Phasedown of Hydrofluorocarbons: Management of Certain Hydrofluorocarbons and Substitutes Under the American Innovation and Manufacturing Act of 2020

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Federal RegisterOct 11, 2024
89 Fed. Reg. 82682 (Oct. 11, 2024)
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    Environmental Protection Agency
  • 40 CFR Parts 84, 261, 262, 266, 270, and 271
  • [EPA-HQ-OAR-2022-0606; FRL-10105-02-OAR]
  • RIN 2060-AV84
  • AGENCY:

    Environmental Protection Agency (EPA)

    ACTION:

    Final rule.

    SUMMARY:

    The U.S. Environmental Protection Agency is issuing regulations to implement certain provisions of the American Innovation and Manufacturing Act of 2020. This rulemaking establishes an emissions reduction and reclamation program for the management of hydrofluorocarbons that includes requirements for leak repair and installation and use of automatic leak detection systems for certain equipment using refrigerants containing hydrofluorocarbons and certain substitutes; the servicing and/or repair of certain refrigerant-containing equipment to be done with reclaimed hydrofluorocarbons; the initial installation and servicing and/or repair of fire suppression equipment to be done with recycled hydrofluorocarbons, technician training, and recycling of hydrofluorocarbons prior to the disposal of fire suppression equipment containing hydrofluorocarbons; removal of hydrofluorocarbons from disposable cylinders before discarding them; and certain recordkeeping, reporting, and labeling requirements. In addition, EPA is establishing alternative Resource Conservation and Recovery Act standards for certain ignitable spent refrigerants being recycled for reuse.

    DATES:

    This rule is effective December 10, 2024.

    FOR FURTHER INFORMATION CONTACT:

    Christian Wisniewski, Stratospheric Protection Division, Office of Atmospheric Protection (Mail Code 6205A), Environmental Protection Agency, 1200 Pennsylvania Ave. NW, Washington, DC 20460; telephone number: 202-564-0417; email address: wisniewski.christian@epa.gov. You may also visit EPA's website at https://www.epa.gov/climate-hfcs-reduction for further information.

    For information related to the alternative standards for certain ignitable spent refrigerants under the Resource Conservation and Recovery Act (RCRA), please contact Tracy Atagi, Materials Recovery and Waste Management Division, Office of Resource Conservation and Recovery (5304T), Environmental Protection Agency, 1200 Pennsylvania Ave. NW, Washington, DC 20460; telephone number: (202) 566-0511; email address: atagi.tracy@epa.gov.

    SUPPLEMENTARY INFORMATION:

    Throughout this document whenever “we,” “us,” “the Agency,” or “our” is used, we mean EPA. Acronyms that are used in this rulemaking that may be helpful include:

