects
continued domestic and global demand for HFC-134a. EPA will analyze any
available information on market adjustment to the January 1, 2024,
stepdown and regulations effective January 1, 2025, in finalizing this
rulemaking.
In considering supply of the regulated substance currently used by
this application, EPA also notes that the Agency is unaware of any
reason why this application cannot use recovered and reprocessed HFCs.
For example, EPA is not aware of any specific purity
[[Page 75912]]
requirements for HFCs used in this application. As a result, the supply
of recovered and reprocessed HFCs that can be secured from chemical
manufacturers is relevant when assessing whether the supply of HFC-134a
is insufficient to accommodate this application. The likeliest source
of these reprocessed HFCs for defense sprays would be reclaimed
refrigerants, which must meet specific purity requirements.\16\ Since
there are no Federal purity requirements or industry purity standards
for HFCs used in aerosols, the purity of reclaimed HFCs is likely the
same or higher than the virgin HFCs used in this application. The
supply of reclaimed HFC-134a in the United States is substantial and
increases the supply of HFC-134a available to this application.
However, as is true in many other parts of EPA's supply analysis, there
is uncertainty regarding the overall supply and demand for reclaimed
HFCs.
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\16\ In alignment with the definition in 42 U.S.C. 7675(b)(9),
EPA defined reclaim as ``the reprocessing of regulated substances to
all of the specifications in appendix A to 40 CFR part 82, subpart F
(based on Air-Conditioning, Heating, and Refrigeration Institute
(AHRI) Standard 700-2016) that are applicable to that regulated
substance and to verify that the regulated substance meets these
specifications using the analytical methodology prescribed in
section 5 of appendix A to 40 CFR part 82, subpart F'' (40 CFR
84.3). Thus, HFC-134a refrigerant that is reclaimed and used by a
different user than the one recovering the refrigerant must meet the
purity requirements of AHRI 700, Standard for Specifications for
Refrigerants. That standard, among other things, requires that
reclaimed HFC-134a must be visibly clean (that is, no visible solids
or particulate), no more than 1.5 percent by volume of air in the
vapor phase, no more than 10 parts per million of water by weight,
and no more than 0.5 percent by weight of other volatile impurities.
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There is additional uncertainty around the supply and demand for
HFC-134a as a result of the 2023 Technology Transitions Rule (88 FR
73098, October 24, 2023). GWP restrictions under the 2023 Technology
Transitions Rule begin taking effect January 1, 2025, with the latest
restriction taking effect on January 1, 2028. Overall demand for HFC-
134a could fall since all subsectors subject to Technology Transitions
restrictions will not be permitted to use neat HFC-134a, as its GWP of
1,430 is greater than the highest GWP limit (i.e., 700). However, many
subsectors subject to Technology Transition restrictions already use
chemicals that fall below the GWP restriction levels, and where this is
the case EPA does not anticipate any change in demand of HFC-134a.
Additionally, some sectors may use blends with HFC-134a as a component
where the GWP is below the applicable limit. Moreover, HFC-134a will
likely continue to be used in other applications not subject to these
restrictions (e.g., heavy-duty trucks), as well as for servicing
existing equipment (e.g., light-duty motor vehicle air conditioning).
HFC suppliers may also shift their production and import practices,
such that supply of HFC-134a changes. EPA intends to review available
information on market shifts that occur when the first set of
Technology Transition restrictions take effect on January 1, 2025, and
where possible will incorporate any relevant information into the
analysis underpinning finalization of this rulemaking. Based on this
additional information, at finalization of this proposed rule, EPA may
be in a position to determine that the supply of HFC-134a is not
insufficient to accommodate this application once all of the Technology
Transition restrictions take effect as of January 1, 2028, if not
earlier (i.e., as early as January 1, 2026).
EPA also intends to finalize a rulemaking under subsection (h) of
the AIM Act, the Emissions Reduction and Reclamation Rule (88 FR 72216,
October 19, 2023), in the summer of 2024. EPA proposed a number of
requirements including those concerning use of reclaimed HFCs for
certain activities. In addition, EPA intends to finalize a rulemaking,
``Trichloroethylene (TCE); Regulation Under the Toxic Substances
Control Act (TSCA)'' (88 FR 74712, October 31, 2023), later this year;
this rulemaking has proposed to ban the use of TCE due to unreasonable
risk of injury to human health. If finalized as proposed, this would
prohibit TCE from being used as a feedstock to manufacture HFC-134a
within eight and a half years from when that rule is finalized. While
this could end the production of HFC-134a in the United States,\17\ it
is unclear how this change would affect overall supply of HFC-134a, as
there is currently still global supply of HFC-134a that could be
imported into the United States. EPA anticipates being able to consider
the projected effects of these other rules prior to finalizing this
rulemaking.
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\17\ Though there are other pathways to produce HFC-134a, the
pathway using TCE is the primary production pathway in the United
States, and it is EPA's understanding that it is complex to change
production pathways.
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Entities do not need to seek or receive ASAs in order to use HFC-
134a in defense sprays. Further, entities do not have to expend an
allowance to purchase HFC-134a from another entity that has imported or
produced the regulated substance. EPA notes that of the six defense
spray entities that have received ASAs at some point for calendar years
2022, 2023, and 2024, three did not receive ASAs in at least one of
those years. EPA is also aware of at least two entities selling bear
sprays that use HFC-134a that have never applied for, and therefore
never received, ASAs. This suggests that at least those two entities
were able to acquire HFC-134a on the open market without having ASAs.
These facts could suggest that ASAs may not be imperative for entities
in this application to access HFC-134a.
In sum, HFC-134a is currently more widely available than other
HFCs, and defense sprays' need for HFC-134a is small compared to the
overall demand for HFC-134a across a range of sectors. At the same
time, there is inherent uncertainty in the HFC market due to future
stepdowns and new regulations coming into effect. Further information
regarding EPA's assessment of the supply of HFC-134a related to the
needs of the defense sprays application can be found in the defense
sprays chapter of the TSD.
EPA is also considering the supply of HFC-152a, as it is used in at
least one defense spray product, as noted above. HFC-152a is produced
in substantial quantities, though the current domestic production of
HFC-152a is about half that of HFC-134a, on a mass basis.\18\ In 2022,
domestic production of HFC-152a was 29,654.9 MT, about 22 percent of
U.S. HFC production by mass. There is currently only one U.S. HFC-152a
production facility, and that producer has announced plans to increase
production by approximately 20 percent by mid-2024.\19\ At the time of
this proposal, the facility expansion is not yet complete, so EPA
cannot say with certainty when it will be available. However, there is
also substantial global production of HFC-152a, which also supplies the
U.S. market. Multiple entities imported HFC-152a in 2022, importing a
total of 5,810.1 MT. Overall, HFC-152a made up approximately 20 percent
of total U.S. HFC consumption in 2022 on a mass basis. In addition, at
the end of 2022, suppliers held 5,076.3 MT of HFC-152a in domestic
inventory, which is equivalent to about 16 percent of calculated
consumption of HFC-152a in 2022. The company that has commercialized
the bear spray using HFC-152a has never received allowances for HFC-
152a, which suggests that at least this entity is able
[[Page 75913]]
to acquire HFC-152a on the open market without having ASAs.
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\18\ See https://www.epa.gov/climate-hfcs-reduction/hfc-data-hub/expanded-hfc-data.
\19\ See https://www.chemours.com/en/news-media-center/all-news/press-releases/2023/chemours-announces-capacity-increase-of-hfc-152a-providing-reliable-domestic-supply-of-low-global-wa.
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In addition, HFC-152a has one of the lowest EVs relative to other
regulated HFCs, so fewer allowances are needed to import or produce
HFC-152a in comparison to the same volume of higher-EV HFCs. For
example, an importer would need to expend 143 consumption allowances to
import 100 kg of HFC-134a compared to 12.4 allowances to import 100 kg
of HFC-152a--a greater than 90% reduction. This means that, from a
strictly allowance-focused view, HFC-152a will be easier to acquire
than most other HFCs as the phasedown progresses and the number of HFC
allowances is reduced. Allowances allocated to an end user may
therefore not be necessary to secure production or import of HFC-152a.
Future projections suggest that there could be increased demand for
HFC-152a, although there is inherent uncertainty with how industry will
respond to the phasedown of HFCs at this early stage. HFC-152a has a
GWP that is below all the GWP limits for sectors and subsectors subject
to the 2023 Technology Transitions Rule (88 FR 73098, October 24,
2023). The 2023 Technology Transitions Rule identified HFC-152a as an
available or potentially available substitute for all 13 foam
subsectors, aerosol propellants, motor vehicle air conditioning, and
household refrigerators and freezers.\20\ However, there are also
multiple other acceptable alternatives, including non-HFCs, and, for
subsectors where a transition to another substitute has already
occurred (e.g., motor vehicle air conditioning, household refrigerators
and freezers), it is highly unlikely that a new transition to HFC-152a
would be considered. For subsectors where HFC-152a neat or in blends is
likely under consideration, it is not yet known if there will be any
significant shift toward use of HFC-152a, particularly as many relevant
subsectors have begun to move out of HFCs entirely. For example, the
MCTOC 2022 Assessment report notes that a significant proportion of
aerosols already use non-HFCs as propellants. Similarly, the FTOC 2022
Assessment Report highlights that fluorocarbon use in foams has been
falling for decades, and foams are largely expected to continue
transitioning to non-HFCs, including hydrocarbons, HFOs, and
hydrochlorofluoroolefins (HCFOs). Demand for HFC-152a may therefore
change in future years as subsectors transition to alternatives from
their currently used HFC.
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\20\ See 2023 Technology Transitions Rule (88 FR 73098, October
24, 2023) TSD ``American Innovation and Manufacturing Act of 2020--
Subsection (i)(4) Factors for Determination: List of Substitutes.''
This list is not exhaustive, so it is possible HFC-152a is an
available alternative for other subsectors. In addition, EPA did not
identify information for products or equipment containing certain
substitutes, which may indicate a lack of current commercial demands
for the substitutes in those products or equipment. However, this
did not automatically remove those substitutes from the list of
available substitutes, as commercial demands is only one subfactor
that needed to be considered under subsection (i)(4)(B).
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In sum, while there is a reasonably large supply of HFC-152a that
is expected to increase over the coming years relative to other HFCs,
there is uncertainty around future demand for the reasons described
above.
3. What is EPA proposing regarding eligibility for application-specific
allowances?
Given the rapidly changing landscape for HFC supply and EPA's
assessment of substitute availability application-wide, EPA is
proposing two options based on our current analysis and in anticipation
of additional available information before this proposed rule is
finalized. Specifically, EPA is proposing to finalize one of the
following outcomes: (1) No renewal, such that the application will not
receive ASAs or (2) Renew eligibility for ASAs for two years, such that
ASAs are available for calendar years 2026 and 2027.\21\ EPA is also
seeking comment on renewing eligibility for the full five-year period.
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\21\ The proposed amendatory text included in this Federal
Register notice shows only one of the co-proposed options. This is
for illustrative purposes and should not be read as EPA favoring one
co-proposal over another.
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As explained earlier in this proposal, an application must meet
both criteria to be eligible to receive ASAs. For the reasons described
earlier in this section, EPA is proposing to determine that there is
not a safe and technically achievable substitute that is immediately
available for the entire application, but a safe or technically
achievable substitute will be available for the entirety of the defense
spray application by January 1, 2028. In other words, EPA proposes to
determine that the criterion in subsection (e)(4)(B)(i)(I) is not met
for defense sprays starting January 1, 2028. Under this proposed
determination, even if EPA received information to determine that
supply of the currently used regulated substance was insufficient,
defense sprays would not be eligible for renewal as of January 1, 2028,
unless they have insufficient supply of a substitute HFC, as discussed
in more detail below.
EPA is also proposing to determine that either (1) the supply of
HFC-134a is not insufficient to accommodate this application; or (2)
the supply of HFC-134a will not be insufficient to accommodate this
application as of January 1, 2028. In other words, EPA proposes to
determine that the criterion in subsection (e)(4)(B)(i)(I) is either:
(1) not met at all for this application for HFC-134a, and therefore the
application would not be eligible to receive ASAs starting January 1,
2026; or (2) not met as of January 1, 2028, and therefore the
application would not be eligible to receive ASAs starting January 1,
2028. Under the first option, this means that even if the application
does not have a safe or technically achievable substitute available,
ASAs would not be available for defense spray manufacturers as of
January 1, 2026. For the second option, defense sprays would not be an
eligible application for ASAs as of January 1, 2028, regardless of the
availability of substitutes.
EPA does not have sufficient information to make a definitive
determination on whether supply of HFC-152a is insufficient to
accommodate this application at the time of this proposal. We are
monitoring this issue and will be seeking information on the
alternatives that subsectors subject to Technology Transitions
restrictions transition into and how much additional domestic
production capacity of HFC-152a comes online in the coming year.
EPA is also taking comment on whether defense sprays should be
eligible to receive ASAs for the full five-year period from 2026-2030.
A full five-year renewal could be without restriction or could be based
on and tailored only to the application's need to purchase HFC-152a. As
explained earlier, HFC-152a is used commercially in one bear spray
product, so this latter scenario could be relevant if HFC-152a is an
available safe and technologically achievable substitute for the entire
defense spray application by 2028. Under this scenario, EPA would
follow an approach similar to the option proposed for SCPPU foams for
marine and trailer uses in Section V.D.3.
EPA intends to review comments and other relevant information
received on this proposal to further understand how the market
surrounding this application evolves and the availability of
substitutes application-wide before EPA finalizes this proposed rule.
Specifically, we intend to review additional information on how the HFC
market adjusts to the 2024 stepdown, defense sprays' research into
alternative propellants and related trials (including relevant data on
flammability), what alternatives consumer aerosols transition to (as
they are subject to the
[[Page 75914]]
Technology Transitions restrictions starting in 2025), and research
into alternative propellants intended to be used in technical aerosols
(which are subject to the Technology Transitions restrictions starting
in 2028). EPA invites submission of comment and additional data related
to these data gaps. EPA will consider this new information, in addition
to public comments, in making a final determination for this
application.
4. Proposed Restriction Under EPA's Technology Transitions Program
The 2023 Technology Transitions Rule (88 FR 73098, October 24,
2023) restricts the manufacture and import of all aerosol products that
use HFCs or HFC blends that have a GWP greater than 150. This
restriction begins January 1, 2025, for all aerosols except for those
specifically listed in the final rule as technical aerosols, which have
manufacture and import restrictions starting January 1, 2028. The
listed technical aerosols are applications for which EPA received
sufficient information through the comment period or through EPA's own
analysis indicating that additional time is needed to transition to
substitutes due to various technical requirements, such as non-
flammability and/or a specific vapor pressure. The list of technical
aerosols does not include defense sprays.
The 2023 Technology Transitions Rule exempts applications that
receive ASAs (40 CFR 84.56(a)(2)). However, as finalized in the October
24, 2023, rule, if an application no longer qualifies for ASAs, the
Technology Transitions restrictions then apply.
While most aerosols are required under the Technology Transitions
Program to meet a 150 GWP limit starting on January 1, 2025, the EPA
provided additional time to comply with this limit for some technical
aerosol uses. Most of the U.S. aerosol industry subject to the January
1, 2025, compliance date has already transitioned to using propellants
that meet the 150 GWP limit,\22\ and therefore has available
substitutes for use based on EPA's consideration of the factors listed
in subsection (i)(4)(B) (e.g., technological achievability, commercial
demands, safety, consumer costs, etc.). By contrast, the uses that
received an extension for compliance with the 150 GWP limit until
January 1, 2028, 40 CFR 84.54(a)(16)(i)(A)-(O), currently use HFC-134a
(most often as a propellant) and have limitations that require
additional time ``to reformulate, test, and transition'' to ensure
availability of substitutes under subsection (i)(4)(B) for these
technical uses.
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\22\ See Household and Commercial Products Association (HCPA)
and National Aerosols Association (NAA) Technology Transitions
Petition to EPA dated July 6, 2021. Available in the public docket
at EPA-HQ-OAR-2021-0289-0037.
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EPA is proposing that defense sprays would be considered under the
Technology Transitions Program consistent with technical aerosols, with
the corresponding compliance deadlines on the manufacture and import of
defense sprays using HFCs and blends containing HFCs with a GWP of 150
or greater beginning January 1, 2028, with a three-year sell-through of
those products. Thus, defense sprays manufactured or imported prior to
January 1, 2028, could continue to be sold until January 1, 2031. As
discussed in Section V.C.1 of this preamble, while some defense spray
uses may have substitutes available in the near term that are
technically achievable and safe, EPA's proposed assessment under
subsection (e)(4)(B) is that such substitutes are not immediately
available across all defense spray uses. In particular, the
flammability or specific vapor pressure of potential substitute
propellants present availability concerns for some uses in the near
term. Consideration of technological achievability and safety, as well
as other subsection (i)(4)(B) factors, indicates that a compliance date
of January 1, 2025, for transition of all defense spray uses is not
appropriate, but the approval of substitute propellants as safe under
SNAP and TEAP analyses (see Section V.C.1), as well as EPA's assessment
that many propellant uses in this subsector have been able to
successfully transition to substitutes, provides support for EPA's
proposed finding that all defense sprays will have available
substitutes by January 1, 2028. We invite comment on whether
availability of substitutes for use in defense sprays, particularly
considering those factors enumerated under subsection (i)(4)(B),
indicates that defense sprays could in fact meet the existing 150 GWP
limit restriction if the application ceased being eligible for ASAs on
January 1, 2026. We note that given the January 1, 2028, compliance
date for the transition of the remaining aerosol sector, comments
urging the Agency to provide additional time for compliance beyond that
date will need to provide very specific and detailed information in
support of that request, speaking to the statute's factors under
subsection (i)(4) and in particular the subsection (i)(4)(B) factors.
Under the 2023 Technology Transitions Rule, the labeling
requirements are effective at the same time as the manufacture and
import restrictions, which, if EPA finalizes this action as proposed,
would be January 1, 2028. Recordkeeping and reporting provisions are
effective for all sectors and subsectors under the 2023 Technology
Transitions Rule starting January 1, 2025. EPA proposes that the
recordkeeping requirements would apply to defense spray manufacturers
and importers beginning January 1 of the year that use no longer
qualifies for ASAs, and the first report would be due March 31 of the
following year. For example, if defense sprays are no longer eligible
for ASAs in 2026, manufacturers and importers would need to keep
records as required by the 2023 Technology Transitions Rule starting
January 1, 2026, and submit their first Technology Transitions report
to EPA by March 31, 2027, even if EPA finalizes its proposal that the
150 GWP limit for the manufacture and import of defense sprays using
HFCs would not apply until January 1, 2028.
EPA requests comment on the proposal to consider defense sprays
consistent with technical aerosols for purposes of the Technology
Transitions Program and the restrictions that result from such a
classification, such as the GWP limit that would take effect on January
1, 2028, use restrictions, a three-year sell-through window for
inventory ending January 1, 2031, and labeling and reporting
requirements.
EPA has previously determined that available substitutes for use as
aerosol propellants include HFC-152a (GWP 124) and HFO-1234ze(E) (GWP
<1) (88 FR 73098, October 24, 2023). EPA is also interested in any
supporting data and information related to the availability of
substitutes and whether a different timeline is more appropriate for
transitioning in this application or for a subset of products in this
application.
D. Structural Composite Preformed Polyurethane Foam for Marine Use and
Trailer Use
The third application to which EPA has been allocating ASAs to
since 2022 is SCPPU foam for marine and trailer uses, in accordance
with subsection (e)(4)(B)(iv)(I)(cc) of the AIM Act. In the Allocation
Framework Rule (86 FR 55116, October 5, 2021), EPA defined this
application as ``a foam blown from polyurethane that is reinforced with
fibers and with polymer resin during the blowing process, and is
preformed into the required shape (e.g., specific boat or trailer
design) to increase structural strength while reducing the weight of
such structures'' (40 CFR 84.3). SCPPU foam is different from other
types of
[[Page 75915]]
polyurethane (PU) foams due to its specialized structural properties,
and it is preformed into required shapes (e.g., specific boat or
trailer design). HFC-134a is the current HFC used in the blowing
process for SCPPU foam. After analyzing information relevant to the
statutory criteria, as outlined in this section and the TSD, EPA is
proposing a range of options--to not renew the eligibility for entities
in this application to receive ASAs, to renew for two years, or to
renew access to ASAs for five years with allowances determined based on
the use of a lower-GWP HFC substitute for HFC-134a. EPA is also taking
comment on the possibility of renewing for a full five-year period
consistent with the current allowance allocation approach.
1. Availability of Safe and Technically Achievable Substitutes
EPA anticipates that SCPPU foam for marine and trailer uses'
commercialization of formulations using alternatives to HFC-134a as
blowing agents is well underway and will evolve significantly between
issuance of this proposed rulemaking and its finalization. The Agency
will consider information collected from regulated entities and other
relevant sources through the public comment period and the current
reporting requirements to inform a final determination.
EPA is aware, from manufacturer communications and reporting, of
two substitutes currently under development for this application--an
HFC-152a/cyclopentane blend and an HFO. EPA notes that SNAP has listed
both HFC-152a and cyclopentane as acceptable for all PU foams,
including rigid PU uses in both marine flotation and commercial
refrigeration (the two respective end uses for this application). Based
on information from the manufacturers of SCPPU foam for marine and
trailer uses, EPA understands that the research and development phase
for both potential substitutes is nearing completion and that companies
are nearing a phase where they will be able to commercialize use of
substitutes. If commercialization occurs as companies anticipate and as
shared with EPA, the entire application would be able to use a
substitute different from HFC-134a before January 1, 2026. According to
the information shared with EPA, one substitute seems close to being
commercialized for SCPPU foam for marine use, and the other substitute
seems close to being commercialized for SCPPU foam for trailer use. The
company that is close to commercializing use of the HFC-152a/
cyclopentane blend performed multiple early trial runs with HFOs, all
of which failed to meet their needs, so the company decided to pursue
the HFC-152a blend. On this basis, we are proposing to determine that
the HFO is not an available substitute application-wide for the five-
year period from 2026-2030, given additional research and development
trials are needed, as well as the subsequent ramp up to
commercialization. EPA understands that often different companies use
different blowing agents to produce the same foam. At this time, it is
unclear why an HFC-152a/cyclopentane blend cannot be used across the
entirety of the application and similarly whether at some future date
another blowing agent (e.g., an HFO) might be used application-wide. To
inform determinations in this rulemaking, EPA invites comment on any
potential reasons why an HFC-152a/cyclopentane blend might not be safe
and technically achievable for the entire application, including any
supporting data and information, such as trial data. While there are
two different end uses in this application, the foam used in both sub-
applications is the same (i.e., it is an SCPPU foam).
Other than an HFO and an HFC-152a/cyclopentane blend, EPA is not
aware of other safe and available alternatives at this time. There are
currently a range of alternatives identified as acceptable by SNAP and
as technically proven by the TEAP's FTOC for other PU foams, including
rigid PU uses in both marine flotation and commercial refrigeration.