    AHRI—Air-Conditioning, Heating, and Refrigeration Institute

    ALD—Automatic Leak Detection

    AIM Act—American Innovation and Manufacturing Act of 2020

    APF—Air Permitting Forum

    APU—Auxiliary power unit

    ASHRAE—American Society of Heating, Refrigerating and Air-Conditioning Engineers

    ASTM—American Society for Testing and Materials

    BOEM—Bureau of Ocean Energy Management

    BTU/h—British thermal units per hour

    CAA—Clean Air Act

    CARB—California Air Resources Board

    CBI—Confidential Business Information

    CFC—Chlorofluorocarbon

    CFR—Code of Federal Regulations

    CH4 —Methane

    CO2 —Carbon dioxide

    CO2 e—Carbon Dioxide Equivalent

    DOD—Department of Defense

    DOI—Department of the Interior

    DOJ—Department of Justice

    DOT—Department of Transportation

    EEAP—Environmental Effects Assessment Panel

    EOL—End of Life

    EPA—Environmental Protection Agency

    ER&R—Emissions Reduction and Reclamation

    EVe—Exchange Value Equivalent

    FAA—Federal Aviation Administration

    FEMA—Fire Equipment Manufacturers Association

    F-HTFs—Fluorinated Heat Transfer Fluids

    FOIA—Freedom of Information Act

    FSSA—Fire Suppression Systems Association

    GHG—Greenhouse gas

    GWP—Global Warming Potential

    HARC—Halon Alternatives Research Corporation

    HCFC—Hydrochlorofluorocarbon

    HCFO—Hydrochlorofluoroolefin

    HEEP—HFC Emissions Estimating Program

    HFC—Hydrofluorocarbon

    HFO—Hydrofluoroolefin

    HSWA—Hazardous and Solid Waste Amendments of 1984

    HVAC—Heating, Ventilation, and Air Conditioning

    HVACR—Heating, Ventilation, Air Conditioning, and Refrigeration

    ICR—Information Collection Request

    in-Hg—inches of Mercury

    IPCC—Intergovernmental Panel on Climate Change

    IPR—Industrial Process Refrigeration

    LRM—Lifecycle refrigerant management

    MACS—Mobile Air Climate Systems Association

    MMTCO2 e—Million Metric Tons of Carbon Dioxide Equivalent

    MMTEVe—Million Metric Tons of Exchange Value Equivalent

    MVAC—Motor Vehicle Air Conditioner

    NAICS—North American Industrial Classification System

    NAFED—National Association of Fire Equipment Distributors

    NEDA/CAP—National Environmental Development Association's Clean Air Project

    NFPA—National Fire Protection Association

    NODA—Notice of Data Availability

    NRDC—Natural Resources Defense Council

    NTTAA—National Technology Transfer and Advancement Act

    OCS—Outer Continental Shelf

    OCSLA—Outer Continental Shelf Lands Act

    ODP—Ozone Depletion Potential

    ODS—Ozone-depleting substances

    OEM—Original Equipment Manufacturer

    OMB—Office of Management and Budget

    PII—Personally identifiable information

    ppm—Parts Per Million

    PRA—Paperwork Reduction Act

    PTAC—Packaged terminal air conditioners

    R4 Program—Refrigerant Recovery, Reclaim, and Reuse Requirements (CARB Program)