Alternatives include a lower-GWP HFC (i.e., HFC-152a), hydrocarbons,
and HFOs. However, alternatives identified as acceptable for PU foams
are not necessarily available for SCPPU foam, given the unique
technical requirements for this foam (e.g., specialized structural
properties). SNAP generally lists substitutes at the sector and end use
level, not the application level (e.g., the Agency has listed
substitutes for rigid PU foam, which would allow for those substitutes
in SCPPU foam, but it has not evaluated the use of these substitutes
for SCPPU foam in particular), and TEAP's FTOC did not specifically
discuss or evaluate SCPPU foam as an individual use in its 2022
assessment report. More information about the specialized nature of
SCPPU foam can be found in the SCPPU foam chapter of the TSD.
Aside from the limitations noted above, EPA is not aware of
significant Federal regulatory restrictions on the type of substitutes
that could be considered for this application. EPA is also not aware of
any required standards that SCPPU foam needs to meet to be manufactured
and sold in the United States. The SCPPU foam chapter of the TSD
contains further information on sources consulted, and EPA invites
comment on any additional information the Agency should consider in
analyzing substitutes for this application.
After reviewing the available information, including reports on
progress made by manufacturers of SCPPU foam for marine and trailer
use, EPA has not identified a safe and technically achievable
substitute that is available at the time of this proposal, but
anticipates that substitutes will likely be available soon. We are
monitoring this issue and are seeking information from the entities
that use HFCs in this application on whether progress continues as
anticipated to inform our final determination.
2. Supply
Entities manufacturing SCPPU for marine and trailer uses currently
use an HFC-134a formulation. As described in more detail in Section
V.C.2 of this preamble, HFC-134a is the most widely produced of all
HFCs. There is substantial domestic and global production of HFC-134a.
This application's demand for HFC-134a is very small compared to
domestic consumption; allocated ASAs for this application in 2024 are
equivalent to 0.1 percent of calculated domestic consumption of HFC-
134a in 2022, on an MTEVe basis. However, as noted earlier, the global
and domestic HFC markets are continuing to adapt to regulations
promulgated pursuant to the AIM Act, including the implementation of
the phasedown of production and consumption of HFCs, and other
authorities. EPA anticipates this market will continue to change, and
EPA will analyze additional information as it becomes available ahead
of finalizing this rulemaking. Such additional information will include
whether there were immediate market shifts as a result of both the
stepdown of the level of permissible production and consumption of HFCs
that took effect on January 1, 2024, and regulations effective January
1, 2025.
In addition to changes in the HFC market due to the overall
phasedown of production and consumption, other AIM Act regulatory
programs are expected to take effect both between proposal and
finalization of this rulemaking and during the applicable period under
review in this rulemaking, as described in more detail in Section
V.C.2. These requirements may reduce demand for HFC-134a domestically
for
[[Page 75916]]
certain other uses, though EPA expects continuing demand for HFC-134a
in applications not subject to restrictions will continue. There may
also be new or expanded use of blends with HFC-134a as a component
designed to meet new restrictions. In addition, other EPA regulations
may impact domestic supply of HFC-134a, but global supply should remain
substantial in comparison to this application's demand for HFC-134a.
EPA is currently not aware of any applicable restrictions on where
this application could purchase HFCs, including any purity requirements
or regulatory restrictions on supply. As such, it is EPA's assessment
that this application may be able to use recovered and reprocessed HFCs
supplied by chemical manufacturers. This is relevant in assessing what
supply of regulated substance may be available to an application, since
in such a case EPA does not need to limit its analysis to only virgin
chemicals. The likeliest source of reprocessed HFCs for this
application would be reclaimed refrigerants, which are held to AHRI 700
standards (see footnote 17 in Section V.C.2). Since there are no
Federal purity requirements for HFCs used in foams or any industry
requirements, the purity of reclaimed HFCs is likely the same or higher
than the virgin HFCs used in this application. While EPA is not aware
of specific purity requirements for this application, EPA notes that
efficacy of blowing agents can be influenced by their composition and
purity. As described in more detail in Section V.C.2, the supply of
reclaimed HFC-134a in the United States is significant, though there is
uncertainty regarding the future demand for this material.
As part of this proposed analysis, EPA is also considering the
supply of HFC-152a. As further explained in Section IV.C, as part of
the framework for its analysis EPA is proposing to evaluate the supply
of a substitute HFC if that HFC is a safe or technically achievable
substitute for an application. As outlined in the prior section
(Section V.D.1), EPA's analysis suggests that HFC-152a blended with
cyclopentane appears to be a safe and technically achievable substitute
for this application. EPA is therefore evaluating the supply of HFC-
152a to determine whether it would be insufficient to accommodate this
application. As described in more detail in Section V.C.2, other AIM
Act regulations may increase demand for HFC-152a domestically for
certain uses, though EPA notes that many sectors where HFC-152a is a
technically achievable substitute have already transitioned to other
alternatives. Domestic production capacity is also expected to
increase, but EPA cannot say with certainty when it will be available.
Global supply should also remain substantial in comparison to this
application's demand for HFC-152a.
3. What is EPA proposing regarding eligibility for application-specific
allowances?
In light of the rapid evolution of information regarding both the
availability of substitutes for this sector (including all companies in
this application's stated plans to transition away from HFC-134a before
2026) and HFC supply, EPA is proposing a range of options based on the
current Agency analysis and in anticipation of increased available
information before this proposed rule is finalized. Specifically, EPA
is proposing to finalize any of the following outcomes: (1) no renewal,
such that the application will not receive ASAs, (2) renew eligibility
for ASAs for two years, such that ASAs are available for calendar years
2026 and 2027, or (3) renew eligibility to continue receiving ASAs for
the full five-year period with allowance amounts determined based on
the EV of HFC-152a.\23\
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\23\ The proposed amendatory text included in this Federal
Register document shows only one of the co-proposed options. This is
for illustrative purposes and should not be read as EPA favoring one
co-proposal over another.
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Before finalization of this rule, we anticipate new information to
become available on the supply of HFCs and availability of substitutes
for the application, as outlined in detail in this section. EPA will
consider this new information, in addition to public comments, in
making a final determination for this application.
As explained earlier in this section, the development of safe or
technically achievable substitutes for this application is a rapidly
evolving space, such that multiple possible outcomes can reasonably be
expected to occur through 2030. All entities that have received ASAs
for SCPPU foam for marine and trailer uses to date have told EPA that
they plan to transition to substitutes before January 1, 2026. One
potential outcome at rule finalization is that EPA depends on these
statements to determine that a ``safe or technically achievable
substitute is available for the applicable period'' for this
application. Statements from all of the companies that use regulated
substances to manufacture SCPPU foam that they will transition to
substitutes before the next ASA period could serve as a reasonable
basis to determine that safe and technically achievable substitutes are
available. There are also specific milestones that these entities have
reached, such as one company receiving a final air permit for an
expansion of the manufacturing facility that will use the HFC-152a/
cyclopentane blend, indicating the company is able to move forward with
full-scale testing and commercialization. If the entities' plans shared
with EPA remain the same at the time when EPA is finalizing this
proposed rule, particularly if they have already commercialized use of
the substitutes, it is likely that EPA would determine that a safe or
technically achievable substitute is available for this application. If
EPA makes this determination, SCPPU foam for marine and trailer uses
will not be eligible for ASAs as of January 1, 2026, even if EPA
receives information to determine that supply of the currently used
regulated substance is insufficient, unless the application has
insufficient supply of a substitute HFC, as discussed in more detail
below in this section. However, EPA recognizes there is uncertainty as
to whether plans to commercialize will remain the same, be delayed, or
be subject to unanticipated hurdles that could require additional
evaluation of this alternative. EPA also has less information regarding
the deployment of the HFO alternative outside of statements from the
entity working toward its development and commercialization. Before
finalization of this proposed rule, EPA intends to review and consider,
as appropriate, all available information, specifically regarding
expected timelines and testing data. EPA invites comment regarding the
availability of safe or technically achievable substitutes for this
application. The Agency will continue to collect information from
regulated entities and other relevant sources through the public
comment period and the current reporting requirements to inform a final
determination of whether the criterion in subsection (e)(4)(B)(i)(I) is
met.
EPA is also proposing to determine either: (1) the supply of HFC-
134a is not insufficient to accommodate this application; or (2) the
supply of HFC-134a is not insufficient to accommodate this application
as of January 1, 2028. In other words, EPA proposes to determine that
the criterion in subsection (e)(4)(B)(i)(I) is either: (1) not met at
all for this application for HFC-134a, and therefore the application
would not be eligible to receive ASAs with allowances calculated based
on HFC-134a use starting January 1, 2026; or (2) not met as of January
1, 2028, and therefore the application would not be
[[Page 75917]]
eligible to receive ASAs with allowances calculated based on HFC-134a
use starting January 1, 2028. Under the first option, this means that
even if the application did not have a safe or technically achievable
substitute available, ASAs would not be available for manufacturers of
SCPPU foam for marine and trailer uses as of January 1, 2026. For the
second option, SCPPU foam for marine and trailer uses would not be an
eligible application for ASAs as of January 1, 2028, regardless of the
availability of substitutes. However, if the available substitute is an
HFC with insufficient supply, EPA may determine SCPPU foam for marine
and trailer uses are eligible for renewal for that substitute HFC.
Given the current uncertainty over which EPA anticipates having
more clarity ahead of finalization of this proposed rule, at this time
EPA contends that it could determine that the criterion in subsection
(e)(4)(B)(i)(I) is met now, met as of January 1, 2028, or is not met at
all through the entire renewal period with respect to HFC-152a. Under
the first possible determination (supply of HFC-152a is not
insufficient now), even if the application did not have a safe or
technically achievable non-HFC substitute available as of January 1,
2026, the application would not be eligible for renewal as of that
date. Under the second possible determination (supply of HFC-152a is
not insufficient as of January 1, 2028), the application would not be
eligible for ASAs as of January 1, 2028, even if the application did
not have a safe or technically achievable non-HFC substitute. Under the
third possible determination (supply of HFC-152a is insufficient), the
application would be eligible for ASAs if there was no safe or
technically achievable non-HFC substitute for the entire application.
EPA will monitor reported data over the next year on the noted areas of
uncertainty and invites comment on this issue.
In light of the range of outcomes EPA has proposed regarding its
determinations on whether the criteria in subsection (e)(4)(B)(i)(I)
and (II) are met, EPA is proposing three potential outcomes on whether
and how SCPPU foam for marine and trailer uses may be eligible for
future ASAs: (1) not eligible to receive ASAs; (2) eligible to receive
calendar year 2026 and 2027 ASAs; and (3) eligible to receive ASAs for
the five-year period of calendar years 2026-2030 with allowance amounts
determined based on the EV of HFC-152a. EPA is also taking comment on
SCPPU foam for marine and trailer uses eligibility to receive ASAs
consistent with the current approach through calendar year 2030 ASAs.
EPA also could finalize different outcomes based on how the transition
to substitutes progresses between this proposal and rule finalization.
Under outcome (3), EPA is proposing to allocate allowances based on
an expectation that the application can use HFC-152a. To achieve this,
EPA is proposing to base the calculation of allowance allocations on
the estimated total mass of HFCs needed by the application and allocate
at the level necessary to purchase HFC-152a on an EV-weighted basis.
For example, if a company used 1,000 kg of HFC-134a and 500 kg of HFC-
152a in Year 3 (as defined by the regulatory formula; see Section VII
for further discussion of regulatory formula and proposed revisions),
and HFC-152a substituted for HFC-134a one-for-one on a gram basis for
this application, EPA would multiply 1,500 kg by the applicable average
annual growth rate (AAGR) and then by the EV of HFC-152a to calculate
the company's allowance allocation for the following year. EPA would
not limit which HFCs could be purchased for use in the application once
the allowances are issued. EPA is taking comment on whether the Agency
should apply any relevant mass conversions in this calculation (i.e.,
if an application needed more or less HFC-152a on a gram-by-gram basis
when substituting for HFC-134a) where the total mass of HFCs used would
be multiplied by a mass ratio, as appropriate, then multiplied by the
AAGR.
As outlined in detail elsewhere in this section, before EPA
finalizes this proposed rule, the Agency intends to review available
information and comments received on this proposal to get further
clarity on progress toward commercialization of substitutes, how the
overall HFC market has adjusted to the 2024 stepdown, what alternatives
are adopted by subsectors subject to 2025 Technology Transitions
Program restrictions, and how much additional domestic HFC-152a
production capacity comes online.
4. Proposed Restriction Under EPA's Technology Transitions Program
The 2023 Technology Transitions Rule (88 FR 73098, October 24,
2023) restricts the manufacture and import of foam products that use as
a blowing agent HFCs or HFC blends that have a GWP of 150 or greater
(hereafter, ``foam products''). This restriction begins January 1,
2025. Examples of items subject to this restriction include products
that are foams, such as extruded polystyrene boardstock; products for
blowing foam, such as two-part foam systems for blowing PU foam; and
products that are manufactured using foam, such as boats or
refrigerated trailers.
The 2023 Technology Transitions Rule exempts applications which
receive ASAs (40 CFR 84.56(a)(2)). However, as finalized in the October
24, 2023, rule, if an application no longer qualifies for ASAs, the
Technology Transitions restrictions would apply.
As discussed in the preamble to the 2023 Technology Transitions
Rule, the transition to non-HFC and lower-GWP substitutes is already
well underway or completed for much of the foams sector (see 88 FR
73184). EPA therefore established a uniform GWP limit of 150 for the
entire foams sector starting January 1, 2025. The sole exception to
this restriction for the foams sector was SCPPU foam for marine and
trailer uses, per their receipt of ASAs. As discussed above in Section
V.D.1, EPA proposes that while there are no safe and technically
achievable alternatives available at this time under subsection
(e)(4)(B) specifically for use in SCPPU foams for marine and trailer
uses, we anticipate, based on currently available information, that the
development of substitutes for these uses is progressing rapidly, such
that by the time EPA finalizes this action, substitutes meeting the
(e)(4)(B)(i)(I) criterion may be available. While the list of
considerations under subsection (i)(4)(B) that EPA is to factor in, to
the extent practicable, when considering availability of substitutes
for issuing restrictions under subsection (i) includes factors beyond
those characteristics listed in subsection (e)(4)(B)(i)(I), in this
instance EPA's view is that technological achievability of lower-GWP
substitutes in marine and trailer uses is the primary barrier to
transitioning away from the use of HFC-134a in these two uses. Many of
the factors listed in subsection (i)(4)(B) are not relevant to EPA's
assessment of availability of substitutes for these two uses, such as
building codes, appliance efficiency standards, and contractor training
costs. As noted in Section V.D.1 of this preamble, EPA's SNAP Program
has already listed as acceptable the potential substitutes under
consideration and the entities actively developing the substitutes and
working to bring those substitutes to market are almost certainly
considering costs to consumers and affordability for small business
consumers as part of their efforts.
We propose that the applicability of the restriction on HFC foam
blowing
[[Page 75918]]
agents in the 2023 Technology Transitions Rule to SCPPU foam for marine
and trailer uses will depend entirely on which of the three co-
proposals EPA ultimately finalizes. That is, under co-proposal (1),
where EPA would not renew ASAs for SCPPU for marine and trailer uses as
of the effective date of a final rule based on this proposal,
requirements of the Technology Transitions Program, which include
labeling, reporting, recordkeeping, and restrictions on HFCs, would
apply beginning January 1, 2026. Under co-proposal (2), where EPA would
renew ASAs for SCPPU for marine and trailer uses for 2026 and 2027,
requirements of the Technology Transitions Program would apply
beginning January 1, 2028. For both co-proposals (1) and (2), EPA
proposes that the recordkeeping requirements would apply to
manufacturers of SCPPU foams for marine and trailer uses beginning
January 1 of the year those uses no longer qualify for ASAs, and the
first report would be due March 31 of the following year, as discussed
above in Section V.C.4. For example, under co-proposal (1),
manufacturers would need to keep records as required by the 2023
Technology Transitions Rule starting January 1, 2026, and submit their
first Technology Transitions report to EPA by March 31, 2027; under co-
proposal (2), manufacturers would need to keep such records starting
January 1, 2028, and would submit their first Technology Transitions
report by March 31, 2029. Under co-proposal (3), where EPA would renew
ASAs for SCPPU for marine and trailer uses based upon the use of HFC-
152a instead of HFC-134a, SCPPU for marine and trailer uses would
continue to be exempt from the 2023 Technology Transitions Rule. The
requirements under each co-proposal for SCPPU for marine and trailer
uses are summarized in Table 2 below. EPA is interested in data and
information related to the availability of substitutes and the proposed
timeline for transitioning in this application.
Table 2--Applicability of Technology Transitions Requirements Under Co-Proposals for SCPPU for Marine and
Trailer Uses
----------------------------------------------------------------------------------------------------------------
Technology transitions Date technology Date technology
Co-proposal GWP limit and transitions labeling transitions reporting
compliance date requirements begin requirements begin
----------------------------------------------------------------------------------------------------------------
(1) No renewal of ASAs............... GWP limit of 150 January 1, 2026........ First report due March
beginning January 1, 31, 2027, including
2026. data from January 1,
2026, through December
31, 2026.
-------------------------------------------------
(2) Renew eligibility for ASAs for GWP limit of 150 First report due March 31, 2029, including data
2026 and 2027. beginning January 1, from January 1, 2028, through December 31,
2028. 2028.
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(3) Renew eligibility for 2026-2030 Because application continues to be eligible for ASAs, it is exempt from
with allowance amounts determined Technology Transitions requirements.
based on the EV of HFC-152a.
----------------------------------------------------------------------------------------------------------------
E. Etching of Semiconductor Material or Wafers and the Cleaning of
Chemical Vapor Deposition Chambers Within the Semiconductor
Manufacturing Sector
EPA has been allocating ASAs for regulated substances used for the
etching of semiconductor material or wafers and the cleaning of CVD
chambers within the semiconductor manufacturing sector in accordance
with subsection (e)(4)(B)(iv)(I)(dd) of the AIM Act. In the Allocation
Framework Rule, EPA defined ``etching'' in the context of semiconductor
manufacturing as ``a process type that uses plasma-generated fluorine
atoms and other reactive fluorine-containing fragments that chemically
react with exposed thin films (e.g., dielectric, metals) or substrate
(e.g., silicon) to selectively remove portions of material. This
includes semiconductor production processes using fluorinated GHG
reagents to clean wafers.'' (40 CFR 84.3). EPA defined ``chemical vapor
deposition chamber cleaning'' (hereafter referred to as ``chamber
cleaning'') in the context of semiconductor manufacturing as ``a
process type in which chambers used for depositing thin films are
cleaned periodically using plasma-generated fluorine atoms and other
reactive fluorine-containing fragments'' (40 CFR 84.3). At the time of
this proposal, EPA is aware of three HFCs that are used for this
application in manufacturing. HFC-23 is commonly used for selective dry
etching of silicon dioxide (SiO2) and silicon nitride (SiN),
while HFC-32 and HFC-41 are used in high-aspect-ratio hole etching.
HFC-23, HFC-32, and HFC-41 may also be minimally used in chamber
cleaning processes.
EPA is proposing to determine that no safe or technically
achievable substitute will be available for the semiconductor
application and that supply of the regulated substance that
manufacturers and users are capable of securing from chemical
manufacturers is insufficient to accommodate the semiconductor
application through calendar year 2030. Therefore, EPA proposes to
renew the eligibility of entities using regulated substances for the
defined semiconductor application to receive ASAs for the five-year
period of calendar years 2026 through 2030.
1. Availability of Safe and Technically Achievable Substitutes
EPA has not identified any substitutes that it would propose to
deem safe and technically achievable that are available for the
entirety of the defined semiconductor application.
In developing this assessment, EPA reviewed information from
industry trade groups, the TEAP's MCTOC, the Intergovernmental Panel on
Climate Change (IPCC), scientific journal articles, and more. The
sources examined by EPA are outlined in greater detail in the TSD
included in the docket for this proposed action.
The MCTOC 2022 Assessment report reviewed HFC gases commonly used
in semiconductor manufacturing, along with their alternatives, using
the following criteria: commercially available, technically proven,
environmentally sound, economically viable and cost effective, safe to
use in industrial applications considering flammability and toxicity
issues, and easy to use and maintain.\24\ Based on this report and
other sources, EPA is
[[Page 75919]]
aware that semiconductor manufacturers currently utilize other
fluorinated gases, such as sulfur hexafluoride (SF6),
nitrogen trifluoride (NF3), some saturated PFCs (i.e.,
CF4, C2F6, c-
C4F8), and some unsaturated PFCs (i.e.,
C4F6, C5F8) for the
processes of etching and chamber cleaning. The MCTOC 2022 Assessment
report lists these chemicals as both commercially available and
technically proven and can be used as substitutes for etching and
chamber cleaning. In developing its proposed determination regarding
substitutes, however, EPA did not consider many of these chemicals in
its proposed consideration of the availability of safe and technically
achievable substitutes because of their higher GWPs, lower utilization
rates (i.e., higher emission rates), or higher toxicity than HFCs.
Sulfur hexafluoride (SF6), which is used in the etching of
silicon, silicon dioxide (SiO2), and silicon nitride (SiN),
as well as chamber cleaning, has a 100-year GWP of 22,800. Nitrogen
trifluoride (NF3), which is used in the etching of silicon
and silicon nitride (SiN), as well as for chamber cleaning, has a 100-
year GWP of 17,200. Saturated PFCs, used in the etching of silicon,
silicon dioxide (SiO2), and other materials, have a 100-year
GWP ranging between 7,390 to 12,200. Saturated PFCs are also difficult
to abate and have relatively low utilization rates.
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\24\ See https://ozone.unep.org/system/files/documents/MCTOC-Assessment-Report-2022.pdf.
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Unsaturated PFCs are used in high-aspect-hole-ratio etching. They
have GWPs of less than two; however, these compounds have not been
widely adopted at least in part since these chemicals can only be used
in certain processes and are not necessarily viable for all types of
etching, etching all materials, or chamber cleaning. For example,
unsaturated PFCs are not known to be used in chamber cleaning, so the
Agency does not consider unsaturated PFCs as available for the entire
application.
The MCTOC 2022 Assessment report also lists other compounds that
are currently being studied for use but are not yet technically proven,
are not considered safe or easy to use, and may have additional
toxicity concerns. These chemicals include carbonyl sulfide, HFO-
1336mzz(E), PFC-1216, chlorine trifluoride (ClF3),
hexafluoroisobutylene (HFIB), and trifluoroiodomethane
(CF3I). Carbonyl sulfide, used in certain etching
applications, is also highly flammable and toxic. HFO-133mzz(E) is
being considered as a replacement for certain etching chemicals. PFC-
1216 is being studied for use in etching silicon dioxide
(SiO2). Chlorine trifluoride (ClF3) may be used
for chamber cleaning for Low Pressure CVD chambers but is extremely
flammable and is not considered safe or easy to use. Although not known
to currently be used, hexafluoroisobutylene (HFIB) could be used in
certain etching applications for silicon containing material.
Trifluoroiodomethane (CF3I) is used for etching of silicon
dioxide (SiO2) and silicon nitride (SiN), but the MCTOC 2022
Assessment report does not list it as safe or easy to use.
EPA is aware of certain HFCs that may be in the early stages of
research for high-aspect-ratio hole etching, such as HFC-134a and HFC-
125. ASA holders have stated that research on lower-GWP alternatives is
ongoing and there are currently no known alternatives to HFCs, PFCs,
and nitrogen trifluoride (NF3), and any alternatives would
not be commercially available until at least 2030.
In light of the above analysis, EPA has not identified a safe and
technically achievable substitute that is available at the time of this
proposal. When a substitute or substitutes are identified for the
entirety of the application, it would still take significant time to
replace the current HFC(s) with the substitute(s). One industry trade
group has stated that semiconductor technologies require at least 10
years from fundamental research to high volume manufacturing to
innovate and implement new technologies and their associated raw
materials. Given that no promising substitutes have been identified,
there is no information before the Agency at the time of this proposal
to suggest that there would be a safe and technically achievable
substitute available prior to the next five-year review.
2. Supply
HFC-23, HFC-32, and HFC-41 are all currently used in the etching of
semiconductor material or wafers and the cleaning of CVD chambers
within the semiconductor manufacturing sector. As described earlier in
Section IV.B of the preamble, EPA is proposing to determine that an
application meets this criterion if EPA determines that any of the HFCs
currently used in an application's equipment or to manufacture the
application's products for use have insufficient supply.
As described above in Section E of this preamble, HFC-23 is used in
the etching of silicon dioxide (SiO2) and silicon nitride
(SiN) and is also used minimally in chamber cleaning. In 2022, domestic
producers produced approximately 1,049.3 MT of HFC-23. 876.2 MT were
subsequently destroyed, and one producer sold 5.2 MT of this HFC-23 for
consumptive uses, which could be used for semiconductors as well as
other uses. In addition, there were about a half dozen entities that
imported HFC-23 with total amount of imports equaling 125.6 MT.
Overall, HFC-23 made up only 0.07 percent of total U.S. HFC consumption
in 2022 on a mass basis. Moreover, as HFC-23 has the highest EV, it may
be possible that this supply is further constricted in the future as
the phasedown progresses and the number of available allowances is
reduced. As stated elsewhere in this proposed rule, EPA recognizes that
there is inherent uncertainty regarding HFC production, and in
particular for HFCs with a more limited number of production facilities
and/or higher GWPs than other regulated HFCs, this uncertainty may be
greater. Therefore, EPA understands there will be changes to the market
conditions resulting from the domestic and global phasedown of HFC
production and consumption.
In addition, the use of HFC-23 in the semiconductor manufacturing
application is large compared to the annual consumption of HFC-23. In
2022, semiconductor ASA holder purchases \25\ of HFC-23 accounted for
about 81 percent of calculated consumption of HFC-23. Furthermore, at
the end of 2022, suppliers held 304.0 MT of HFC-23 in domestic
inventory, which is equivalent to about 293 percent of calculated
consumption of HFC-23 in 2022; not all of this HFC-23 may be considered
available supply, as the entities both holding this material in
inventory and reclaiming these HFCs are broader than EPA's
interpretation of chemical manufacturers (see Section IV.B for more
information).
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\25\ For this calculation, EPA is using purchases in 2022
instead of allowances allocated so that percent of consumption can
be calculated for each HFC.
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EPA also analyzed the supply of HFC-32. In 2022, the one domestic
producer of HFC-32 produced 17,744.3 MT of HFC-32. There were also over
a dozen entities that imported HFC-32, with total import quantities
equaling 9,885.3 MT. Overall, HFC-32 made up approximately 17 percent
of total U.S. HFC consumption in 2022 on a mass basis. The use of HFC-
32 in the semiconductor manufacturing application is small compared to
the annual consumption of HFC-32. In 2022, semiconductor ASA holder
purchases of HFC-32 accounted for less than 0.035 percent of calculated
consumption of HFC-32. At the end of 2022, suppliers held 21,435 MT of
HFC-32 in domestic inventory, which is equivalent to about 80 percent
of calculated consumption of HFC-32 in 2022; similar to considerations
for
[[Page 75920]]
supply of HFC-23 and for other applications, not all of this inventory
may be considered available.
Another factor EPA is considering is the impact that other
regulatory actions may have for the available supply of HFC-32. As
described in more detail above in Section V.A, the overall market for
HFCs is likely to continue changing in light of AIM Act and potentially
other restrictions. There is particular uncertainty regarding demand
for HFC-32. The 2023 Technology Transitions Rule (88 FR 73098, October
24, 2023) set a GWP threshold of 700 for certain sectors and subsectors
where previously higher-GWP HFCs or HFC blends have been used. HFC-32
has a GWP of 675 and may be a suitable alternative in those sectors and
subsectors. In other cases, the 2023 Technology Transitions Rule set a
GWP threshold of 150 and thus HFC-32 could not be used unless as a
component of blends. The first set of restrictions under the 2023
Technology Transitions Rule have compliance dates of January 1, 2025,
with the latest compliance dates taking effect on January 1, 2028.
Additionally, the proposed Emissions Reduction and Reclamation Rule (88
FR 72216, October 19, 2023) proposes requirements for the use of
recycled or reclaimed HFCs for certain uses, as discussed elsewhere in
this preamble. When finalized, that rule may affect the use of
reclaimed HFC-32.
EPA also analyzed the supply of HFC-41. There is one domestic
supplier of HFC-41 that produced 22.2 MT of HFC-41 in 2022. In
addition, there were multiple entities that imported HFC-41, with total
import quantities equaling 38.3 MT. Overall, HFC-41 made up only 0.03
percent of total U.S. HFC consumption in 2022 on a mass basis. The use
of HFC-41 in the semiconductor manufacturing application is moderately
large compared to the annual consumption of HFC-41. In 2022,
semiconductor ASA holder purchases of HFC-41 accounted for 21.5 percent
of calculated consumption of HFC-41. At the end of 2022, suppliers held
26.7 MT of HFC-41 in domestic inventory, which is equivalent to about
60 percent of calculated consumption of HFC-41 in 2022; as noted for
the supply of HFC-23 and HFC-32 and for other applications, not all of
this inventory may be considered available.
One factor that plays into the sufficiency of supply of these HFCs
is the purity specifications used by individual companies in the
semiconductor manufacturing sector. While there is no Federal standard
or regulation governing the purity of HFCs used in semiconductor
manufacturing, EPA is aware that individual companies in this sector
set their own requirements. HFCs purchased for use in semiconductor
manufacturing is produced at around 95-97 percent purity and then
typically is purified to 99.999-99.9999 percent purity before it is
used by semiconductor manufacturers. Supplying refined HFCs to end
users can take up to one year, as purifiers require long lead times.
These purity requirements are also relevant when considering if
reclaimed HFCs can be used in this application. EPA notes that virgin
HFCs produced for semiconductor use are typically only at 95-97 percent
purity, so EPA is not aware of why reclaimed HFCs cannot also be
purified to industry specifications; EPA invites comments on this. Of
the three HFCs utilized by the semiconductor industry, only HFC-23 and
HFC-32 were reclaimed in 2022 and thereby could be a source of supply
for this application, though the amount of reclaimed material is small.
In addition, it is possible to capture the unreacted process gases used
in semiconductor manufacturing, but the reclamation of fluorinated
gases from the semiconductor manufacturing process is not currently
economically viable.
There are other factors that may further impact the supply of HFCs
for this application. The Creating Helpful Incentives to Produce
Semiconductors Act of 2022 (CHIPS Act) has allocated over 50 billion
dollars to semiconductor research, development, manufacturing, and
workforce development in the United States, which has led to additional
investment by semiconductor manufacturers. The U.S. market share of
memory chip production is projected to grow from less than 2 percent to
up to 10 percent over the next decade.26 27
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\26\ See https://www.whitehouse.gov/briefing-room/statements-releases/2022/01/21/fact-sheet-biden-harris-administration-bringing-semiconductor-manufacturing-back-to-america-2/.
\27\ See https://www.mckinsey.com/industries/industrials-and-electronics/our-insights/semiconductor-fabs-construction-challenges-in-the-united-states.
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3. What is EPA proposing regarding eligibility for application-specific
allowances?
EPA is proposing to renew the eligibility of entities using
regulated substances for the etching of semiconductor material or
wafers and the cleaning of CVD chambers within the semiconductor
manufacturing sector to receive ASAs for the five-year period of
calendar years 2026 through 2030. EPA is proposing to determine ``that
the requirements described in subclauses (I) and (II) of clause (i) are
met'' in accordance with the requirements of 42 U.S.C.
7675(e)(4)(B)(v)(II). Specifically, for the reasons outlined earlier in
this section, EPA is proposing to determine that no safe or technically
achievable substitute will be available for the etching of
semiconductor material or wafers and the cleaning of CVD chambers
within the semiconductor manufacturing sector for the entire five-year
period. EPA is also proposing to determine that supply of the regulated
substance that manufacturers and users are capable of securing from
chemical manufacturers is insufficient to accommodate this application
through calendar year 2030. As explained earlier, EPA is proposing to
determine the supply criterion is met if supply of one HFC used by the
application is insufficient to accommodate the application. EPA
proposes to determine that the supply of HFC-23 and HFC-41 are
insufficient to accommodate the application for the reasons outlined in
the prior section.
F. Mission-Critical Military End Uses
EPA has been allocating ASAs for regulated substances used for
MCMEU in accordance with subsection (e)(4)(B)(iv)(I)(ee) of the AIM
Act. In the Allocation Framework Rule, EPA defined ``mission-critical
military end uses'' as ``those uses of regulated substances by an
agency of the Federal Government responsible for national defense which
have a direct impact on mission capability, as determined by the U.S.
Department of Defense (DOD), including, but not limited to uses
necessary for development, testing, production, training, operation,
and maintenance of Armed Forces vessels, aircraft, space systems,
ground vehicles, amphibious vehicles, deployable/expeditionary support
equipment, munitions, and command and control systems'' (40 CFR 84.3).
In the Allocation Framework Rule, EPA finalized an approach that treats
the allocation of MCMEU allowances differently than the other
applications given the ``complex nature of the way DOD sources and uses
HFCs for mission-critical applications,'' (e.g., significantly larger
networks of sites and users, including contractors, of HFCs than others
covered by ASAs) (86 FR 55116, 55153, October 5, 2021). EPA set up a
system whereby DOD must provide the amount of HFCs needed for mission-
critical military use and that the two agencies would ``work together
to ensure the amount necessary is available for mission-critical
military applications'' (86 FR 55116, 55153, October 5, 2021).
[[Page 75921]]
As the definition states, DOD has discretion to identify which uses
of HFCs have a direct impact on mission capability. DOD is required to
report to EPA ``the broad sectors of use covered by current mission-
critical military end uses in the next calendar year,'' per 40 CFR
84.31(h)(3)(iv). Given the complex nature of the way DOD sources and
uses HFCs for mission-critical applications, EPA has always maintained
that DOD should have discretion to request the amount of allowances
necessary to meet its mission-critical end uses and the Agency is not
altering that approach through this rulemaking.
Recognizing the sensitive nature of the application, as well as the
expert judgement that DOD has in identifying which uses of HFCs have a
direct impact on mission capability, EPA consulted with DOD throughout
development of this proposed rule, including in advance of interagency
review, and received input to support EPA's evaluation of the statutory
criteria described in Section IV of this preamble.
After analyzing information relevant to the statutory criteria, as
outlined in this section, and based on input from DOD, EPA is proposing
to determine that no safe or technically achievable substitute will be
available for the MCMEU application and that the supply of the
regulated substances that the application is capable of securing from
chemical manufacturers is insufficient to accommodate the MCMEU
application through calendar year 2030. Therefore, EPA proposes to
renew the eligibility of the MCMEU application to receive ASAs for the
five-year period of calendar years 2026 through 2030.
1. Availability of Safe and Technically Achievable Substitutes
As discussed earlier in the preamble, in situations where there are
not safe and technically achievable substitutes available for the
entirety of the application, EPA would consider the statutory criterion
regarding substitutes as being met. In public technical reports DOD
(included in the rulemaking docket), DOD identified mission-critical
end uses that do not have safe and technically achievable substitutes
available. For example, DOD uses a mixture of HFC-227ea and sodium
bicarbonate dry chemical in automatic fire extinguishing systems that
protect the crew compartments of ground vehicles. DOD has tested
potential replacements but has not identified a viable alternative to
date. There are distinct technical specifications for some mission-
critical end uses that are distinct from civil standards for the same
category of use (e.g., refrigerants and fire suppression agents). For
example, automatic fire suppression systems in ground vehicles must
meet unique military requirements for inhalation toxicity that allow
personnel to stay within the protected space for at least five minutes
after fire suppression.
Furthermore, because Congress defined this application as what is
``mission-critical,'' EPA has always acknowledged that this application
is more fluid in terms of what particular HFC uses fall within the
application. DOD may change which end uses it determines to be mission-
critical over time. This further feeds into EPA's proposed assessment
that the Agency cannot determine at this time that there will be safe
and technically achievable substitutes available for the entirety of
the application.
2. Supply
In 2021, DOD sent a letter to EPA with information regarding
mission-critical end uses at the time, including a list of six HFCs
used in the application (HFC-125, -134a, -143a, -227ea, -236fa, and -
32). EPA has determined through communications with DOD that at least
some of these HFCs continue to be utilized in mission-critical end
uses. As described in section IV.B of the preamble, EPA is proposing to
determine that an application meets this criterion if EPA determines
that any of the HFCs currently used to manufacture products or systems
for use in the application have insufficient supply.
In the analysis of other applications in this proposal, EPA has
evaluated the supply of five out of six HFCs that DOD identified as
using in 2021 (i.e., all but HFC-143a). EPA is proposing to determine
that supply of some of these HFCs is insufficient to accommodate the
application. For example, in the evaluation of supply for the onboard
aerospace fire suppression application, EPA is proposing to determine
that the supply of HFC-227ea and HFC-236fa is insufficient to
accommodate the application. This is in addition to the unique
restrictions that apply to the Defense Logistics Agency and DOD
purchasing requirements that impact the available supply of HFCs to DOD
for MCMEUs. For example, there are Buy America requirements in Federal
Acquisition Regulation (FAR) 25.1 and Defense Federal Acquisition
Regulation Supplement (DFARS) 225.1 which may restrict how DOD can
procure goods, which may include HFCs. Furthermore, as noted in the
substitutes discussion for the MCMEU application, EPA has always
acknowledged that this application is more fluid in terms of what HFC
uses fall within the application. DOD may change which end uses it
determines to be mission-critical over time. The fact that DOD may
determine that different HFCs and different annual quantities of those
HFCs are necessary for mission-critical end uses further feeds into
EPA's proposed assessment that the supply of HFCs will be insufficient
to accommodate the application.
3. What is EPA proposing regarding eligibility for application-specific
allowances?
EPA proposes to renew eligibility for DOD to receive MCMEU ASAs for
the five-year period of calendar years 2026 through 2030. EPA is
proposing to determine ``that the requirements described in subclauses
(I) and (II) of clause (i) are met'' in accordance with the
requirements of 42 U.S.C. 7675(e)(4)(B)(v)(II). Specifically, for the
reasons outlined earlier in this section, EPA is proposing to determine
that no safe or technically achievable substitute will be available for
the entirety of the application and that the supply of the regulated
substance that manufacturers and users are capable of securing from
chemical manufacturers is insufficient to accommodate the application
through calendar year 2030.
G. Onboard Aerospace Fire Suppression
EPA has been allocating ASAs for regulated substances used for
onboard aerospace fire suppression in accordance with subsection
(e)(4)(B)(iv)(I)(ff) of the AIM Act. In the Allocation Framework Rule,
EPA defined ``onboard aerospace fire suppression'' as the ``use of a
regulated substance in fire suppression equipment used on board
commercial and general aviation aircraft, including commercial-
derivative aircraft for military use; rotorcraft; and space vehicles.
Onboard commercial aviation fire suppression systems are installed
throughout mainline and regional passenger and freighter aircraft,
including engine nacelles, auxiliary power units (APUs), lavatory trash
receptacles, baggage/crew compartments, and handheld extinguishers''
(40 CFR 84.3). At the time of this proposal, EPA is aware of only one
area, lavatory trash receptacles, in which HFCs (specifically HFC-227ea
and HFC-236fa) are used in commercial aviation. For military uses, HFC-
125 has been used in engine nacelles and APUs, and HFC-236fa has been
used in a streaming application (i.e., a portable
[[Page 75922]]
extinguisher).\28\ In addition to HFC uses in commercial and military
aviation, EPA is aware that HFCs have limited usage in general
aviation, which consists of private and/or business aircraft. The
Agency seeks additional information on how HFCs are used for general
aviation and how widespread the use is.
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\28\ See https://www.epw.senate.gov/public/_cache/files/d/1/d152a591-878f-4a4d-b9c1-dc7121c06eca/9D366FF1E61F7EFFD6A71C37C92924A5.04.03.2020-boeing.pdf.
---------------------------------------------------------------------------
After analyzing information relevant to the statutory criteria, as
outlined in this section and the TSD, EPA is proposing to determine
that no safe or technically achievable substitute will be available for
the entirety of onboard aerospace fire suppression and that supply of
the regulated substance that manufacturers and users are capable of
securing from chemical manufacturers is insufficient to accommodate the
onboard aerospace fire suppression application through calendar year
2030. Therefore, EPA proposes to renew the eligibility of entities
using regulated substances for onboard aerospace fire suppression to
receive ASAs for the five-year period of calendar years 2026 through
2030.
1. Availability of Safe and Technically Achievable Substitutes
Identification of available safe and technically achievable
substitutes in this application requires considering a range of
factors, including fire suppression effectiveness, toxicity, and space
and weight considerations. EPA has not identified available substitutes
that it would propose to deem safe and technically achievable for the
entirety of the onboard aerospace fire suppression application. As
discussed earlier in the preamble, in situations where there are not
safe and technically achievable substitutes available for the entirety
of the application, EPA would not consider this statutory criterion
met.
HFCs are used in onboard aerospace fire suppression in fixed
systems for total flooding applications and in portable equipment for
streaming uses (e.g., handheld fire extinguishers). Fire suppression
agents must satisfy environmental and safety criteria, including but
not limited to acceptable ODPs and GWPs, be effective extinguishants,
and, for spaces where people would be present, have sufficiently low
toxicity such that under normal use the discharge of agent in occupied
spaces would not harm people. Other important features that are
sometimes relevant for onboard aerospace fire suppression include being
electrically non-conductive, and ``clean'' in certain applications such
as for high-value electronics, controls, or other critical systems in
the protected spaces where it is important to leave no non-volatile
residue that could damage the equipment.
As noted at the start of this section, HFCs are used in limited
areas within the application. Because there are potentially overlapping
ASAs available for a military use of HFCs, EPA has focused its analysis
of substitute availability primarily on commercial aviation. EPA is
aware of only one application where HFCs are used in commercial
aviation: lavatory trash receptacle fire extinguishing systems.
Lavatory trash receptacle systems are total flooding systems; total
flooding systems are designed to automatically discharge a fire
extinguishing agent throughout a confined space. EPA has not identified
any safe and technically achievable substitutes for lavatory trash
receptacle systems. In coming to this proposed determination, EPA
reviewed information from multiple sources including FAA, the EPA SNAP
Program, FSTOC, and the International Civil Aviation Organization
(ICAO) which is outlined in greater detail in the TSD included in the
docket for this proposed action. The FSTOC 2022 Assessment Report noted
that it is not aware of any research to develop an HFC substitute in
lavatory trash receptacle fire extinguishing systems. Furthermore,
FSTOC noted that identifying substitutes for lavatory trash receptacles
is a low priority for industry given that it makes up less than one
percent of the installed fire suppression base on board aircraft.
In developing its proposed determination, given the global effort
to find viable halon alternatives, EPA did not consider halons in its
proposed consideration of the availability of safe and technically
achievable substitutes. However, both Halon 1301 and Halon 1211 are
technically achievable and continue to be used in onboard aerospace
fire suppression. Although the onboard aerospace fire suppression
industry has relied on halons for fire suppression for decades, the
United States phased out the production and import of virgin halons in
1994 due to their high ODP. Recycled halons have been the only supply
of halons in the United States for nearly 30 years and still comprise
the majority of installed fire suppression capacity on most aircraft.
Industry has made extensive efforts to identify alternatives to halons
particularly with recent estimates from the TEAP's FSTOC that the
dwindling supply of recycled halons could lead to shortages in the next
decade.
In assessing whether there was a safe and technically achievable
substitute available, EPA also considered what alternatives are listed
for use under SNAP for fire suppression that would be relevant for
these applications. EPA notes that 2-bromo-3,3,3-trifluoropropene (2-
BTP) is listed as an acceptable substitute subject to use conditions
for use as a streaming agent in handheld extinguishers and for certain
total flooding applications (e.g., engine nacelles and APUs). FAA has
approved the use of 2-BTP in handheld extinguishers, and commercial
aircraft manufacturers have begun replacing Halon 1211 with 2-BTP
extinguishers on newly designed aircraft. As noted above, the SNAP
Program listed 2-BTP as acceptable as a total flooding agent in engine
nacelles and APUs; however, 2-BTP has not been listed as acceptable in
lavatory trash receptacles and the factors for consideration are
different from other acceptable SNAP-listed uses. For examples, use in
lavatory trash receptacles would be in a space occupied by people,
whereas use in engine nacelles and APUs are in unoccupied spaces.
Furthermore, FAA has not approved 2-BTP for any total flooding systems
to date.
As noted in the introduction to this section, in addition to the
use of HFCs for lavatory trash receptacles in commercial aviation, HFC-
125 has been used in engine nacelles and APUs on commercial-derivative
aircraft for military use. Industry has explored several other fire
suppression agents in engine nacelles and APUs, but none have proven to
be a viable solution. For example, the industry previously explored FK-
5-1-12 for use as a fire suppression agent in engine nacelles, but it
failed an FAA-required live fire test. As a result, for the purposes of
its evaluation under the AIM Act subsection (e), EPA has not identified
safe and technically achievable substitutes that are available for use
in engine nacelles or APUs.
In addition to the areas in which HFCs are used in total flooding
systems, HFC-236fa is used as a streaming agent in commercial-
derivative aircraft for military use. As previously noted in this
section, 2-BTP has been listed as acceptable by SNAP, is FAA-approved,
and commercial aircraft manufacturers have begun transitioning to 2-BTP
extinguishers on newly produced aircraft. While EPA analysis suggests
that 2-BTP is available as a safe and technically achievable
substitute, as explained elsewhere in this proposal, EPA would only
determine the statutory
[[Page 75923]]
criterion in subsection (e)(4)(B)(i)(I) is not met if the Agency
determines substitutes are available for the entirety of the
application.
If a substitute were identified for the entirety of the
application, it would still take significant time for transition to the
substitute to occur for this application. FAA has testing requirements
and minimum performance standards that a new fire suppression agent
must meet before it can be used commercially. While there is no
prescribed amount of time it takes to meet these requirements, a
stakeholder indicated to EPA in a November 2023 public stakeholder
meeting that the certification process can take three to five years.
Another stakeholder described the FAA process as arduous and noted that
it could take many years to receive certification for a new fire
suppression agent. There is no information before the Agency at the
time of this proposal to suggest that there would be a safe and
technically achievable substitute available prior to the next five-year
review.
2. Supply
As previously discussed, HFC-227ea, HFC-236fa, and HFC-125 are all
currently used in onboard aerospace fire suppression. As described in
Section IV.B of the preamble, EPA is proposing to determine that the
requirements of 42 U.S.C. 7675(e)(4)(B)(i)(II) are met for this
application if EPA determines that any of the HFCs currently used in a
commercial product or to manufacture products for use in the
application have insufficient supply.
HFC-227ea is the only regulated substance for which onboard
aerospace fire suppression allowances have been expended to date. As
previously stated, HFC-227ea is used in commercial aviation whereas
HFC-236fa and HFC-125 are used in commercial-derivative aircraft for
military use. As intended in the Allocation Framework Rule, there is
overlap between the onboard aerospace fire suppression application and
the MCMEU application. EPA is not reopening this approach through this
rulemaking, so as long as DOD continues to classify the operation of
Armed Forces aircraft as mission-critical, then DOD may use MCMEU
allowances for fire suppression equipment installed on commercial-
derivative aircraft. Therefore, in addition to HFC-227ea being the only
regulated substance for which onboard aerospace fire suppression
allowances have been expended, the uses of HFC-227ea are the only uses
for which the onboard aerospace fire suppression application is the
sole pathway to receive allowances. In 2022, the sole domestic producer
of HFC-227ea produced 1,324.7 MT of HFC-227ea, comprising one percent
of U.S. HFC production on a mass basis. In addition, there were nine
entities that imported HFC-227ea with the total amount of imports
equaling 454.2 MT. Overall, HFC-227ea made up only 0.2 percent of all
U.S. HFC consumption in 2022 on a mass basis. At the end of 2022,
suppliers held 1,008.3 MT of HFC-227ea in domestic inventory, which is
equivalent to about 323 percent of calculated consumption of HFC-227ea
in 2022; as noted in the supply discussions for the other applications
above (Sections B-E), not all of this HFC-227ea may be considered
available supply, as the entities holding this material are broader
than EPA's interpretation of chemical manufacturers. As stated
elsewhere in this proposed rule, EPA recognizes that there is inherent
uncertainty regarding HFC production, and in particular for HFCs with a
more limited number of production facilities and/or higher GWPs than
other regulated HFCs, this uncertainty may be greater; HFC-227ea has
one of the highest GWPs of the regulated HFCs. Additionally, EPA
understands there will be changes to market conditions resulting from
the domestic and global phasedown of HFC production and consumption
that could affect future supply of HFC-227ea. Given the relative size
of the market for HFC-227ea and the limited number of producers in the
United States and abroad, the supply chain for HFC-227ea is potentially
more fragile than other supply chains (e.g., HFC-134a). This makes it
more likely that the supply of HFC-227ea available from chemical
manufacturers will be insufficient during 2026-2030 for this
application.
The use of HFC-227ea in onboard aerospace fire suppression is small
compared to the annual consumption of HFC-227ea. Allocated ASAs for
this application in 2024 are equivalent to 0.8 percent of calculated
consumption of HFC-227ea in 2022. While this small usage could make it
easier for suppliers to divert a fraction of their available supply to
this application, the supply chain for HFC-227ea remains fragile for
reasons mentioned earlier in this section, including low production and
a limited number of suppliers.
Another factor EPA is considering is the impact that other
regulatory actions may have for the available supply of HFC-227ea.
Specifically, the proposed Emissions Reduction and Reclamation Rule
proposes requirements for the use of recycled HFCs for the initial
charge (i.e., installation) and/or servicing in fire suppression
systems generally, but not onboard aerospace fire suppression systems
as long as the application continues to be eligible for ASAs. If this
requirement is finalized as proposed, this could decrease the demand
for virgin HFC-227ea.
EPA also analyzed the supply of the other HFCs currently used in
this application to determine whether supply of those HFCs was also
insufficient to accommodate the application. HFC-236fa is used in
portable extinguishers in commercial-derivative aircraft. There is
currently one producer in the United States of HFC-236fa, however,
there was no domestic production reported in 2022. Globally, HFC-236fa
is produced in even smaller quantities than HFC-227ea. In 2022, there
were seven entities that imported HFC-236fa with the total amount of
imports equaling 301.4 MT. Overall, HFC-236fa made up less than 0.2
percent of all U.S. HFC consumption in 2022 on a mass basis. At the end
of 2022, suppliers held 127.5 MT of HFC-236fa in domestic inventory,
which is equivalent to about 47 percent of calculated consumption of
HFC-236fa in 2022; as noted for HFC-227ea and other HFCs discussed in
this preamble, not all of this inventory may be considered available
supply (see Section IV.B for more information). While onboard aerospace
fire suppression allowance holders have not used allowances for HFC-
236fa to date, allocated ASAs for this application in 2024 are
equivalent to 0.3 percent of calculated consumption of HFC-236fa in
2022. However, similar to the analysis for HFC-227ea, given the
relative size of the market for HFC-236fa and the limited number of
producers in the United States and abroad, the supply chain for HFC-
236fa is potentially more fragile than other supply chains (e.g., HFC-
134a). This makes it more likely that the supply of HFC-236fa available
from chemical manufacturers will be insufficient during 2026-2030 for
this application. Also, if finalized as proposed, the Emissions
Reduction and Reclamation Rule (88 FR 72216, October 19, 2023) could
result in similar changes for HFC-236fa as previously discussed with
HFC-227ea.
HFC-125 is used in engine nacelles and APUs in military use. HFC-
125 is one of the most widely produced HFCs in the world with multiple
producers in the United States and globally. In 2022, U.S. production
of HFC-125 totaled 19,175.7 MT, comprising 14 percent of U.S. HFC
production on a mass basis. In addition, there were 19 entities that
imported HFC-125 with the total amount of imports equaling 23,849 MT.
[[Page 75924]]
Overall, HFC-125 made up approximately 25 percent of total U.S. HFC
consumption in 2022 on a mass basis. At the end of 2022, suppliers held
56,208.2 MT of HFC-125 in domestic inventory, which is equivalent to
about 141 percent of calculated consumption of HFC-125 in 2022; for
reasons explained elsewhere in this preamble, not all of this inventory
may be considered available supply. Allocated ASAs for this application
in 2024 are equivalent to 0.0059 percent of calculated consumption of
HFC-125 in 2022. The 2023 Technology Transitions Rule (88 FR 73098,
October 24, 2023) is restricting the use of HFCs and HFC blends above
certain GWP limits in a number of sectors and subsectors as early as
2025. In all likelihood, demand for certain blends containing HFC-125
will decrease. However, given HFC-125 could be used in lower-GWP
blends, including blends with GWPs that are less than the relevant GWP
limits, there is uncertainty regarding how HFC-125 demand will be
impacted. A reduction in demand for HFC-125 in the refrigeration and
air conditioning sectors could result in an increase in available
supply for use in fire suppression equipment.
3. What is EPA proposing regarding eligibility for application-specific
allowances?
EPA is proposing to renew the eligibility of entities using
regulated substances for onboard aerospace fire suppression to receive
ASAs for the five-year period of calendar years 2026 through 2030. EPA
is proposing to determine ``that the requirements described in
subclauses (I) and (II) of clause (i) are met'' in accordance with the
requirements of 42 U.S.C. 7675(e)(4)(B)(v)(II). Specifically, for the
reasons outlined earlier in this section, EPA is proposing to determine
that no safe or technically achievable substitute will be available for
onboard aerospace fire suppression and that the supply of the regulated
substance that manufacturers and users are capable of securing from
chemical manufacturers is insufficient to accommodate onboard aerospace
fire suppression through calendar year 2030. As explained earlier, EPA
is proposing to determine the supply criterion is met if supply of one
HFC used by the application is insufficient to accommodate the
application. EPA proposes to determine that the supply of HFC-227ea and
the supply of HFC-236fa are insufficient to accommodate the application
for the reasons outlined in the prior section.
VI. What are the proposed requirements associated with a petition to be
listed as an application that will receive application-specific
allowances?
The Agency is proposing a procedural framework for a petition filed
pursuant to 42 U.S.C. 7675(e)(4)(B)(ii) requesting the designation of
an application as eligible for ASAs. Subsection (e)(4)(B)(ii) outlines
requirements that apply if the Administrator receives a petition
requesting consideration of eligibility for ASAs. In the event a
complete petition is received, the Agency would make a determination on
whether to designate the application as eligible for ASAs after
considering the criteria listed in 42 U.S.C. 7675(e)(4)(B)(i). The AIM
Act specifies a timeline by which the Agency must consider these
petitions. Within 180 days, the Agency must make the complete petition
available to the public and propose and seek comment on whether to
designate the application as eligible for ASAs and if so, the requisite
number of allowances. Within 270 days of receiving the petition, the
Agency must take final action on the petition.
In order to have sufficient information to evaluate a petition
based on the criteria in subsection (e)(4)(B)(i), EPA is proposing to
require that certain information must be included in order for a
petition to be considered complete. The Agency envisions that petitions
could be submitted by a single entity, such as a company or trade
association, or a group of entities. The information listed as required
is not meant to be a comprehensive list of what a petition may include,
but rather a minimum threshold after which the Agency would consider a
petition complete. EPA would only consider the statutory timeline
triggered upon the filing of a complete petition. If the Agency were to
receive a petition that did not include all required elements listed in
this section, EPA proposes that it would consider that petition
incomplete. In the event that an entity filed an incomplete petition,
EPA would notify that entity that their petition was incomplete, but
not process the petition any further. After a petition is submitted, if
the petitioner supplements the petition, EPA would consider the
petition to be re-submitted, and the statutory timelines for action
would restart. New information may fundamentally alter the merits of a
petition and therefore EPA would have to restart its review in order to
account for new information holistically. Comments on EPA's proposed
determination would not restart the statutory timelines unless the
petitioner formally requested to supplement or revise their petition.
EPA proposes that a complete petition must include, at a minimum:
A description of the application, including an explanation
of what the application is, what purpose or function it achieves, and
what populations or commercial products benefit from the application;
A list of regulated substances and description of their
use in the application and an explanation as to why HFCs are required
in the application;
Evidence that no safe or technically achievable
substitute, including not-in-kind technologies, is or is expected to be
available, and that the petitioner has conducted research to evaluate
substitutes for the HFC(s). Examples of evidence that may be accepted
include, but are not limited to, third-party analyses and technical
reports by recognized experts in the field, test results evaluating
potential substitutes on safety and technical achievability, decisions
by EPA to list alternatives under the SNAP Program, or Federal
regulatory standards that inhibit the ability of the application to
transition to a substitute;
Evidence that supply of the regulated substance(s) used in
the application is insufficient to accommodate the application.
Examples of evidence that may be accepted include, but are not limited
to, signed and notarized communication from responsible corporate
officers at multiple representative suppliers and potential suppliers
for the sector or related sectors that the application falls in stating
that the currently used HFCs cannot be sourced; signed and notarized
communication from responsible corporate officers at 10 or more
allowance holders, including at least three of the 10 largest
consumption allowances holders, stating that the currently used HFCs
cannot be sourced;
A signed certification from a responsible corporate
officer at the requesting entity that the application cannot use
recovered and reprocessed HFCs in conjunction with or in place of
virgin HFCs, either due to demonstrated lack of technical achievability
or insufficient supply, and an explanation and evidence documenting why
recovered and reprocessed HFCs cannot be used for the application;
Total quantity (in kg) of all regulated substances
acquired for the application specified in the petition in each of the
previous three years, including a copy of the sales records, invoices,
or other records documenting that quantity; if multiple entities are
[[Page 75925]]
submitting a joint petition, they must each provide EPA with
unaggregated entity-specific information, which may be transmitted
jointly or individually;
The name of the entity or entities supplying regulated
substances for and contact information for those suppliers over the
past three years; if multiple entities are submitting the petition,
they must each provide this information individually to EPA;
Total quantities (in kg) of regulated substances held in
inventory as of the date the petition is submitted; if multiple
entities are submitting the petition, they must each provide this
information individually to EPA;
An estimate of the total quantity of HFCs the petitioner
expects to purchase in the first year it would be eligible for ASAs;
Data on the proportion of the overall cost of the product
or system that reflects the cost of regulated substances; if multiple
entities are submitting the petition, they must each provide this
information individually to EPA;
Historic and projected sales of the product or system; if
multiple entities are submitting the petition, they must each provide
this information individually to EPA;
Evidence of research into design changes to decrease the
amount of HFCs used in the product or system;
An explanation regarding whether the use of the regulated
substance is necessary for the health, safety, or is critical for the
functioning of society (encompassing cultural, intellectual, and
economic aspects);
An explanation regarding steps taken to minimize the use
of the regulated substance and any associated emission of the HFC(s);
and
Information on regulatory restrictions related to possible
alternatives and substitutes.
Requiring minimum information be included in order for the Agency
to deem a petition complete and process that petition would help
provide clarity for the Agency and ensure timeliness and transparency
for the petitioner. If EPA does not take this approach, it could
prevent EPA from having sufficient data to determine whether the
application warrants receiving ASAs and would unnecessarily delay a
response from the Agency. This would mean that a petitioner would have
to wait longer to re-submit a petition if a necessary element were
omitted from the original submission. EPA seeks comment on the proposed
petition process, including all of these proposed elements and the
associated burden with providing such information to the Agency.
In addition to proposing to establish required elements of a
complete petition, EPA is providing a non-exhaustive list of other
elements that are optional, but the Agency may find compelling or
helpful in making a determination on a petition:
Market research on the application, which could include:
an estimate of the number of domestic entities within the application;
an estimate of the amount of bulk HFCs used domestically within the
application; an estimate of the projected annual growth rate for the
duration of the period for which the application is seeking eligibility
to receive ASAs, with supporting evidence by third-party sources;
Economic research on the elasticity of demand for products
or systems within the application, with supporting evidence by third-
party sources;
Research on whether products or systems in the application
outside of the United States have had success in transitioning to
substitutes or otherwise reducing use of HFCs;
Other information that may be relevant as the Agency
evaluates the petition, based on the factors listed in subsection
(e)(4)(B)(i).
EPA notes that for an entity to be eligible to receive ASAs in a
given calendar year, a complete petition should be submitted no later
than January 31 two calendar years prior to provide the Agency
sufficient time to review a petition and be able to issue allowances in
advance of the statutory deadline of October 1 each year. For example,
if an entity would like to receive allowances in calendar year 2027,
the entity should submit a complete petition no later than January 31,
2025. EPA is setting this clear expectation so entities can factor this
into their planning when deciding to petition EPA to be added to the
list of eligible applications. This proposed timeline would allow the
Agency the requisite time to review and take final action on the
petition, consistent with the statutory timeline in subsection
(e)(4)(B)(ii), and also issue a final rule to effectuate that decision
in 40 CFR 84.13.
EPA proposes to allocate allowances to entities in a new
application through the same manner as other entities receiving ASAs,
per 40 CFR 84.13 and 40 CFR 84.31(h). EPA contends that allocating
allowances based on the established regulatory approach would be the
fairest and most transparent method of determining allowance
allocations for entities in a new application. While EPA is proposing
that a petition be required to include some of the information that
would be necessary to determine an allowance allocation, it is possible
that not all entities within an application would be involved in the
submission of the petition. In other words, having entities within a
new application request ASAs by July 31 like all other applications
(per 40 CFR 84.13(b)) would ensure that all entities in a new
application have equal opportunity to request allowances. This may mean
that in cases where there is a final rule pending to add an application
to the list of entities eligible for ASAs at 40 CFR 84.13, any entity
wishing to be eligible for ASAs in the next calendar year would need to
provide the information required at 40 CFR 84.13(h)(2) by July 31.
EPA proposes that if a petition is granted and a new application is
listed as eligible to receive ASAs, that eligibility would apply until
the end of the five-year review cycle during which its petition was
granted. Per subsection (e)(4)(B)(v), EPA must review each ASA use
receiving an allocation of allowances not less frequently than once
every five years. EPA proposes that, at the end of each five-year
review cycle, it will review any applications listed in 40 CFR 84.13(a)
at the time of review, regardless of how they were initially included
on the list. For example, the five-year review period covered in this
proposed rule includes calendar years 2026 through 2030. If a petition
were granted to receive ASAs starting for calendar year 2028, that
application would be eligible for calendar year 2028, 2029, and 2030
allowances, and then EPA would review the eligibility for that
application to continue receiving ASAs starting with calendar year 2031
allowances.
Consistent with the reporting requirements under 40 CFR 84.31(a),
EPA is proposing that all reports, petitions, and any related
supporting documents must be submitted electronically in a format
specified by EPA; \29\ and quantities of regulated substances must be
stated in terms of kilograms unless otherwise specified. EPA is
proposing that these records and copies of reports required by this
section must be retained for three years.
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\29\ Currently, most HFC reports under the AIM Act are submitted
through the HAWK module in the electronic Greenhouse Gas Reporting
Tool (eGGRT).
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VII. Proposed Revisions to Existing Regulations
EPA finalized an approach under the Allocation Framework Rule for
issuing ASAs for the initial years after enactment of the AIM Act. EPA
set up a framework to determine ASA
[[Page 75926]]
allocations for calendar years 2022 through 2025 for five of the six
applications identified in the AIM Act: propellants in MDIs; defense
sprays; SCPPU foam for marine use and trailer use; etching of
semiconductor material or wafers and the cleaning of CVD chambers
within the semiconductor manufacturing sector; and onboard aerospace
fire suppression. As explained in more detail in the Allocation
Framework Rule, EPA allocates ASAs differently for MCMEU, given the
complex nature of the way DOD sources and uses HFCs in the mission-
critical context (86 FR 55116, 55153, October 5, 2021).
The 2024 HFC Allocation Rule did not reopen the methodology for
issuing ASAs but noted that the Agency had begun development of this
proposed rule to review and consider whether to renew eligibility for
each of the six applications for ASAs and would herein consider
revisions to existing regulatory requirements (88 FR 46836, 46840, July
20, 2023). As EPA foreshadowed in the 2024 HFC Allocation Rule, the
Agency is proposing targeted regulatory changes after considering
whether any changes should be made to the existing regulatory
requirements governing ASAs based on implementation over the past
several years. EPA is also proposing one specific regulatory change to
clarify how EPA's regulations would apply to any illegally imported
HFCs that are seized and auctioned by enforcement officials, proposing
to require exporting companies to report ITNs quarterly, and proposing
to simplify the ``date of purchase'' requirement for a RACA.
Under the current regulations established in the Allocation
Framework Rule, EPA issues ASAs based on multiplying the company's HFC
use in the prior year by the higher of:
[cir] The AAGR of use for the company over the past three years; or
[cir] The AAGR of use by all entities requesting that type of ASA
(e.g., for MDIs) over the past three years.
For the calculation of AAGR, EPA calculates the growth rate between
the first and second year plus the growth rate between the second and
third year, divided by two. The formula is as follows:
[GRAPHIC] [TIFF OMITTED] TP16SE24.005
EPA relies on activity from July 1 to June 30 for each of the three
preceding years prior to the annual allocation because of the biannual
reporting deadlines and to include the most recent year of data prior
to the October 1 allocation deadline in the allowance allocation
determinations. EPA established the information an entity requesting
ASAs must provide in 40 CFR 84.31(h)(2). EPA is proposing to codify the
existing practice such that entities reporting on or applying for ASAs
provide supporting documentation to verify reported data on total
quantities of HFCs acquired through conferring allowances, expending
allowances for direct import, purchases without expending allowances,
and quantity held in inventory.
EPA also established that the Agency would consider unique
circumstances that are not reflected by the rates of growth calculated
in the methodology outlined above that are also factually documented
when determining allowance allocations. EPA finalized the following
circumstances as potentially meriting an increased allocation to an
individual company beyond historical growth rates: (1) additional
capacity will come on line in the next year, such as a new
manufacturing plant or expanded manufacturing line, (2) a domestic
manufacturer or some of its manufacturing facilities has been acquired,
and (3) a global pandemic or other public health emergency increases
demand for use of HFCs in an application, such as an increase in
patients diagnosed with medical conditions treated by MDIs. These
scenarios could provide reasons to increase allowance allocations to
affected companies in the affected years. Furthermore, if a company
wanted to make a claim that it qualifies for individualized treatment
due to one of these unique circumstances, the company must sufficiently
document in a verifiable way why it qualifies. Specific documentation
includes, but is not limited to, recent invoices for new tools; permit
documentation for new facilities, facility expansion, or installation
of equipment related to retooling; agency or company press releases for
the launch of new products; or Securities and Exchange Commission
filings documenting facility acquisitions or expansions. Ultimately,
accommodating unique circumstances that are fully documented and proven
help the Agency fulfill Congress's mandate that EPA ``allocate the full
quantity of allowances necessary'' (86 FR 55116, 55151, October 5,
2021). As a result of the multiple allocations between 2021 and 2023
and the lessons learned through this process, EPA is now proposing
limited changes to these existing regulations.
Specifically, EPA is proposing: to require companies provide the
total expected amount of HFCs they intend to purchase in the calendar
year, to expand permissible scenarios that could qualify as unique
circumstances, a different allocation methodology for certain very
small users of HFCs and entities with irregular purchasing history, how
to account for inventory in allocation decisions, new requirements for
conferrals of MCMEU allowances, to establish a pool of set-aside
allowances for situations that meet the criteria for unique
circumstances related to medical conditions treated by MDIs, and to
allow ASA holders to return a portion of their allowances voluntarily
if they do not intend to use them. EPA is proposing other specific
regulatory changes to: clarify how EPA's regulations would apply to any
illegally imported HFCs that are seized and auctioned by enforcement
officials, require exporting companies to report ITNs quarterly, and
simplify the ``date of purchase'' requirement for a RACA.
A. Expected Total HFC Purchases
Under EPA's current program, entities may voluntarily state the
total amount of HFCs they expect to purchase for the next year. EPA has
encouraged entities to provide this data on a voluntary basis to
provide an additional data element for the Agency to consider in making
allocation decisions.
EPA proposes to amend the regulations to require all entities to
provide their total expected HFC purchases for the next calendar year
as a component of overall applications due July 31 for ASAs for the
following calendar year. Under this proposed requirement, entities
would be required to provide an estimate of the total quantity of HFCs
they expect to purchase next year based on their expected eligibility
for allowances. EPA will allocate at that level if it is lower
[[Page 75927]]
than what that entity is eligible for based on the regulatory formula.
EPA is proposing this approach to better understand each entity's
HFC needs in the next year. The regulatory allocation methodology
established in the Allocation Framework Rule, and outlined at the start
of this section, is designed to determine an allocation based on
``projected, current, and historical trends.'' However, this formula
may not fully take into account other considerations that could impact
an entity's HFC needs in the next year. This proposed approach may also
avoid overallocation at the expense of general pool allowance holders.
B. Unique Circumstances
Under EPA's current regulations, entities may request that EPA
consider unique circumstances that are not reflected by the rates of
growth calculated. Entities ``must provide additional information if
requesting that EPA consider unique circumstances'' under 40 CFR
84.13(b)(1). EPA is proposing to codify into the regulations the
Agency's existing practice of requiring entities to provide supporting
documentation to verify any claimed need. EPA previously codified three
situations that would be considered as unique circumstances (40 CFR
84.13(b)(1)). After multiple allocations and many conversations with
stakeholders, EPA is proposing to add to the list of unique
circumstances under which EPA may allocate additional allowances beyond
what is calculated from the regulatory allocation formula. EPA is also
proposing to broaden the third unique circumstance related to MDIs.
First, EPA is proposing to create a unique circumstance for
economic disruption outside the immediate control of the entity
applying for ASAs, such as an economy-wide recession or other
documented short- to medium-term market events that negatively impact a
company's operations, such as a strike that affects product demand or
supply chain disruption. EPA proposes to consider this situation as a
unique circumstance as such an event could lead to an increased need to
purchase HFCs beyond what is reflected in the regulatory formula, but
likely would not be captured under an existing scenario that EPA would
consider as an acceptable unique circumstance. If finalized, entities
would still have to submit documentation that verifies that this
situation has taken place, the current status of the market event
(e.g., whether it has concluded and demand for the HFCs has returned),
and that this situation has materially impacted an entity's HFC needs.
The entity would also have to provide supporting documentation to
justify the projected amount of HFCs needed, including explaining how
projections compare to pre-market event use.
EPA is also proposing to add building a stockpile of a specific HFC
as a scenario which EPA would consider a unique circumstance in the
event a major producer for an application announces they will be
ceasing production of the HFC used by the application-specific entity
in the near future. An entity could request additional allowances for
the purpose of building inventory ahead of the cease in production. For
an entity to be eligible for additional allowances under this unique
circumstance, EPA proposes that the entity must provide EPA with a
letter from their supplier signed by a responsible corporate officer
\30\ stating that the supplier is ceasing all production of the HFC at
issue within three years. Further, EPA proposes that an eligible entity
must certify that they have regulatory requirements beyond the 40 CFR
part 84 requirements that limit its ability to switch suppliers or
there are no other suppliers that could meet their needs (e.g., because
there no other chemical manufacturers that can supply the needed HFC).
EPA proposes to also require evidence that the entity has a restricted
HFC supply chain, such as required purity requirements. If additional
allowances were granted because of this requested unique circumstance,
EPA proposes to require reporting specific to the building of inventory
by the entity that would be allocated ASAs in advance of their
supplier's production facility ceasing production. Such inventory
buildup must be held by the entity that is allocated allowances, and
EPA would subtract those quantities from the entity's purchase history
such that it is not included in the regulatory formula to determine the
entity's allocation the following year.
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\30\ EPA is also proposing to define this term, which is used
elsewhere under the HFC Allocation Program. For purposes of 40 CFR
part 84, subpart A, EPA is proposing that responsible corporate
officer and responsible official mean a person who is authorized by
the regulated entity to make representations on behalf of, or
obligate the company as ultimately responsible for, any activity
regulated under 40 CFR part 84, subpart A.
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EPA is also proposing to expand the scope of the unique
circumstance for a global pandemic or other public health emergency
that increases patients diagnosed with medical conditions treated by
MDIs to include ``healthcare system needs.'' EPA notes that the
reference in the regulations to an ``other public health emergency'' is
not limited to situations where the Department of Health and Human
Services (HHS) has officially declared a public health emergency. The
proposed expansion of the unique circumstance is a direct outgrowth of
experience over the past three years of implementing the phasedown and
is designed to ensure a sufficient volume of HFCs is available to
manufacture MDIs to treat asthma, chronic obstructive pulmonary
disease, and other respiratory diseases when unexpected market events
occur.
EPA proposes to define a healthcare system need as circumstances
where an increase in demand for MDIs used to treat asthma, chronic
obstructive pulmonary disease, and other respiratory diseases may occur
because of a change in market conditions that otherwise would not be
included in calculated rates of growth. If finalized, EPA intends to
consult closely with the FDA and potentially HHS more broadly before
allocating allowances for ``healthcare system needs.''
Examples of the types of events that could fall into a healthcare
system need include, but are not limited to:
A manufacturer that makes MDIs outside of the United
States stops selling approved MDI products in the United States;
Major recall or suspension of production of alternative
(non-MDI) emergency asthma treatments prompting increase in MDI demand;
Change in preferred products from pharmacy benefit
managers or State Medicare programs to patients;
FDA compliance or enforcement actions that impact MDI
market dynamics by reducing availability of generic drug products that;
Significant increase in respiratory infections in general
population (e.g., respiratory syncytial virus (RSV), coronavirus
disease (COVID)); and
Decrease in availability of active pharmaceutical
ingredient or device component for one or more MDI manufacturers
causing a supply shortage.
C. Methodology for Entities With Irregular Purchasing History and Very
Small Users
EPA has observed that there are certain entities with purchase
patterns for which the regulatory formula either is not able to
calculate an allocation or applying the terms of the regulatory formula
would produce absurd results. For these entities, EPA is proposing an
alternative approach for calculating the quantity of allowances each
entity is eligible to receive. Specifically, EPA is proposing to create
an alternative
[[Page 75928]]
method of allocating to entities that are either of the following: (1)
Entity has small purchases of HFCs (<100 kg) at least one of the last
three years where their purchase history would result in 200 percent or
higher AAGR of use for the company over the past three years, or (2)
entity's growth rate cannot be calculated because it had zero purchases
in one of the last three years for reasons other than newly using HFCs.
For entities that fall into either category, the Agency is proposing to
allocate the highest, as measured in exchange value equivalent (EVe),
verified purchase amount in the last three years.
With respect to the first category, EPA is proposing these cutoff
numbers to allow for some narrow flexibility in an entity's purchasing
patterns and to recognize the variability for entities that purchase
relatively small quantities of HFCs. EPA is proposing to move away from
applying the existing regulatory formula for entities where a
relatively small fluctuation in purchasing measured on a mass basis
would result in an extraordinarily large and nonsensical growth rate.
EPA reviewed data from the past three October 1 allocation cycles and
found that the top three highest entity-specific AAGRs from each of the
allocation cycles ranged from about 125 percent or higher, with the
lowest ``small use'' of HFCs in a particular year of less than 5 kg.
Thus, the Agency is proposing 200 percent as the AAGR cutoff and less
than 100 kg as the ``small use'' cutoff.
For the second category, it is mathematically impossible to
calculate a growth rate based on zero purchases in a year under EPA's
existing regulatory formula. Entities that had zero purchases in one of
the three years under consideration would also have to be determined to
be an active purchaser prior to a year with zero purchases. It is not
EPA's intent to capture entities that are new in an application under
this alternative pathway.
EPA is separately proposing a different allocation approach for all
very small purchasers of HFCs. EPA is proposing to define entities in
this category as anyone whose HFC purchases add up to less than 100 kg
in each of the previous three years. The Agency recognizes there are
certain entities that purchase the same small quantities of regulated
substances every year who may not follow a growth-oriented use similar
to that of entities that use HFCs in wide-scale, commercial operations.
Examples of these uses could include those meant for small batch use in
one of the eligible applications for research and development and/or
entities that may not yet be manufacturing commercially if, for example
in the case of MDIs, the entity is still in the product development
phase, is only manufacturing small numbers of MDIs (e.g., for clinical
trials), and is waiting for final FDA approval. For these entities, EPA
proposes to allocate the highest, determined on an EVe basis, of an
entity's past three years' worth of purchases, since their use stays
relatively consistent over time. EPA is taking comment on whether the
Agency should look back further at up to five years' worth of purchase
history. EPA based this number on the past three October 1 allocation
cycles, and reviewed purchasing patterns for the smallest purchasers
who are not new to the HFC market and would not be considered entities
with irregular purchase histories. EPA is taking comment on the cutoff
threshold on what size purchases would allow for an entity to be
considered a ``small user.'' EPA is also soliciting comment on whether,
combined with this approach or as an alternative to this approach, EPA
should round allowance allocations for very small purchasers to account
for purchase of a specific cylinder volume. In order to take this
approach, EPA requests comment on the typical cylinder volume sizes
used in these small purchases. EPA would also require eligible
applicants to provide information on the cylinders being purchased in
their biannual reporting.
D. Average Annual Growth Rate Calculations
EPA currently calculates AAGR on an MTEVe basis. This process
involves converting the mass (e.g., kilogram) of each HFC into MTEVe
and summing those MTEVe quantities across each year, before applying
the AAGR formula described earlier in this section. The Agency is
providing courtesy notice of a change going forward to calculate AAGR
on a mass basis. This new process would be based on summing all HFCs
together for each year to get a total quantity based on mass and using
this mass quantity in the AAGR formula. AAGR calculations are not
codified in the regulations, so this is not a regulatory revision, but
EPA is providing this notice given broader methodology changes proposed
in this rulemaking.
EPA is modifying this calculation because we are concerned that as
entities transition to lower-GWP HFCs, an AAGR calculated on an MTEVe
basis will not appropriately reflect their projected demand for HFCs in
the upcoming calendar year. For example, under an MTEVe-based AAGR
calculation, an entity transitioning to a lower-GWP HFC, which has an
associated lower EV, could have a negative AAGR while simultaneously
experiencing a growth in actual HFC usage. In this situation, the
entity would be allocated an amount of allowances lower than its
current year's HFC use. While entities will require fewer allowances to
purchase these lower-GWP HFCs, until a company has a full three years
of purchase data with this lower-GWP HFC, the calculated allowances may
be substantially less than projected demand, either increasing by too
small an amount or in some cases declining despite an actual increase
in demand. It would be a perverse outcome for entities to receive an
insufficient HFC allocation because they are transitioning to a lower-
GWP alternative.
In addition, growth calculated on a mass basis is more reflective
of demand than MTEVe and is not impacted by any potential swings
resulting from purchasing differing levels of HFCs with different EV
values each year. For example, a company purchasing 20 kg of HFC-41 in
one year and 40 kg of HFC-23, which has an EV approximately 160 times
that of HFC-41, the following year would have the same growth rate as a
company purchasing 20 kg of HFC-41 in one year and 40 kg of HFC-41 the
next year (i.e., the growth rate for that year is 100 percent for both
companies versus 32,000 percent for the first company and 100 percent
for the second company).
E. Inventory
EPA's current regulations require entities receiving ASAs to
provide, as part of their biannual reporting requirements, information
on the quantities of HFCs left in their inventory at the end of the
previous six-month reporting period (40 CFR 84.31(h)(1)(iv)). Upon
finalization of this rulemaking and heading into the allocation of
calendar year 2026 allowances, EPA will have several years of data on
inventory, including how inventory levels have changed over time. In
the Allocation Framework Rule, EPA noted its intent to account for
changes in inventory in the allocation of ASAs (86 FR 55116, 55152,
October 5, 2021).
EPA is proposing to include verified changes in inventory into the
calculation of the quantity of HFCs an entity used over the 12-month
period for all allocations except MCMEU. Changes in inventory are
documented information as to how an entity used HFCs in a particular
year. For example, if an entity purchased 100 kg of HFCs,
[[Page 75929]]
and their inventory grew by 50 kg, this would suggest that the entity
used 50 kg in the manufacturing process under the applicable
application. In this instance, consideration of purchases minus
inventory buildup is a more accurate reflection of HFC use by the
entity than HFC purchases would be alone. EPA proposes to factor in
both drawdown and growth in inventory; a drawdown of inventory would be
added to HFC purchases and a buildup of inventory would be subtracted
from HFC purchases.
EPA is proposing that this approach would not apply to calculation
of MCMEU allowance allocations because DOD has a history of building up
inventory and may need to do so for mission-critical or national
security purposes. The Agency acknowledges that building inventories
can be an important strategy for other entities to navigate changing
market conditions, especially in advance of the 2029 reduction step.
Therefore, as part of this proposal, EPA is also including that
entities may provide a rationale as to why a buildup in inventory
should not be subtracted from the quantities of HFCs they annually
acquire. An example of what the Agency would consider to be acceptable
rationale would be if a producer announced that they would be ceasing
production of an HFC that is used in a particular application, and the
entity wanted to build up inventory of that HFC to continue
manufacturing of their product while they figured out their transition
timeline. Another example could include a situation where an entity had
to purchase a minimum volume (e.g., a full ISO tank) and that last
purchase resulted in an increase in inventory.
In the alternative, EPA is proposing to not incorporate small
amounts of growth in inventory in allocation decisions. EPA would
propose to define a small amount of growth as below 20 percent or,
alternatively, growth in inventory for only a single year. EPA invites
comment on this alternative pathway and also what the Agency should
consider to be a small amount of inventory growth.
F. Department of Defense Conferrals
In the Allocation Framework Rule, EPA finalized that anyone
conferring an ASA, except for the conferral of allowances for MCMEU,
would be required to submit information about each conferral prior to
conferring allowances (40 CFR 84.31(h)(4)). While DOD was not required
to submit conferral information to EPA, DOD was required to maintain
records documenting the conferral(s) of ASAs to other entities up to
and including the producer or importer of the chemical (40 CFR
84.31(h)(7)(iv)).
In order to ensure that certain imports are not delayed or denied,
EPA is proposing to modify the 40 CFR part 84, subpart A regulations to
require that DOD report information consistent with the required
reporting of conferral data from all other ASA holders. This would
include the identity of each conferrer and conferee and the quantity in
MTEVe of ASAs being conferred. This proposed regulatory change would
not be a significant burden for DOD because DOD is already required to
track this data internally (40 CFR 84.31(h)(7)).
If finalized, this regulatory revision would bring the process for
conferring MCMEU allowances in line with other entities receiving ASAs.
The Allocation Framework Rule noted that one of the goals of this
requirement was ``to ensure EPA has the requisite information to track
application-specific allowances'' (86 FR 55116, 55189, October 5,
2021). When an HFC supplier reports to EPA that they have expended ASAs
other than MCMEU allowances, conferral reports have allowed EPA to
confirm whether that supplier was in possession of ASAs. With MCMEU
allowances, given that DOD is not required to share information about
the conferral of MCMEU allowances with EPA, the Agency has encountered
difficulty verifying whether suppliers are in possession of MCMEU
allowances. EPA is particularly concerned that without conferral
information for MCMEU allowances, the Agency would recommend that U.S.
Customs and Border Protection (CBP) deny entry of an import of HFCs
bound for MCMEU. This could cause unnecessary delays for DOD and extra
costs for importers. Different reporting requirements for MCMEU
allowances has resulted in unexpected confusion and delays in the
approval of some producer and/or importer quarterly reports, increasing
administrative burden for DOD, entities who are producing and importing
on behalf of DOD, and EPA. If finalized, this regulatory change would
help address these issues.
In addition to bringing the process for conferring MCMEU allowances
in line with other entities receiving ASAs, EPA is proposing one
additional requirement for the conferral of MCMEU allowances, per a
request from DOD. To enable clearer tracking of MCMEU allowances from
initial conferral to expenditure, EPA is proposing to require that a
certificate number, generated by DOD, be reported to EPA for each
conferral and expenditure of MCMEU allowances. For example, if an
intermediary receives a conferral of MCMEU allowances from DOD and then
confers the allowances further to a supplier, both DOD and the
intermediary must report the same certificate number as part of the
conferral. Finally, when the supplier expends the conferred MCMEU
allowances for production or import of HFCs, the supplier must report
the certificate number in the same report in which the expenditure of
MCMEU allowances is reported. This additional layer of tracking
conferrals could further relieve any unexpected confusion.
G. Limited Set-Aside for Unique Circumstances Related to MDIs
Some stakeholders have expressed concern that an annual allocation
decision is not always sufficient to meet the needs of the entities
eligible for ASAs. Entities have noted that unanticipated events may
arise after July 31, when requests for ASAs are due, that legitimately
necessitate an increased need to purchase more HFCs than expected. EPA
received a comment to the Allocation Framework Rule (86 FR 55116,
October 5, 2021) requesting that EPA create a separate additional pool
of allowances to accommodate growth, new mid-year entrants, and
``under-allocation.'' At the time of that rulemaking, EPA determined
that establishing such a pool of allowances was unnecessary because the
Agency had set up an allocation formula to allocate the full quantity
of allowances necessary, and setting allowances aside just in case they
were needed would reduce the allowances available to general pool
allowance holders thereby reducing how many HFCs can be imported or
produced if the set-aside allowances went unexpended. EPA also noted
that a company can access HFCs from the open market; if a company used
more HFCs in a given year, that increased use would be reflected in the
next year's allocation. However, EPA also noted that the Agency would
learn from implementation of the program and consider adjusting the
methodology (86 FR 55116, 55151, October 5, 2021).
Based on the Agency's observations in implementing the ASA
allocations over the past three years, EPA is proposing to create a
set-aside of allowances specifically for situations that meet the
criteria for the unique circumstance established in 40 CFR
84.13(b)(1)(iii), including the proposed changes described in Section
VII.B of this preamble. In other words, this would be a set aside to
accommodate unforeseen need for regulated substances related to a
global pandemic, other public health emergency, or other healthcare
system needs related to increased patients
[[Page 75930]]
diagnosed with medical conditions treated by MDIs. EPA still sees
significant downsides to creating a set-aside of allowances for
unforeseen demands in the eligible applications as outlined in the
Allocation Framework Rule, but does see benefit in creating a set-aside
for the singular narrow possibility of a public health emergency or
other unforeseen event that would specifically affect availability of
MDIs. As a result, EPA is proposing to set aside allowances that would
be available for the use of HFCs as a propellant in MDIs if the
requester meets the criteria for the unique circumstance as defined in
in 40 CFR 84.13(b)(1)(iii). Application-specific entities could apply
to EPA for these allowances based on a demonstrated need to purchase
more HFCs in the present calendar year in light of events that were
unforeseen at the time of the entity's application for ASAs for the
calendar year at issue. For example, during the beginnings of the
COVID-19 pandemic in 2020, MDI manufacturers purchased nearly 40% more
HFC-134a than they did in 2019, which is substantially more than they
would have been allocated based on Year 3 purchases and the
application's AAGR; this extra demand also could not have been
predicted in July 2019, when manufacturers would have applied for
calendar year 2020 allowances. EPA would consult with the FDA in
determining whether the presented situation meets the criteria as
defined, but scenarios could include a global pandemic. Other examples
of situations that could qualify are described in Section VII.B. EPA is
also taking comment on whether there are other analogous situations
where an unexpected increased need for HFCs resulting from the other
established and proposed unique circumstances could arise in which the
facts would justify the potential use of another set-aside for ASA
holders. If a commenter identifies such a situation, EPA requests that
the commenter also provide information on how EPA would appropriately
cabin requests to demand that was truly unexpected and unforeseeable
and also information on what entities should have to provide as
evidence when applying for set-aside ASAs. At a minimum, it seems
appropriate to require a requesting entity to present EPA with
information on how facts have changed that were unknowable at the time
the entity applied for that year's ASAs and also evidence that the
entity has been unable to acquire needed HFCs from the open market or
through allowance transfer. EPA seeks comment on the appropriate
records that would need to be provided to EPA to document the entity's
unsuccessful efforts to acquire HFCs without additional allowances from
EPA. EPA would likely require at least some of the records described in
Section VI of this preamble.
EPA is presenting a series of options for comment on how such a
set-aside pool would be created. Under Option 1, which is EPA's
preferred option, EPA would form this pool by setting aside 10 percent
of the allocation of certain entities--those that produced or imported
HFCs during 2011-2019 to serve the applications eligible for ASAs,
except MCMEU. An entity that produced or imported HFCs in the time
range of 2011-2019 for a separate entity now receiving ASAs is getting
a current HFC allowance allocation based on those past purchases. At
the same time, ASAs are being issued to entities for conferral to a
producer or importer. This can be viewed as a double allocation. For
example, if Entity A imported for an MDI manufacturer in 2011-2019,
those historic imports are included in calculating Entity A's allowance
allocation. In other words, Entity A is getting a higher allowance
allocation because of their imports for an MDI manufacturer. At the
same time, the MDI manufacturer is being allocated ASAs, which can be
conferred to Entity A to import HFCs for the MDI manufacturer.
Therefore, Entity A has two sets of allowances available to them as a
result of being an importer for MDI manufacturers. Because of this
aspect of the design of EPA's allocation system, if EPA were to create
a set-aside of allowances for application-specific entities, EPA
proposes to hold back 10 percent of the allocation of entities that
produced and imported for application-specific uses during 2011-2019.
This appears more equitable than holding back a set amount of
allowances from all general pool allowance holders, since only those
that historically imported and produced for application-specific uses
may have two sets of allowances now available to them. Of course,
because a company that historically produced or imported for
application-specific uses has two sets of allowances available to them,
it seems that they should have sufficient production and/or consumption
allowances available to purchase additional HFCs for an application-
specific entity if an unexpected need arises. EPA is soliciting comment
on whether, because of this fact, a set-aside is not truly needed, or
if a set-aside is necessary because historic importers and producers
are requiring conferral of ASAs to meet the needs of application-
specific entities.
Under this proposed Option 1 approach, EPA would withhold 10
percent of the identified entities' allowances until April 30. If no
application-specific entity applied for the allowances by April 30,
then the withheld allowances would be issued to the entities from which
they were withheld. If a request is pending, EPA would withhold
allowances until that request was evaluated and allowances were issued.
Such issuance would be done in a proportionate fashion if some, but not
all, of the set-aside allowances were allocated to application-specific
entities. EPA seeks comment on whether April 30 is late enough in the
year to provide the appropriate safety value for unforeseen public
health emergencies and other healthcare system needs.
Alternatively, Option 2 would be that EPA would create a set-aside
pool for application-specific entities in the event of a public health
emergency or other healthcare system need from any revoked allowances,
including from administrative consequences already finalized. In the
Allocation Framework Rule, EPA created administrative consequences
whereby EPA can adjust allowance allocations if EPA determines that a
person failed to comply with certain requirements relating to the HFC
allowance allocation and trading program. Under the administrative
consequence tool, a revoked allowance is one that EPA takes back from
an allowance holder and redistributes to all other allowance holders
(86 FR 55116, 55169, October 5, 2021). Under this second option,
instead of redistributing revoked allowances to all other allowance
holders, EPA would put the revoked allowances into a set-aside pool in
case additional ASAs were needed as a result of a public health
emergency. One potential flaw with this proposed approach is that to
date, entities could expend ASAs to either produce or import HFCs. EPA
created ASAs to function this way because end users in the identified
applications may not know in advance how they will procure HFCs, and
this method provides flexibility to ensure that end users receive the
``full quantity of allowances necessary,'' (86 FR 55148). To ensure
that these ASAs are provided within the overall annual production and
consumption caps, EPA subtracts the amount of ASAs allocated from both
the production and consumption general allowance pools (40 CFR
84.9(a)(3); 84.11(a)(3)). However, to date, EPA has only revoked
consumption
[[Page 75931]]
allowances.\31\ EPA would likely need to hold back some amount of
production allowances under this option, up to 1,000,000 MTEVe, to
ensure sufficient allowances were available.
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\31\ See https://www.epa.gov/climate-hfcs-reduction/administrative-consequences-under-hfc-allocation-rule.
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A third, less preferred option, would be to hold back a set amount
of allowances. This set-aside would be created from all general pool
allowance holders. EPA proposes that the Agency could hold back
allowances in the range of 500,000 to 1,000,000 MTEVe production and
consumption allowances. If no application-specific entity applied for
the allowances by April 30, then the withheld allowances would be
issued to the entities from which they were withheld. If a request is
pending, EPA would withhold allowances until that request was evaluated
and allowances were issued. As explained previously, this approach
seems less equitable than Option 1. This approach also does not allay
the concerns identified by EPA in the Allocation Framework Rule for
establishing a set-aside for ASAs. However, EPA is interested in
stakeholder input regarding this option.
Finally, as an alternative to creating a set-aside at all, EPA is
taking comment on the possibility of allowing conferral of ASAs from
other applications in the event an unforeseen event that meets the
unique circumstance outlined in 40 CFR 84.13(b)(1)(iii). Under EPA's
current regulations, conferred ASAs may only be used to produce or
import HFCs for the application-specific use associated with the
allowance(s) (40 CFR 84.13(h)). Under this alternative, EPA would amend
the regulations such that if an unforeseen event meeting 40 CFR
84.13(b)(1)(iii), ASAs could be conferred and expended to produce or
import HFCs for application-specific use different from the application
associated with the allowance. For example, if EPA agreed that there
was a public health emergency that created an unexpected need to
purchase more HFCs for MDI manufacturing, under this approach ASAs
allocated for aerospace fire suppression could be conferred to import
or produce HFCs for use in MDI manufacturing.
EPA seeks comment on these proposals, in particular on the scope of
the need, the number of allowances that are expected to need to be set
aside, the date by which requests must be received to be considered,
and all other aspects of the proposal.
H. Return of Unneeded Allowances
EPA is aware that some application-specific entities are allocated
more allowances than are necessary to accommodate their needs for a
given calendar year. This may be because for that specific year, the
regulatory formula overestimated that individual entity's need. It is
also possible that the entity's expectations for the year did not match
reality because of unexpected intervening events, such as a drop in
demand for the entity's products or supply chain difficulties. In light
of these considerations, EPA is proposing to allow ASA holders to
return their allowances voluntarily if they do not intend to use them.
ASA holders could return allowances up to and including June 30 of the
year for which the allowances can be expended (e.g., calendar year 2025
allowances would have to be returned by June 30, 2025). This would be
completely optional and intended to be used at the discretion of the
ASA holder. EPA proposes to use any returned allowances to either: (1)
fulfill unexpected higher demand of another ASA holder (see proposal in
Section VII.G of this preamble); or (2) return the allowances to the
general pool of allowance holders proportionate to respective market
shares. EPA sees benefit of redeploying allowances that would go unused
into the overall HFC market for smoother transition and to ease the
overall HFC phasedown.
EPA is soliciting comment on this proposal, including whether it is
needed if EPA finalizes other proposals outlined in this notice. EPA is
particularly interested in whether this proposed approach is needed if
EPA finalizes the requirement for entities to include in their
application for allowances their anticipated need for the following
calendar year. EPA is also interested in stakeholder input on whether
codifying an ability for entities to return unneeded allowances would
have unintended negative effects, including limiting the availability
of allowances for transfer to another application-specific entity that
has an unanticipated need for more allowances during the calendar year.
I. Enabling Auctions of Illegally Imported HFCs
In addition to the proposed changes to EPA's application-specific
regulations outlined in this section, EPA is also proposing a targeted
change to the regulations related to the enforcement and compliance
provisions EPA finalized in the Allocation Framework Rule. As explained
in the Allocation Framework Rule, EPA established a comprehensive
system of mechanisms that together and by themselves discourage and
prevent illegal production, import, and subsequent sales of illegally
produced or imported HFCs. Since the requirement came into effect that
entities must expend allowances to produce or import HFCs, EPA has been
working with partner agencies across the Federal government to
implement a comprehensive enforcement and compliance program.
One issue that EPA has been grappling with is what to do with HFCs
that an entity imports or attempts to import without expending the
requisite number of allowances. Among other things, the Federal
government has been considering reexport, destruction, and auctions as
potential available pathways for such HFCs. EPA is in the process of
working with partner Federal agencies, particularly CBP, to consider
the feasibility of an auction of HFCs that have been stopped or seized
by CBP as was done in the past with illegally imported ODS. As part of
this process, EPA has identified a provision in the existing 40 CFR
part 84 regulations that could be read to inhibit some auctions of
HFCs, although there is nothing in 40 CFR part 84 that prohibits
auctions. In order to ensure auctions are an option, if the Federal
government otherwise chooses to pursue them, EPA in this rulemaking is
proposing to amend the prohibition relating to the sale and prohibition
of illegally imported HFCs in 40 CFR 84.5 to clarify that a person may
sell or distribute, or offer for sale or distribution, a regulated
substance purchased at an auction authorized by CBP if the buyer
expended consumption allowances or ASAs in a quantity equal to the EV-
weighted equivalent of the illegally imported regulated substances.
This proposed change would provide explicit clarity to an entity that
purchases HFCs at such an auction that the HFCs they purchase can be
sold as if they were initially imported with allowances.\32\
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\32\ The sales provision in 40 CFR 84.5 does not apply to other
government personnel or contractors that need to move the HFCs for
eventual disposition consistent with the regulatory requirements,
such as through an auction with verification by EPA prior to sale.
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EPA is also proposing targeted changes to the reporting
requirements to provide clarity in the regulations for how such
purchases would be reported. EPA proposes that entities purchasing HFCs
at auction would need to report the import of those HFCs (that was done
by another entity prior to the auction purchase) under 40 CFR
84.31(c)(1) and maintain records consistent with 40 CFR 84.31(c)(2).
EPA proposes that entities would use the date that entry
[[Page 75932]]
was filed for the HFCs purchased at auction for purposes of 40 CFR
84.31(c)(1) reporting and maintain records of that purchase under 40
CFR 84.31(c)(2). This would provide a date that can be easily verified
and would align with when the entity formally expressed intent to CBP
to enter the HFCs into U.S. commerce.
Additionally, EPA is proposing that entities who purchase HFCs at
auction would not be subject to the advance notification requirement in
40 CFR 84.31(c)(7) for HFCs purchased via an auction authorized by CBP,
as the window for the notification would have already passed and EPA
would be verifying whether a prospective purchaser has sufficient
allowances as part of any auction. However, EPA proposes that entities
would still have to provide notification to EPA via a CBP-authorized
electronic data interchange system, such as the Automated Broker
Interface, prior to the HFCs entering U.S. commerce and provide the
same data elements as in 40 CFR 84.31(c)(7). If a certificate of
analysis (see 40 CFR 84.31(c)(7)(xvi)) is not available at the time of
filing entry, EPA is proposing that the entity would need to do any
required sampling and testing prior to sale in U.S. commerce.
J. Quarterly Exporter Reporting of Internal Transaction Numbers
ITNs uniquely identify shipments being exported from the U.S. to
another country. EPA currently requires companies to report ITNs when
they request additional consumption allowances after exporting bulk
HFCs. EPA is proposing to require companies to additionally report ITNs
quarterly for all HFC exports. It is EPA's understanding that reporters
can obtain ITNs from either CBP or their broker with relative ease,
once they have a process to do so in place. Many reporters already
gather ITNs on a regular basis for the purpose of submitting RACA
reports.
Under CBP regulations, there are some instances in which exporters
may acquire ITNs but are not required to do so. These instances may
include exports to Canada and lower-value exports, for example. EPA
proposes that exporters would not be required to report ITNs for
shipments that are exempt from needing ITNs under CBP regulations. EPA
is not proposing any changes to the existing regulations related to
RACAs, so reporters would still need to obtain ITNs for any exports
listed in RACA submissions (e.g., exports to Canada).
EPA is proposing to require exporters to report ITNs quarterly to
better enable EPA to perform quality assurance and integrity checks
between exports reported to the Agency under the reporting requirements
in 40 CFR 84.31 with Customs records. This, in turn, will enable EPA to
better ensure the accuracy of the overall volume of HFCs that are
exported, which is a critical component of the overall calculation of
the HFC phasedown, in addition to being communicated for transparency
to stakeholders and being a key part of the Agency's international
reporting obligations under the Montreal Protocol.
K. Date of Purchase for Requests for Additional Consumption Allowances
(RACAs)
EPA is proposing to change the existing requirement in 40 CFR
84.17(a)(5) to report the date HFCs were purchased as part of a RACA.
Instead, EPA would require an entity to only report whether the HFCs
exported were purchased before January 1, 2022, or after that date. EPA
has received feedback from entities requesting RACAs that it is
difficult to report the date HFCs were purchased because the
information can be difficult to obtain. For example, a company may
purchase several batches of HFCs over the course of several months and
combine these batches into a homogenous mixture in an on-site holding
tank. These batches of HFCs could come from multiple suppliers. The
contents of the holding tank are then siphoned off into smaller
containers and exported to a foreign country, at which point the
company seeks a RACA for those exported HFCs. In this scenario, it is
difficult to determine what the ``date of purchase'' was for any given
container of HFCs that was exported.
When EPA initially codified the requirement to provide the date
purchased as part of a RACA, the primary purpose of this data element
was to track how much material is being exported out of pre-2022
inventory, before the phasedown program was in effect. This, in turn,
helps the Agency understand certain market trends (e.g., how many
containers are being sold out of older inventory as opposed to more
recently purchased inventory). However, EPA can track this trend with a
simpler data element. Accordingly, EPA proposes to change the existing
requirement to provide the date HFCs were purchased to whether the HFCs
were purchased before or after January 1, 2022.
VIII. Authorization To Produce for Export
In previous rulemakings, i.e., the Allocation Framework Rule and
the 2024 Allocation Rule, some commenters expressed concern that under
EPA's methodology for issuing production and consumption allowances,
certain producers were not allocated sufficient allowances to meet the
demands of their international customers working in applications for
which ASAs were allocated to the domestic manufacturers. Commenters
said that foreign semiconductor manufacturing remains important even
while domestic semiconductor manufacturing increases under the CHIPS
Act.
This issue was generally beyond the scope of prior rulemakings, but
EPA recognizes that under the methodology for issuing general pool
production and consumption HFC allowances \33\ in tandem with how ASAs
have historically been issued, domestic HFC producers that manufacture
low EV HFCs with proportionally smaller market shares may face
challenges due to a combination of the phasedown itself, EPA's
allocation methodology, and that EPA does not allocate ASAs for
entities' operations outside the United States.
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\33\ EPA is not reopening nor proposing to revisit the
methodology for issuing general pool production and consumption HFC
allowances in this rulemaking.
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Subsection (e)(5) of the AIM Act provides that the Administrator
may authorize an entity to produce a regulated substance in excess of
the number of production allowances otherwise allocated to that entity,
subject to several conditions including:
The authorization is valid for a renewable period of not
more than five years;
Authorization must be established via notice and
opportunity for public comment; and
The production is solely for export to, and use in, a
foreign country that is not subject to the prohibition in subsection
(j)(1); \34\ and
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\34\ Given that the prohibition of (j)(1) does not take effect
until 2033, and EPA is proposing to make allowances available to
Iofina through 2030, EPA does not consider this restriction related
to subsection (j)(1) as relevant to this rulemaking.
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The production so authorized would not violate the
production or consumption limits.
EPA has received a request from Iofina Chemical (Iofina) to
authorize additional production of HFCs under subsection (e)(5) that
can be exported to supply semiconductor manufacturers outside of the
United States. Iofina has informed EPA that it has experienced
challenges acquiring HFC allowances via a transfer from another
allowance holder so it can produce low-EV, HFC-41, to sell to
semiconductors manufacturers abroad. Iofina has flagged
[[Page 75933]]
this challenge for EPA for several years. The company has also noted
that even if it were able to secure a transfer for a single year,
Iofina could not plan over multiple years.
EPA has considered Iofina's specific situation, the limited number
of allowances that would be needed to accommodate its request, and its
stated intent to export HFCs for use in an application that Congress
specified in subsection (e)(4)(B) of the AIM Act, and is proposing to
authorize Iofina to undertake additional production for export as
contemplated by AIM Act subsection (e)(5). To operationalize this
subsection of the AIM Act, EPA is proposing to establish a production
for export category of allowances and associated recordkeeping and
reporting requirements. EPA is proposing that this new category of
allowances would be nontransferable. Consistent with language in
subsection (e)(5) of the AIM Act that EPA may ``authorize an entity''
(emphasis added), the Agency is proposing that these production for
export allowances would be available only to Iofina to supply regulated
HFCs to application-specific end users located abroad, specifically and
only for the etching of semiconductor material or wafers and cleaning
of CVD chambers within the semiconductor manufacturing sector. EPA is
proposing to issue 3,000.0 MTEVe of allowances annually to Iofina for
the stated purpose for each of the calendar years 2026 through 2030.
EPA proposes to determine that authorization of production for
export to Iofina in this instance is appropriate and consistent with
subsection (e)(5) of the AIM Act. EPA proposes that this is
particularly true where the ASA requirements of subsection
(e)(4)(B)(iv) provide priority access to HFCs for defined applications.
This proposal is intended to address a need that has been voiced
consistently and exclusively by Iofina, for which Iofina has provided
supporting information to substantiate the request.
EPA is proposing to allocate 3,000.0 MTEVe non-transferrable
production for export allowances exclusively to Iofina on an annual
basis for each of the calendar years 2026 through 2030. A detailed
discussion of the rationale for the Agency's proposal follows.
A. To what entities is EPA proposing to allocate production for export
allowances?
As described above, EPA is proposing to only allocate production
for export allowances to Iofina. The Agency has determined that the
company has demonstrated their need for production for export
allowances. Iofina has made good faith efforts to acquire allowances
via an inter-company transfer and has had difficulty finding another
allowance holder willing to transfer production and consumption
allowances to them in order to produce regulated HFCs for export.
Iofina has documented foreign customer demand in an application-
specific end use for the HFC they produce. Iofina has committed to
conduct extensive due diligence to verify and ensure that the HFCs they
sell abroad are only sold to an entity that will use the HFC for the
etching of semiconductor material or wafers and cleaning of CVD
chambers within the semiconductor manufacturing sector and are not
going to be diverted for some other use (e.g., destroyed for carbon
credits, sold to another entity that will use the HFCs for another end
use).
EPA has also considered how this authorization supports the HFC
phasedown overall. Iofina produces only one HFC, HFC-41, one of the
lowest EV HFCs controlled by the AIM Act with an EV of 92, at its
facility in Covington, Kentucky. Iofina produced HFCs during the 2011-
2019 timeline and in subsequent years, and accordingly have been
allocated allowances for calendar years 2022, 2023, and 2024. Because
Iofina has always produced a low EV HFC, their allocation is smaller
than companies that have historically produced higher EV HFCs, which
now have flexibility to transition into a lower EV HFC at higher
volumes. HFC-41 comprises a small portion of overall U.S. HFC
calculated production \35\ (0.02 percent in 2022 on a mass basis and
approximately 0.001 percent on an EVe basis), and Iofina is the only
U.S. producer of HFC-41 for consumptive use. Further, HFC-41 has a
lower EV than all other regulated substances used in the etching of
semiconductor material or wafers and the cleaning of CVD chambers
within the semiconductor manufacturing sector. Coupled with the
extremely small volume of allowances that this production would
require, EPA sees authorizing this additional flexibility as
appropriate to support continued U.S. production of HFC-41.
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\35\ See EPA HFC Data Hub at https://www.epa.gov/climate-hfcs-reduction/hfc-data-hub.
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EPA recognizes that upon reviewing this proposed rulemaking, there
may be other HFC producers who would be interested in receiving
production for export allowances for application-specific uses abroad.
At this time, EPA has only assessed the appropriateness of proposing an
allocation for Iofina in light of the specific circumstances presented
by that entity. The Agency is not proposing, nor creating a mechanism
to finalize, production for export allowances for any other entity
through this rulemaking. If other producers were to express a similar
interest, EPA would consider whether to act in a separate rulemaking
under subsection (e)(5), but we emphasize that this action is dependent
on facts specific to Iofina, including the relatively small size of
Iofina's production and the modest impacts on the overall market for
HFCs that will result.
B. How many production for export allowances is EPA proposing to issue
to Iofina on an annual basis, and for how many years is EPA proposing
to issue these allowances?
EPA is proposing to issue Iofina non-transferrable production for
export allowances in the amount of 3,000.0 MTEVe on an annual basis.
The Agency arrived at this proposed amount based on an evaluation of a
combination of factors including: Iofina's request; supporting
information from the company explaining and demonstrating the need for
production for export allowances; Iofina's relative market share of
production allowances and recent yearly allocations from EPA; recent
conferral activity where Iofina is the recipient; and, the general
effect to other producers of issuing Iofina production for export
allowances in the proposed amount.
The production cap for calendar year 2024 through 2028 (the current
phasedown step) is 229,521,263 MTEVe and the production cap for
calendar year 2029 through 2033 (the next phasedown step) is
114,760,632 MTEVe. The proposed number of production for export
allowances the Agency would issue Iofina would be approximately 0.001
percent of the overall production cap for 2026 through 2028 and 0.003
percent for 2029 and 2030.\36\ Accordingly, the Agency does not
envision any shortage of production allowances for these years as a
result of the proposal to issue Iofina 3,000.0 MTEVe of production for
export allowances. In essence, the proposed 3,000.0 MTEVe of production
for export allowances issued to Iofina would not materially affect any
other domestic producer even in light of the next phasedown step.
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\36\ Percent = (Number of Production of Allowances Issued)/
(Production Cap)*100.
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Consistent with the provisions in subsection (e)(5)(A)(i), EPA is
proposing that if finalized, Iofina would be issued
[[Page 75934]]
production for export allowances on an annual basis for a five-year
period between 2026 through 2030.
C. Would Iofina need to expend consumption allowances for materials
produced with production for export allowances and subsequently
exported?
Subsection (e)(5) of the AIM Act allows EPA to ``authorize a person
to produce'' for export if such production would not violate the yearly
cap described in subsection (e)(2)(B). To operationalize this statutory
requirement, EPA proposes to require that any material produced with
production for export allowances must be exported in the same year it
was produced. The AIM Act defines ``consumption'' as the amount of HFCs
produced and imported minus the quantity of HFCs exported. Therefore,
production of an HFC in a given year would be ``netted out'' when
calculating consumption if that HFC is exported in that same year.
Because HFCs produced with production for export allowances would be
exported in the same year and therefore would be ``netted out'' when
evaluating the United States' calculated yearly consumption, EPA is
proposing that when Iofina produces for export using this specific
category of allowances, it is not required to expend consumption
allowances in an equivalent amount. Relatedly, EPA is also proposing
that Iofina's materials produced with production for export allowances
are not eligible for additional consumption allowances through the RACA
provisions in 40 CFR 84.17.
D. How will this process affect the issuance of other types of
allowances?
Under 40 CFR part 84, subpart A, EPA first issues ASAs. Because the
Agency is proposing an annual finite number of production for export
allowances for Iofina, EPA proposes to issue these non-transferrable
allowances immediately after ASAs are issued. As a result, EPA is
proposing small modifications to 40 CFR 84.9 to reflect that the number
of available general pool production allowances is the difference
between the yearly production cap and the sum of ASAs issued and the
number of production for export allowances. It should be noted that
because production for export allowances is a separate category from
general pool production allowances, Iofina would be eligible for both
of these types of allowances beginning in 2026 through 2030 if the
production for export allowance provisions are finalized. EPA is not
proposing any changes to how general pool consumption allowances are
issued on an annual basis and is neither revising nor reopening the
methodology codified in 40 CFR 84.11.
E. What are the proposed recordkeeping and reporting requirements for
production for export allowances?
In order to maintain overall stringency while allowing for the
flexibilities in the AIM Act described in this general information
section of the preamble, EPA is proposing that Iofina comply with
recordkeeping and reporting requirements in addition to what is already
required of the entity as a domestic producer under 40 CFR 84.31(a) and
(b) and as an exporter under 40 CFR 84.31(d).
1. Annual Certifications
EPA is proposing that Iofina secure signed certifications by a
responsible corporate officer from their overseas application-specific
customers attesting that any regulated HFCs produced using production
for export allowances will only be used in application-specific uses
(i.e., only for the etching of semiconductor material or wafers and the
cleaning of CVD chambers within the semiconductor manufacturing
sector). EPA is proposing that Iofina must provide such written and
signed certification for each of their overseas customers, accompanied
by a description of how the foreign use aligns with the definitions in
40 CFR 84.13(a) and 40 CFR 84.3. If the regulated HFCs produced by
Iofina using product for export allowances are to be held at an
intermediary prior to receipt by the semiconductor manufacturer, the
intermediary must also submit the same certification. As part of the
yearly written certification, EPA is proposing that the name and
address of the foreign entity, and the contact person's name, email
address, and phone number are included. Further, EPA is proposing that
Iofina must provide copies of these signed certifications with its end
of year fourth quarter report due February 14 (i.e., certifications for
calendar year 1 are due on February 14 of year 2).
2. Quarterly Export and Inventory Reporting
In addition to submitting the quarterly exporter reports currently
required under 40 CFR 84.31(a) and (b), the Agency is proposing that
Iofina must, as part of these quarterly exporter reports, document the
amounts exported that were produced using production for export
allowances. Iofina would also be required to document the country to
which HFCs were exported. As part of this documentation and to help
ensure that EPA can quickly locate exports of regulated HFCs produced
by Iofina, the Agency is proposing that an ITN be provided for each
shipment regardless of monetary value, destination country, or other
characteristics that could otherwise exempt or preclude an exporting
entity from obtaining an ITN. Additionally, EPA is proposing that
Iofina report quarterly no later than 45 days after the applicable
quarterly control period on inventory of regulated HFCs produced with
production for export allowances so EPA can effectively track their
use. Inventory of regulated HFCs produced with production for export
allowances must be zero as of December 31 for that calendar year;
otherwise, EPA may pursue actions including but not limited to
allowance adjustments, i.e., administrative consequences, or
enforcement action. All reports described in this section would be
subject to EPA's auditing provisions under 40 CFR 84.33 if finalized as
proposed.
3. Recordkeeping
EPA is proposing that Iofina maintains for a period of five years
the certifications from all of its customers and any intermediaries
attesting that the regulated HFCs they are receiving are only to be
used for the etching of semiconductor material or wafers and cleaning
of CVD chambers within the semiconductor manufacturing sector. The
Agency is also proposing that Iofina maintain for a period of five
years records demonstrating that Iofina has conducted extensive due
diligence to verify and ensure that the HFCs they sell abroad are only
sold to an entity that will use the HFC for an application-specific use
and are not going to be diverted for some other use (e.g., destroyed
for carbon credits, sold to another entity that will use the HFCs for
another end use).
IX. How will EPA handle confidentiality for newly reported information?
Consistent with EPA's commitment to transparency in program
implementation, as well as to proactively encourage compliance, support
enforcement of program requirements, and enable third-party engagement
to complement EPA's enforcement efforts, EPA is proposing several ways
it intends to release data that would be collected if this proposed
rule is finalized as proposed.
EPA has reviewed the data elements that are proposed to be reported
under this rulemaking. Based on that review, EPA is proposing certain
confidentiality
[[Page 75935]]
determinations in advance through this notice and comment rulemaking
for individual reported data elements that EPA would be collecting
through this rulemaking. This proposal identifies certain information
that must be submitted to EPA that may be subject to disclosure to the
public without further notice because the Agency proposes to find that
the information does not meet the standard for confidential treatment
under Exemption 4 of the Freedom of Information Act (FOIA). EPA is also
proposing to identify certain other categories of information that
would be entitled to confidential treatment. For data elements for
which EPA is not making a confidentiality determination in this action,
EPA will apply the 40 CFR part 2 process for establishing case-by-case
confidentiality determinations. The confidentiality determinations in
this proposed action are intended to increase the efficiency with which
the Agency responds to FOIA requests and to provide consistency in the
treatment of the same or similar information. Establishing these
determinations through this rulemaking will provide predictability for
both information requesters and entities submitting information to EPA.
The confidentiality determinations are also proposed to increase
transparency around this program's implementation.
A. Background on Determinations of Whether Information Is Entitled to
Treatment as Confidential Information
Exemption 4 of the FOIA exempts from disclosure ``trade secrets and
commercial or financial information obtained from a person [that is]
privileged or confidential'' (5 U.S.C. 552(b)(4)). In order for
information to meet the requirements of Exemption 4, EPA must find that
the information is either: (1) a trade secret, or (2) commercial or
financial information that is: (a) obtained from a person, and (b)
privileged or confidential.
Generally, when we have information that we intend to disclose
publicly that is covered by a claim of confidentiality under FOIA
Exemption 4, EPA has a process to make case-by-case or class
determinations under 40 CFR part 2 to evaluate whether such information
qualifies for confidential treatment under the exemption. 40 CFR
2.205.\37\ In this action, EPA is proposing to make categorical
confidentiality determinations in advance through this notice and
comment rulemaking for some information that must be submitted to EPA
under the proposed requirements. If EPA finalizes these determinations,
that information could be disclosed to the public without further
notice.
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\37\ This approach of making categorical determinations for a
class of information is a well-established Agency practice. Prior
examples of rules where EPA has made such categorical determinations
include Confidentiality Determinations for Data Required Under the
Mandatory Greenhouse Gas Reporting Rule and Amendments to Special
Rules Governing Certain Information Obtained Under the Clean Air Act
(76 FR 30817) (May 26, 2011); Control of Air Pollution From New
Motor Vehicles: Heavy-Duty Engine and Vehicle Standards (88 FR 4296)
(January 24, 2023); and Renewable Fuel Standard (RFS) Program: RFS
Annual Rules (87 FR 39600) (July 1, 2002).
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The U.S. Supreme Court decision in Food Marketing Institute v.
Argus Leader Media, 139 S. Ct. 2356 (2019) (Argus Leader) addresses the
meaning of ``confidential'' within the context of FOIA Exemption 4. The
Court held that ``[a]t least where commercial or financial information
is both customarily and actually treated as private by its owner and
provided to the government under an assurance of privacy, the
information is `confidential' within the meaning of Exemption 4.''
Argus Leader, 139 S. Ct. at 2366. The Court identified two conditions
``that might be required for information communicated to another to be
considered confidential.'' Id. at 2363. Under the first condition,
``information communicated to another remains confidential whenever it
is customarily kept private, or at least closely held, by the person
imparting it.'' Id. (internal citations omitted). The second condition
provides that ``information might be considered confidential only if
the party receiving it provides some assurance that it will remain
secret.'' Id. (internal citations omitted). The Court found that the
first condition necessary for information to be considered confidential
within the meaning of Exemption 4, but did not address whether the
second condition must also be met.
Following the issuance of the Court's opinion in Argus Leader, the
U.S. Department of Justice (DOJ) issued guidance concerning the
confidentiality prong of Exemption 4, articulating ``the newly defined
contours of Exemption 4'' post-Argus Leader.\38\ Where the Government
provides an express or implied indication to the submitter prior to or
at the time the information is submitted to the Government that the
Government would publicly disclose the information, then the submitter
generally cannot reasonably expect confidentiality of the information
upon submission, and the information is not entitled to confidential
treatment under Exemption 4.\39\ In this proposed rule, EPA intends to
clearly assert that certain information would not be kept confidential
and may be disclosed publicly, if it is determined to not be entitled
to confidential treatment in the final version of this rulemaking. This
assertion aligns with the Supreme Court's decision, and the subsequent
DOJ guidance that the government's assurances that a submission will be
treated as not confidential should dictate the expectations of
submitters. If EPA were to finalize these determinations, submitters
would be on notice before they submit any information that EPA has
determined that the identified information outlined in the memorandum
provided in the docket for this action titled Proposed Confidentiality
Determinations for Data Elements in the Proposed Rule, will not be
entitled to confidential treatment upon submission and may be released
by the Agency without further notice. As a result, submitters will not
have a reasonable expectation that the information will be treated as
confidential; rather, they should have the expectation that the
information will be disclosed.
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\38\ ``Exemption 4 After the Supreme Court's Ruling in Food
Marketing Institute v. Argus Leader Media and Accompanying Step-by-
Step Guide,'' Office of Information Policy, U.S. DOJ, (October 4,
2019), available at https://www.justice.gov/oip/exemption-4-after-supreme-courts-ruling-food-marketing-institute-v-argus-leader-media.
\39\ See id.; see also ``Step-by-Step Guide for Determining if
Commercial or Financial Information Obtained from a Person is
Confidential under Exemption 4 of the FOIA,'' Office of Information
Policy, U.S. DOJ, (updated October 7, 2019), available at https://www.justice.gov/oip/step-step-guide-determining-if-commercial-or-financial-information-obtained-person-confidential.
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As described further below, EPA is proposing to make categorical
confidentiality determinations as some of the proposed data elements
that would be submitted to EPA contain information that is not entitled
to confidential treatment. For data elements not explicitly listed in
the document in the docket, EPA will apply the 40 CFR part 2 process
for establishing case-by-case confidentiality determinations.
There may be additional reasons not to release information
determined to not be entitled to confidential treatment, for example if
it is personally identifiable information (PII). The Agency will
separately determine whether any data should be withheld from release
for reasons other than business confidentiality before data is
released. EPA requests comment on the proposed confidentiality
determinations.
[[Page 75936]]
B. Data Elements Associated With a Petition To Be Listed as an
Application That Will Receive Application-Specific Allowances
In light of the statutory requirement in subsection (e)(4)(B)(ii)
to make a complete petition available to the public, and consistent
with EPA's commitment to transparency in program implementation, EPA
has reviewed the data elements EPA has proposed would be required for a
petition to be listed as an application that will receive ASAs.
Specifically, EPA proposes to not provide confidential treatment to,
and may release without further process, all required elements of the
petition, except for a subset of the elements for which EPA has
proposed that multiple entities could submit information individually
to EPA; \40\ and all information submitted to EPA that does not
correspond to a required element. The memorandum to the docket lists
each individual element of a complete petition, as proposed by EPA,
with an accompanying proposed determination on whether that element
would be entitled or not to confidential treatment. EPA is proposing
that through this rulemaking, entities are put on notice of data
release in line with the Argus Leader decision. EPA is providing an
express indication to all potential petitioners prior to the time
information is submitted to EPA that EPA will publicly disclose the
information without further process. Therefore, potential future
submitters cannot reasonably expect confidentiality of the information
upon submission, and the information is not entitled to confidential
treatment under Exemption 4. EPA invites comment on this proposed
determination.
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\40\ For example, EPA is proposing that (1) data on the
proportion of the overall cost of the product or system that
reflects the cost of regulated substance(s) and (2) historic and
projected sales for the product or system would not be treated as
confidential business information, as these are important elements
for the public to consider when EPA is taking action on a petition
for application-specific allowances.
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C. Data Elements Related to Proposed Revisions to Existing Regulations
To maximize program transparency, EPA is proposing to release
several data elements associated with the proposed limited changes to
existing regulations, including specific data elements associated with
the following proposed regulatory revisions: (1) a pool of set-aside
allowances for situations that meet the criteria for unique
circumstances related to the propellants in MDIs application; (2)
allowing ASA holders to return their allowances voluntarily if they do
not intend to use them; and (3) the ``date of purchase'' requirement
for a RACA. The memorandum to the docket lists each individual element
EPA has proposed related to these regulatory revisions with an
accompanying proposed determination on whether that element would be
entitled or not to confidential treatment. EPA is proposing that
through this rulemaking notice, entities are put on notice of data
release in line with the Argus Leader decision. EPA is providing an
express indication to all entities prior to the time information is
submitted to EPA that EPA will publicly disclose the information
without further process. Therefore, potential future submitters cannot
reasonably expect confidentiality of the information upon submission,
and the information is not entitled to confidential treatment under
Exemption 4. EPA invites comment on this proposed determination.
EPA is proposing to regulatorily determine that certain other
information would be entitled to confidential treatment. EPA is
proposing that supporting documentation verifying a need to purchase
regulated substances in the present calendar year for purposes of the
proposed set aside because it is likely to include the type of
information that submitters customarily keep private or closely held.
EPA is also proposing that data elements associated with the following
proposed regulatory revisions would be entitled to confidential
treatment: (1) requiring companies provide the total expected amount of
HFCs they intend to purchase in the calendar year; (2) new requirements
for the conferral of MCMEU allowances; and (3) requiring exporters to
report ITNs quarterly. These data elements constitute the type of
information that submitters customarily keep private or closely held.
Furthermore, in the case of ITNs reported by exporters, it is EPA's
understanding that the ITN, as part of the Electronic Export
Information (EEI) contained in the Automated Export System (AES), is
considered confidential by the Department of Commerce. Additional
information on the proposed determinations for specific data elements
associated with the proposed regulatory revisions is provided in the
memorandum in the docket for this action. EPA invites comments on these
proposed confidentiality determinations, including information on
whether the listed elements are the type of information customarily
kept private or closely held.
D. Data Elements Reported to EPA Related to Production for Export
EPA is proposing to establish a production for export category of
allowances as described in Section VIII. If EPA were to finalize the
proposal for production for export allowances, EPA is proposing to
release several data elements that a production for export allowance
holder would be required to submit, including: (1) quantity of
allowances expended for each regulated substance; (2) quantity of each
regulated substance produced for export; (3) quantity of each regulated
substance, produced using production for export allowances, that was
exported; (4) quantity of each regulated substance held in inventory at
the end of the quarter; and (5) the country to which regulated
substances, produced using production for export allowances, were
exported. The memorandum to the docket lists each individual element
EPA has proposed related to the production for export allowances with
an accompanying proposed determination on whether that element would be
entitled or not to confidential treatment. EPA is proposing that
through this rulemaking, entities are put on notice of data release in
line with the Argus Leader decision. EPA is providing an express
indication to all entities prior to the time information is submitted
to EPA that EPA will publicly disclose the information without further
process. Therefore, potential future submitters cannot reasonably
expect confidentiality of the information upon submission, and the
information is not entitled to confidential treatment under Exemption
4. EPA invites comment on this proposed determination.
EPA is proposing that the ITNs submitted for all exports of
regulated substances produced using production for export allowances
would be entitled to confidential treatment for the same rationale
described earlier in this section for the proposed requirement that
exporters report ITNs on a quarterly basis. EPA requests comment on
this proposed determination, including comments on why this information
may not be entitled to confidential treatment.
EPA is proposing that the signed certifications would be entitled
to confidential treatment because it is EPA's understanding that these
certifications could have the potential to reveal confidential business
relationships (i.e., the relationship between the allowance holder,
overseas customer, and any intermediaries). EPA requests comment on
this proposed determination, including comments on why this information
may not be
[[Page 75937]]
entitled to confidential treatment. Specifically, EPA requests comment
on whether the existence of a business relationship between an HFC
producer and customer is information that is customarily closely held.
X. What are the costs and benefits of this action?
The changes proposed in this proposed rule would not result in any
significant changes to the phasedown program as a whole, and thus do
not fundamentally change the assumptions made in the Allocation
Framework Rule RIA and subsequent RIA addenda. The Allocation Framework
Rule RIA estimated benefits and costs for the HFC phasedown between
2022 and 2050, including assuming for analytical purposes that the
allocation system would continue unchanged for years past the initial
period (i.e., for 2024 and beyond). This action would not change the
total number of allowances issued each year or the associated
environmental impacts. Further, the 2023 Technology Transitions Rule
RIA Addendum quantified the costs and benefits associated with the
transitions necessary for compliance based on the sector- and
subsector-specific restrictions finalized in that rule. Given that the
2023 Technology Transitions Rule promulgated restrictions for sectors
that encompass both defense sprays and SCPPU foams (aerosols and foam
blowing sectors, respectively), the compliance costs associated with
the proposals described in Section V of this proposed rule to restrict
the use of certain HFCs in defense sprays and SCPPU foams have already
been accounted for in the 2023 Technology Transitions Rule RIA
Addendum. Therefore, EPA is not developing an update to the RIA for
this proposed rule; however, given that some elements proposed in this
rulemaking could result in incremental impacts for a subset of
entities, the Agency did analyze potentially salient costs and benefits
considerations associated with this proposed rulemaking. A summary of
this analysis is included below, and additional details are presented
in Discussion of Costs and Benefits for Phasedown of
Hydrofluorocarbons: Review and Renewal of Eligibility for Application-
specific Allowances, which is available in the docket for this action
(EPA-HQ-OAR-2024-0196).
This analysis is intended to provide the public with information on
the relevant costs and benefits of this action and to comply with
Executive Orders. The analysis does not form a basis or rationale for
any of the actions EPA is proposing in this rulemaking.
For entities in applications for which EPA is co-proposing an
option to not renew eligibility for ASAs, the biggest drivers for any
costs would be no longer being exempted from the restrictions
promulgated under the Technology Transitions Program. However, entities
within those applications that currently receive ASAs would also avoid
recordkeeping and reporting costs associated with being an ASA holder
because they would no longer receive ASAs and thereby no longer need to
comply with related recordkeeping and reporting provisions, resulting
in burden relief.
General pool allowance holders may receive benefits in the form of
additional allowances if EPA finalized one or more applications no
longer being eligible for ASAs. However, EPA anticipates that the
number of additional allowances would be insignificant, totaling well
under one percent of consumption allowances in a given year. For
example, the number of allowances allocated in calendar year 2024 to
the two applications for which EPA is co-proposing an option to not
renew is equivalent to 0.1 percent of calendar year 2024 consumption
allowances. In addition, as these marginal benefits constitute a
transfer from one group to another and do not change the total number
of allowances issued, there is no net societal impact.
EPA estimates that there may be costs related to the proposed
requirements for ASA petitions and revisions to existing regulations.
For example, in a scenario in which EPA does not renew the defense
sprays and SCPPU foam for marine and trailer uses applications, the
estimated costs of this proposed rule would be $19,052 in one-time
costs and $54,310 in annual costs. More discussion of this scenario is
included in the costs and benefits memo available in the docket that is
referenced above. Other than these costs, EPA has not identified
additional costs or benefits beyond those estimated in the Allocation
Framework Rule RIA and subsequent RIA addenda.
XI. Statutory and Executive Order Review
A. Executive Order 12866: Regulatory Planning and Review and Executive
Order 14094: Modernizing Regulatory Review
This action is a ``significant regulatory action'' as defined in
Executive Order 12866, as amended by Executive Order 14094.
Accordingly, EPA submitted this action to the Office of Management and
Budget (OMB) for Executive Order 12866 review. Documentation of any
changes made in response to the Executive Order 12866 review is
available in the docket. EPA prepared an economic analysis of the
potential impacts associated with this action. This analysis,
``Discussion of Costs and Benefits for Phasedown of Hydrofluorocarbons:
Review and Renewal of Eligibility for Application-specific
Allowances,'' is available in the docket for this action (EPA-HQ-OAR-
2024-0196) and is briefly summarized in Section X of this preamble,
titled, ``What are the costs and benefits of this action?''. The high
end costs of this proposed rule are estimated in the table below:
Table 3--Summary of Costs in Scenario in Which Defense Sprays and SCPPU
Foam for Marine and Trailer Uses Applications Are Not Renewed
------------------------------------------------------------------------
Activity One-time costs Annual costs
------------------------------------------------------------------------
Application-specific allowance .............. $(189,728)
recordkeeping and reporting burden
relief for entities no longer eligible
for ASAs...............................
Technology Transitions recordkeeping and 19,052 221,462
reporting burden for entities no longer
eligible for ASAs......................
Petitions requesting eligibility for .............. 12,758
ASAs...................................
Other regulatory revisions.............. .............. 9,818
-------------------------------
Total............................... 19,052 54,310
------------------------------------------------------------------------
[[Page 75938]]
B. Paperwork Reduction Act (PRA)
The information collection activities in this proposed rule have
been submitted for approval to OMB under the PRA. The Information
Collection Request (ICR) document that the EPA prepared has been
assigned EPA ICR number 2685.05. You can find a copy of the ICR in the
docket for this proposed rule, and it is briefly summarized here.
Subsection (d)(1)(A) of the AIM Act specifies that on a periodic
basis, but not less than annually, each person that, within the
applicable reporting period, produces, imports, exports, destroys,
transforms, uses as a process agent, or reclaims a regulated substance
shall submit to EPA a report that describes, as applicable, the
quantity of the regulated substance that the person: produced,
imported, and exported; reclaimed; destroyed by a technology approved
by the Administrator; used and entirely consumed (except for trace
quantities) in the manufacture of another chemical; or, used as a
process agent. EPA collects such data regularly to support
implementation of the AIM Act's HFC phasedown provisions. EPA requires
quarterly reporting to ensure that annual production and consumption
limits are not exceeded. It is also needed for EPA to be able to review
allowance transfer requests, of which remaining allowances is a major
component of EPA's review. In addition, EPA collects information to
calculate allowances, to track the movement of HFCs through commerce,
and to require auditing. Collecting these data elements allows EPA to
confirm that the entity has not exceeded its allowed level of
production and consumption and that the aggregated annual quantity of
production and consumption in the United States does not exceed the cap
established in the AIM Act. As described above in this preamble, EPA is
proposing a procedural process for submitting a petition to designate a
new application as eligible for priority access to allowances;
reporting and recordkeeping requirements relevant for narrow revisions
to the methodology used to allocate allowances to ASA holders for
calendar years 2026 and beyond; and other limited reporting and
recordkeeping revisions, such as for the proposal to authorize an
entity to produce regulated substances for export.
All information sent by the submitter electronically is transmitted
securely to protect information that is CBI or claimed as CBI
consistent with the confidentiality determinations made in the
Allocation Framework Rule and the proposed confidentiality
determinations described in Section IX of this preamble, if finalized
as proposed. The reporting tool guides the user through the process of
submitting such data. Documents containing information claimed as CBI
must be submitted in an electronic format, in accordance with the
recordkeeping requirements.
Respondents/affected entities: Respondents and affected entities
will be individuals or entities that produce, import, export, reclaim,
recycle for use as a fire suppressant, distribute, destroy, transform,
use HFCs as a process agent, or produce for export, certain HFCs that
are defined as a regulated substance under the AIM Act. Respondents and
affected entities will also be any entity issued or conferred ASAs.
Respondent's obligation to respond: Mandatory (AIM Act).
Estimated number of respondents: 342.
Frequency of response: Quarterly, biannual, annual, and as needed
depending on the nature of the report.
Total estimated burden: 36,248 hours (per year). Burden is defined
at 5 CFR 1320.3(b).
Total estimated cost: $5,486,236 (per year), includes $1,038,450
annualized capital or operation & maintenance costs.
An agency may not conduct or sponsor, and a person is not required
to respond to, a collection of information unless it displays a
currently valid OMB control number. The OMB control numbers for the
EPA's regulations in 40 CFR are listed in 40 CFR part 9.
Submit your comments on the Agency's need for this information, the
accuracy of the provided burden estimates and any suggested methods for
minimizing respondent burden to the EPA using the docket identified at
the beginning of this proposed rule. The EPA will respond to any ICR-
related comments in the final rule. You may also send your ICR-related
comments to OMB's Office of Information and Regulatory Affairs using
the interface at www.reginfo.gov/public/do/PRAMain. Find this
particular information collection by selecting ``Currently under
Review--Open for Public Comments'' or by using the search function. OMB
must receive comments no later than October 16, 2024.
C. Regulatory Flexibility Act (RFA)
I certify that this action will not have a significant economic
impact on a substantial number of small entities (SISNOSE) under the
RFA. The small entities subject to the requirements of this action are
entities that hold HFC allowance allocations (including production,
consumption, and application-specific allowances), entities that
applied for but did not receive set-aside allowances in 2022, entities
that previously imported HFCs between 2017 and 2019 but did not receive
2022 allowance allocations, and entities that recover and reprocess
HFCs. Given there are co-proposals for two applications, EPA conducted
this preliminary screening analysis based on the pathway that could
lead to the highest cost burden on small entities; therefore, this
analysis assumes for analytical purposes that the defense sprays and
SCPPU foam for marine and trailer uses applications will not be
renewed. The Agency has determined that four of the 276 affected small
businesses--or 1.4 percent of all affected small businesses--could
incur costs in excess of one percent of annual sales, and three of
those four small businesses--or 1.1 percent of all affected small
businesses--could incur costs in excess of 3 percent of annual sales.
The four entities that could incur costs in excess of one percent of
annual sales are all entities that currently receive ASAs in the
defense sprays and SCPPU foam for marine and trailer uses applications.
These costs are primarily driven by these entities no longer being
exempted from Technology Transition Program restrictions. Further
details of this analysis are presented in Economic Impact Screening
Analysis for Phasedown of Hydrofluorocarbons: Review and Renewal of
Eligibility for Application-specific Allowances, which is available in
the docket for this action (EPA-HQ-OAR-2024-0196).
D. Unfunded Mandates Reform Act (UMRA)
This action does not contain any unfunded mandate of $100 million
(adjusted annually for inflation) or more (in 1995 dollars) as
described in UMRA, 2 U.S.C. 1531-1538, and does not significantly or
uniquely affect small governments. The action imposes no enforceable
duty on any State, local or Tribal governments and the costs involved
in this action are estimated not to exceed $183 million in 2023$ ($100
million in 1995$ adjusted for inflation using the GDP implicit price
deflator) or more in any one year.
E. Executive Order 13132: Federalism
This action does not have federalism implications. It will not have
substantial direct effects on the States, on the relationship between
the national government and the States, or on the distribution of power
and responsibilities among the various levels of government.
[[Page 75939]]
F. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
This action does not have Tribal implications as specified in
Executive Order 13175. EPA is not aware of Tribal businesses engaged in
activities that would be directly affected by this action. Based on the
Agency's assessments, EPA also does not believe that potential effects,
even if direct, would be substantial. Accordingly, this action will not
have substantial direct effects on Tribes, on the relationship between
the Federal government and Indian Tribes, or on the distribution of
power and responsibilities between the Federal government and Indian
Tribes, as specified in Executive Order 13175. Thus, Executive Order
13175 does not apply to this action.
EPA periodically updates Tribal officials on air regulations
through the monthly meetings of the National Tribal Air Association and
has shared information on this rulemaking through this and other fora.
G. Executive Order 13045: Protection of Children From Environmental
Health Risks and Safety Risks
EPA interprets Executive Order 13045 as applying only to those
regulatory actions that concern environmental health or safety risks
that EPA has reason to believe may disproportionately affect children,
per the definition of ``covered regulatory action'' in section 2-202 of
the Executive Order.
Therefore, this action is not subject to Executive Order 13045
because it does not concern an environmental health risk or safety
risk. Since this action does not concern human health, EPA's Policy on
Children's Health also does not apply.
H. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution or Use
This action is not a ``significant energy action'' because it is
not likely to have a significant adverse effect on the supply,
distribution, or use of energy. This action applies to certain
regulated substances and certain applications containing regulated
substances, none of which are used to supply or distribute energy.
I. National Technology Transfer and Advancement Act
This rulemaking does not involve technical standards.
J. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations and
Executive Order 14096: Revitalizing Our Nation's Commitment to
Environmental Justice for All
The EPA believes that this type of action does not concern human
health or environmental conditions and therefore cannot be evaluated
with respect to potentially disproportionate and adverse effects on
communities with environmental justice concerns. This proposed rule
does not change the HFC phasedown schedule.
Although this action does not concern human health or environmental
conditions, the EPA identified and addressed environmental justice
concerns associated with the HFC phasedown within the Allocation
Framework Rule (86 FR 55116, October 5, 2021) and the 2024 Allocation
Rule (88 FR 46836, July 20, 2023). In these rulemakings, EPA identified
and addressed environmental justice concerns by assessing available
information to analyze baseline human health or environmental
conditions, conducting updated analyses based on more recently
available data, and providing meaningful participation opportunities
for communities with environmental justice concerns. EPA carefully
evaluated available information on HFC production facilities and the
characteristics of nearby communities. Based on EPA's analysis, EPA
found evidence of environmental justice concerns near HFC production
facilities from cumulative exposure to existing environmental hazards
in these communities.
List of Subjects in 40 CFR Part 84
Environmental protection, Administrative practice and procedure,
Air pollution control, Chemicals, Climate Change, Emissions, Imports,
Reporting and recordkeeping requirements.
Michael S. Regan,
Administrator.
For the reasons set out in the preamble, the EPA proposes to amend
40 CFR part 84 as follows:
PART 84 PHASEDOWN OF HYDROFLUOROCARBONS
0
1. The authority citation for part 84 continues to read as follows:
Authority: Pub. L. 116-260, Division S, Sec. 103.
0
2. Amend Sec. 84.3 by adding the definitions ``Healthcare system
need'', ``Responsible corporate officer'', and ``Responsible official''
in alphabetical order to read as follows:
Sec. 84.3 Definitions.
* * * * *
Healthcare system need means circumstances where an increase in
demand for MDIs used to treat asthma, chronic obstructive pulmonary
disease, and other respiratory diseases may occur because of a change
in market conditions that otherwise would not be included in calculated
rates of growth.
* * * * *
Responsible corporate officer means a person who is authorized by
the regulated entity to make representations on behalf of, or obligate
the company as ultimately responsible for, any activity regulated under
40 CFR part 84, subpart A.
Responsible official means a person who is authorized by the
regulated entity to make representations on behalf of, or obligate the
company as ultimately responsible for, any activity regulated under 40
CFR part 84, subpart A.
* * * * *
0
3. Amend Sec. 84.5 by:
0
a. In paragraph (a)(1), adding ``, unexpended production for export
allowances,'' after the phrase ``unexpended production allowances and
consumption allowances''.
0
b. Revising paragraph (c)(2).
0
c. In paragraph (d), adding ``production for export,'' after ``All
production, consumption,'' and adding ``production for export,'' after
the phrase ``confer a production, consumption,''.
0
d. Revising paragraph (f).
0
e. Adding paragraph (k).
The revisions and additions read as follows:
Sec. 84.5 Prohibitions relating to regulated substances.
* * * * *
(c) * * *
(2) No person may use a regulated substance produced or imported by
expending application-specific allowances for any purpose other than
those for which the application-specific allowance was allocated, and
as set forth in this paragraph (c). Application-specific allowances are
apportioned to a person under Sec. Sec. 84.13 and 84.15 for the
production or import of regulated substances solely for the individual
application listed on the allowance.
* * * * *
(f) Sale and distribution. No person may sell or distribute, or
offer for sale or distribution, any regulated substance
[[Page 75940]]
that was produced or imported in violation of paragraphs (a) through
(d) of this section, except:
(1) for such actions needed to re-export the regulated substance;
or
(2) if the regulated substance was purchased at a government
auction authorized by the United States Customs and Border Protection
and consumption allowances were expended in the requisite quantity to
cover the regulated substances at issue.
Every kilogram of a regulated substance sold or distributed, or
offered for sale or distribution, in contravention of this paragraph
constitutes a separate violation of this subpart. Sale or distribution,
or offer for sale or distribution, of less than one kilogram of
regulated substance in contravention of this paragraph constitutes a
separate violation of this subpart.
* * * * *
(k) Production for export allowances. No person may use a regulated
substance produced by expending production for export allowances for
any purpose other than those for which the production for export
allowance was allocated, aligning with the applications as listed in
Sec. 84.13(a).
0
4. Amend Sec. 84.9 by:
0
a. In paragraph (b)(3) adding ``and 3,000.0 MTEVe allowances to be
allocated pursuant to Sec. 84.18,'' after ``Sec. 84.13''.
0
b. Redesignating paragraph (c) as paragraph (d).
0
c. Adding new paragraph (c).
The addition reads as follows:
Sec. 84.9 Allocation of calendar-year production allowances.
* * * * *
(c) Starting with the allocation of 2026 calendar year allowances,
the relevant Agency official will withhold ten percent of production
allowances otherwise calculated under paragraph (b) of this section
from any entity that produced regulated substances in any calendar year
2011 through 2019 for a separate entity that is being issued
application-specific allowances in accordance with Sec. 84.13, except
for mission-critical military end uses. If there are remaining
production allowances after distribution from the set-aside under Sec.
84.15, the relevant agency official will distribute such allowances to
the entity from which they were withheld.
* * * * *
0
5. Amend Sec. 84.11 by:
0
a. Redesignating the second paragraph (c) as paragraph (e).
0
b. Redesignating paragraph (c) as paragraph (d).
0
c. Adding new paragraph (c).
The addition reads as follows:
Sec. 84.11 Allocation of calendar-year consumption allowances.
* * * * *
(c) Starting with the allocation of 2026 calendar year allowances,
the relevant Agency official will withhold ten percent of consumption
allowances otherwise calculated under paragraph (b) of this section
from any entity that imported regulated substances in any calendar year
2011 through 2019 for a separate entity that is being issued
application-specific allowances in accordance with Sec. 84.13, except
for mission-critical military end uses. If there are remaining
consumption allowances after distribution from the set-aside under
Sec. 84.15, the relevant agency official will distribute such
allowances to the entity from which they were withheld.
* * * * *
0
6. Amend Sec. 84.13 by:
0
a. In paragraph (a), removing ``2022, 2023, 2024, and 2025'' and adding
in their place ``as designated''.
0
b. In paragraph (a)(1), adding ``for calendar years 2022-2030'' after
the phrase ``metered dose inhalers''.
0
c. In paragraph (a)(2), adding ``for calendar years 2022-2025'' after
the phrase ``defense sprays''.
0
d. In paragraph (a)(3), adding ``for calendar years 2022-2030'' after
the phrase ``trailer use''.
0
e. In paragraph (a)(4), adding ``for calendar years 2022-2030'' after
the phrase ``semiconductor manufacturing sector''.
0
f. In paragraph (a)(5), adding ``for calendar years 2022-2030'' after
the phrase ``end uses''.
0
g. In paragraph (a)(6), adding ``for calendar years 2022-2030'' after
the phrase ``fire suppression''.
0
h. In paragraph (b)(1), adding ``, including supporting documentation
that verifies this need'' after the phrase ``this section''.
0
i. In paragraph (b)(1)(ii) remove ``or'' after the phrase ``facility or
facilities;''.
0
j. In paragraph (b)(1)(iii), removing ``A global pandemic or other
public health emergency that increases'' and adding in their place ``A
global pandemic, other public health emergency, or other healthcare
system needs related to increased'' and removing ``inhalers.'' and
adding in its place ``inhalers;''.
0
k. Adding paragraphs (b)(1)(iv) and (v).
0
l. Adding paragraph (b)(2).
0
m. Redesignating paragraph (c)(1) as paragraph (c)(7).
0
n. Adding new paragraph (c)(1).
0
o. Adding paragraphs (c)(4) through (6).
0
p. Revising newly redesignated paragraph (c)(7) introductory text.
0
q. Removing paragraph (e).
0
r. Redesignating paragraphs (f) through (h) as paragraphs (e) through
(g), respectively.
0
s. Adding new paragraph (h).
The revisions and additions read as follows:
Sec. 84.13 Allocation of application-specific allowances.
* * * * *
(b) * * *
(1) * * *
(iv) Economic disruption outside the immediate control of the
applicant; or
(v) Buildup of a stockpile of a specific regulated substance in the
event of a production cessation. Requests for this unique circumstances
must include: a letter from the applicant's supplier signed by a
responsible corporate officer stating that the supplier is ceasing all
production of the regulated substance at issue within three years;
certification that the applicant has regulatory requirements beyond
this part that limit ability to switch suppliers or there are no other
suppliers that could meet their needs; and evidence that the applicant
has a restricted HFC supply chain.
(2) Entities must provide an estimate of the total quantity of
regulated substances they expect to purchase in the following calendar
year based on their expected eligibility for allowances.
(c) * * *
(1) Accounting for verified changes in inventory in calculating
growth rates and purchase amounts, except:
(i) for applications for mission-critical military end uses; and
(ii) if the applying entity provides a rationale deemed acceptable
by the relevant agency official as to why inventory buildup should not
be accounted for;
* * * * *
(4) Subtracting out quantities reported under Sec. 84.31(h)(1)(x)
in calculating growth rates and purchase amounts;
(5) Allocating allowances equivalent to the highest verified
purchase amount measured in exchange value equivalent from the prior
three years for entities that meet any of the following criteria:
(i) entity purchased less than 100 kilograms of regulated
substances in at least one of the last three years, and the average
growth rate of use for the company over the past three years calculated
under paragraph (7)(i) is equal to or greater than 200 percent;
(ii) entity had zero purchases in one of the last three years for
reasons other than newly using regulated substances; or
(iii) entity purchased equal to or less than 100 kilograms of
regulated
[[Page 75941]]
substances in each of the past three years;
(6) For the application of structural composite preformed
polyurethane foam for marine use and trailer use, utilizing the
exchange value for HFC-152a in calculating the allowance allocation,
regardless of what regulated substance was used by an entity;
(7) For all other entities, multiplying the use of regulated
substances by the company in the specific application in the prior year
by the higher of:
* * * * *
(h) Any entity receiving an allocation of allowances pursuant to
this section may voluntarily choose to return any quantity of
allowances to EPA up to, and including, June 30 of the calendar year in
which the allowances can be expended. If any allowances are so
returned, those allowances will be distributed to the persons who meet
the criteria listed in Sec. Sec. 84.9 and 84.11 proportionate to
entities' market share as calculated in Sec. Sec. 84.9(b)(2) and
84.11(b)(5).
0
7. Add Sec. 84.14 to read as follows:
Sec. 84.14 Petition for designation of an application as eligible for
application-specific allowances.
(a) Petitions filed pursuant to 42 U.S.C. 7675(e)(4)(B)(ii) must
include:
(1) A description of the application, including an explanation of
what the application is, what purpose or function it achieves, and what
populations or commercial products benefit from the application;
(2) A list of regulated substance(s) and description of their use
in the application and an explanation as to why regulated substances
are required in the application;
(3) Evidence that no safe or technically achievable substitute is
or is expected to be available, and that the petitioner has conducted
research to evaluate substitutes for the regulated substance(s);
(4) Evidence that supply of the regulated substance(s) used in the
application is insufficient to accommodate the application;
(5) A signed and notarized certification from a responsible
corporate officer at the requesting entity that the application cannot
use recovered and reprocessed regulated substance in conjunction with
or in place of virgin regulated substance, either due to demonstrated
lack of technical achievability or insufficient supply, and an
explanation and evidence documenting why recovered and reprocessed
regulated substance cannot be used for the application;
(6) Total quantity (in kilograms) of all regulated substances
acquired by each entity submitting the petition for the application
specified in the petition in each of the previous three years,
including records documenting that quantity;
(7) The name of the entity or entities supplying regulated
substances and contact information for those suppliers over the past
three years;
(8) Total quantity (in kilograms) of each regulated substance held
in inventory by each entity submitting the petition as of the date the
petition is submitted;
(9) An estimate of the total quantity of regulated substances the
petitioner expects to purchase in the first year it would be eligible
for ASAs;
(10) Data on the proportion of the overall cost of the product or
system that reflects the cost of regulated substances for each entity;
(11) Historic and projected sales for the product or system for
each entity;
(12) Evidence of research into design changes to decrease the
amount of regulated substance used in the product or system;
(13) An explanation regarding whether the use of the regulated
substance(s) is necessary for the health, safety, or is critical for
the functioning of society (encompassing cultural and intellectual
aspects);
(14) An explanation regarding steps taken to minimize the use of
the regulated substance and any associated emission of the HFC(s); and
(15) Information on regulatory restrictions related to possible
alternatives and substitutes.
(b) If the petition does not include the required information
listed in paragraph (a), the petition will be deemed incomplete, and
EPA will notify the entity submitting the petition.
(c) In the event that an application becomes eligible to receive
application-specific allowances:
(1) EPA will allocate allowances to entities in a new application
in accordance with Sec. 84.13; and
(2) A new application would be eligible to receive application-
specific allowances for no longer than the latest calendar year
included in Sec. 84.13(a).
0
8. Amend Sec. 84.15 by adding paragraph (h) to read as follows:
Sec. 84.15 Set-aside of application-specific allowances, production
allowances, and consumption allowances.
* * * * *
(h) Consumption and production allowances from Sec. 84.9(c) and
Sec. 84.11(c) are available in the form of application-specific
allowances to entities that request them no later than April 30 of the
calendar year in which the allowances may be expended that:
(1) qualify for application-specific allowances under Sec. 84.13;
(2) provide supporting documentation that verify a need to purchase
regulated substances in the present calendar year beyond what is
reflected by the rates of growth calculated in Sec. 84.13(c)(1);
(3) are facing a situation that qualifies as a unique circumstance
as defined in Sec. 84.13(b)(iii); and
(4) demonstrate to the satisfaction of the relevant agency official
that the situation described in paragraph (3) was unknowable at the
time the entity made its request for application-specific allowances
pursuant to Sec. 84.13(b).
0
9. Amend Sec. 84.17 by:
0
a. In the introductory text, adding the language ``, except for the
export of regulated substances produced with a production for export
allowance'' to the end of the first sentence.
0
b. Revising paragraph (a)(5).
The revision reads as follows:
Sec. 84.17 Availability of additional consumption allowances.
* * * * *
(a) * * *
(5) The source of the regulated substances and whether the date
purchased was before or after January 1, 2022;
* * * * *
0
10. Add Sec. 84.18 to read as follows:
Sec. 84.18 Authorization of production for export allowances.
(a) EPA will allocate 3,000.0 MTEVe of production for export
allowances to Iofina Chemical by October 1 of the calendar year prior
to the year in which the allowances may be used for calendar years
2026, 2027, 2028, 2029, and 2030.
(b) Production for export allowances cannot be transferred.
(c) Any regulated substances produced with production for export
allowances must be exported in the same calendar year it was produced.
0
11. Amend Sec. 84.31 by:
0
a. In the introductory text of paragraph (a), removing the phrase ``in
the six applications listed in subsection (e)(4)(B)(iv) of the AIM
Act''.
0
b. Redesignating paragraphs (d)(1)(vii) and (d)(1)(viii) as paragraphs
(d)(1)(viii) and (d)(1)(ix), respectively.
0
c. Adding new paragraph (d)(1)(vii).
0
d. In paragraph (h)(1)(i), adding ``, including a copy of the sales
records, invoices, or other records documenting that quantity'' after
the word ``months''.
0
e. In paragraph (h)(1)(ii), adding ``, including a copy of the sales
records, invoices, or other records documenting that quantity'' after
the word ``months''.
[[Page 75942]]
0
f. In paragraph (h)(1)(iii), adding ``, including a copy of the sales
records, invoices, or other records documenting that quantity'' after
the parenthetical ``(i.e., from the open market)''.
0
g. In paragraph (h)(1)(iv), adding ``, including a copy of inventory
records documenting that quantity;'' after the word ``use''.
0
h. In paragraph (h)(1)(viii), removing the last ``and'' after the
phrase ``additional need''.
0
i. In paragraph (h)(1)(ix), removing ``allowances.'' and adding in its
place ``allowances; and''.
0
j. Adding paragraph (h)(1)(x).
0
k. In paragraph (h)(2)(iv), adding ``, including a copy of inventory
records documenting that quantity;'' after the phrase ``current year''.
0
l. In the introductory text of paragraph (h)(4), removing ``, except
for the conferral of allowances for mission-critical military end
uses,''.
0
m. In paragraph (h)(7)(i), removing ``annual'' and adding in its place
``biannual''.
0
n. Redesignating paragraphs (h)(7)(iii) through (h)(7)(vi) as
paragraphs (h)(7)(iv) through (h)(7)(vii), respectively.
0
o. Adding new paragraph (h)(7)(iii).
0
p. Redesignating paragraph (l) as paragraph (n).
0
q. Adding new paragraphs (l) and (m).
The revision and additions read as follows:
Sec. 84.31 Recordkeeping and reporting.
* * * * *
(d) * * *
(1) * * *
(vii) Internal Transaction Numbers for all shipments, except
shipments where an exemption from the requirements for the filing of
Electronic Export Information (EEI) is provided in 15 CFR part 30
Subpart D;
* * * * *
(h) * * *
(1) * * *
(x) If allowances are allocated for a unique circumstance under
Sec. 84.13(b)(1)(v), the quantity (in kilograms) of each regulated
substance purchased with the intent to build inventory during the prior
six-month period, including a copy of records documenting that
quantity.
* * * * *
(7) * * *
(iii) A copy of confirmation notices when conferring allowances for
application-specific use;
* * * * *
(l) Holders of production for export allowances. Any person
allocated production for export allowances must comply with the
following recordkeeping and reporting requirements:
(1) Quarterly Reporting. Within 45 days after the end of each
quarter, each holder of production for export allowances must submit to
the relevant Agency official a report containing the following
information:
(i) The quantity (in exchange value equivalent) of production for
export allowances expended for each regulated substance and the
quantity (in kilograms) of each regulated substance produced for
export;
(ii) The quantity (in kilograms) of each regulated substance
produced using production for export allowances that was exported;
(iii) The quantity (in kilograms) of each regulated substance
produced with production for export allowances held in inventory at the
end of the quarter;
(iv) Internal Transaction Numbers for all exports of regulated
substances produced with production for export allowances;
(v) The country or countries to which regulated substances produced
using production for export allowances were exported.
(2) Annual Reporting. Within 45 days after the end of the fourth
quarter, each holder of production for export allowances must submit to
the relevant Agency official a report containing the following
information:
(i) Signed certifications by a responsible corporate officer from
all foreign customers and supply intermediaries attesting that any
regulated substances produced using production for export allowances
will only be used in an application as listed in Sec. 84.13(a). Each
certification must include the name and address of the foreign entity,
and a contact person's name, email address, and phone number;
(ii) A description of how the use identified in the signed
certifications provided pursuant to paragraph (i) aligns with the
applications as listed in Sec. 84.13(a).
(3) Recordkeeping. Entities who receive production for export
allowances must maintain the following records for three years:
(i) A copy of all certifications reported pursuant to paragraph
(2)(i); and
(ii) Records demonstrating due diligence undertaken to verify and
ensure that all regulated substances produced with production for
export allowances and exported are being used in an application as
listed in Sec. 84.13(a).
(m) Purchasers of HFCs at a government auction. Any entity
purchasing regulated substances at a government auction authorized by
the United States Customs and Border Protection must report such
purchase as if they were an import consistent with the applicable
provisions under this section, except for the following adjustments.
(1) Quarterly reporting. The date that filing for that entry was
accepted by a United States Customs and Border Protection-authorized
electronic data interchange system, such as the Automated Broker
Interface, must be reported as the date on which the regulated
substances were imported for purposes of paragraph (c)(1)(v). Unless
otherwise unavailable, all requirements of paragraph (c)(1) must be
reported. If a data element is unavailable, the auction purchaser must
contact EPA and state that fact in writing by the time they make their
filed report.
(2) Recordkeeping. In addition to the records specified in
paragraph (c)(2), the auction purchaser must maintain records of the
auction purchase, including the accepted bid, confirmation of payment,
certification by the entity that they expended allowances, container
composition testing to verify the regulated substances contained within
the cylinder, and all other final documentation of the auction
purchase. Unless otherwise unavailable, all requirements of paragraph
(c)(2) must be met. If a data element is unavailable, the auction
purchaser must contact EPA and state that fact in writing by the time
they make their filed report.
(3) Advance notification. The auction purchaser must report the
information specified in paragraph (c)(7) prior to the HFCs entering
U.S. commerce. The requirement in paragraph (c)(7)(xvi) does not apply
if a certificate of analysis is not available at the time of submitting
the information in paragraph (c)(7). The entity must complete all
required sampling and testing required in this subpart prior to sale in
U.S. commerce and maintain such records consistent with 84.31.
* * * * *
0
12. Amend Sec. 84.54 by revising paragraph (a)(16)(i)(O) and adding
paragraph (a)(16)(i)(P) to read as follows:
Sec. 84.54 Restrictions on the use of hydrofluorocarbons.
(a) * * *
(16) * * *
(i) * * *
(O) Products for removing bandage adhesives from skin; and
(P) Defense sprays as defined at Sec. 84.3.
* * * * *
[[Page 75943]]
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13. Amend Sec. 84.60 by adding paragraphs (a)(7) and (b)(3) to read as
follows:
Sec. 84.60 Recordkeeping and reporting.
(a) * * *
(7) Effective [DATE], this paragraph shall apply to defense sprays
as defined at Sec. 84.3 and structural composite preformed
polyurethane foam as defined at Sec. 84.3.
(b) * * *
(3) Effective [DATE], this paragraph shall apply to defense sprays
as defined at Sec. 84.3 and structural composite preformed
polyurethane foam as defined at Sec. 84.3.
[FR Doc. 2024-20602 Filed 9-13-24; 8:45 am]
BILLING CODE 6560-50-P