    RACA—Request for Additional Consumption Allowance

    RACHP—Refrigeration, Air Conditioning, and Heat Pumps

    RCOP—Recycling Code of Practice

    RCRA—Resource Conservation and Recovery Act

    RFA—Regulatory Flexibility Act

    RIA—Regulatory Impact Analysis

    SAE—Society of Automotive Engineers

    SC-HFC—Social Cost of Hydrofluorocarbons

    SISNOSE—Significant Economic Impact on a Substantial Number of Small Entities

    SNAP—Significant New Alternatives Policy

    TFA—Trifluoracetic acid

    TSD—Technical Support Document

    UMRA—Unfunded Mandates Reform Act

    VCOP—Voluntary Code of Practice

    VRF—Variable Refrigerant Flow

    VSQG—Very Small Quantity Generator

    Table of Contents

    I. Executive Summary

    A. What is the purpose of these regulations?

    B. What is the summary of the regulations finalized in this notice?

    C. What is the summary of the costs and benefits?

    II. General Information

    A. Do these regulations apply to me?

    B. What is EPA's authority for these regulations?

    III. Background

    A. What are HFCs?

    B. How do HFCs affect public health and welfare?

    C. What regulatory programs addressing refrigerants has EPA already established under the Clean Air Act?

    1. National Recycling and Emission Reduction Program (CAA section 608)

    2. Motor Vehicle Air Conditioning Servicing Program (CAA section 609)

    3. Significant New Alternatives Policy Program (CAA section 612)

    IV. How is EPA regulating the management of HFCs and their substitutes?

    A. What definitions is EPA implementing under subsection (h)?

    1. Terms That Did Not Generate Comment and That EPA Is Finalizing as Proposed

    2. Terms That Received Comment or That EPA is Modifying

    3. What additional comments did EPA receive on definitions?

    B. What types of equipment is EPA addressing under subsection (h)?

    C. How is EPA addressing leak repair?

    1. What refrigerants are subject to leak repair requirements?

    2. Appliances with what charge size are subject to leak repair requirements?

    3. What leak repair provisions is EPA establishing?

    a. Leak Rate Calculations

    b. Requirement To Repair Leaks, Timing and Applicable Leak Rates

    c. Verification Testing

    d. Leak Inspections

    e. Chronically Leaking Appliances

    f. Retrofit and Retirement Plans

    g. Recordkeeping and Reporting

    D. How is EPA establishing requirements for the installation of automatic leak detection systems?

    1. Automatic Leak Detection Requirements

    2. Recordkeeping and Reporting

    E. How is EPA establishing requirements for recovered and reclaimed HFCs?

    1. Reclamation Standard

    2. Requirements for Servicing and/or Repair of Existing Equipment in the RACHP sector

    F. How is EPA establishing an HFC emissions reduction program for the fire suppression sector?

    1. Nomenclature Used in This Section

    2. Emissions Reduction in the Fire Suppression Sector

    a. Minimizing Releases of HFCs

    b. Requirements for Initial Installation of Equipment for Fire Suppression

    c. Requirements for Servicing and/or Repair of Existing Equipment for Fire Suppression

    d. Fire Suppression Technician Training

    e. Recycling of HFCs Prior to Disposal of Fire Suppression Equipment Containing HFCs

    f. Recordkeeping and Reporting

    G. What requirements is EPA establishing for handling disposable cylinders?

    1. Requirements for Disposable Cylinders

    2. Small Cans of Refrigerant

    H. How is EPA establishing RCRA refrigerant recycling alternative standards?

    1. Nomenclature Used in This Section

    2. Background

    3. Final Alternative RCRA Standards for Ignitable Spent Refrigerants Being Recycled for Reuse

    a. Comments on the RCRA Alternative Standards and Changes Made in Response to Comments

    b. Scope of the Final RCRA Alternative Standards

    c. RCRA Alternative Standards Requirements

    4. RCRA Very Small Quantity Generator Wastes

    5. RCRA Regulation of Exports and Imports of Certain Ignitable Spent Refrigerants

    6. Applicability of Alternative Standard in RCRA-Authorized States

    7. Effect on State Authorization

    I. MVAC Servicing and Reprocessed Material

    V. How is EPA treating data reported under this rule?

    A. Background on Determinations of Whether Information is Entitled to Treatment as Confidential Information

    1. Confidential Treatment of Reported Information

    2. Emission Data Under section 114 of the Clean Air Act

    B. Data Elements Reported to EPA Under the Leak Repair Provisions

    C. Data Elements Related to Fire Suppression

    VI. What are the costs and benefits of this action?

    A. Background

    B. Estimated Costs and Benefits of the Final Rule

    1. Total Incremental Costs and Benefits of the Final Rule

    2. Estimating Costs and Benefits Based on Affected Equipment and Appliances

    VII. How is EPA considering environmental justice?

    VIII. How is EPA responding to other comments on the proposed rule?

    IX. Judicial Review

    X. Severability

    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 and Safety Risks

    H. Executive Order 13211: Actions That Significantly Affect Energy Supply, Distribution, or Use

    I. National Technology Transfer and Advancement Act (NTTAA)

    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

    K. Congressional Review Act (CRA)

    I. Executive Summary

    A. What is the purpose of these regulations?

    The Environmental Protection Agency (EPA) is issuing regulations 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 AIM Act authorizes EPA to address hydrofluorocarbons (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 rulemaking focuses on the third area—establishing certain regulations for HFCs and their substitutes for the purposes of maximizing reclaiming and minimizing releases of HFCs from equipment and ensuring the safety of technicians and consumers.

    EPA has issued regulations establishing and codifying a framework for phasing down HFC production and consumption through an allowance allocation program, “Phasedown of Hydrofluorocarbons: Establishing the Allowance Allocation and Trading Program Under the American Innovation and Manufacturing Act” (86 FR 55116, October 5, 2021)—referred to as the “Allocation Framework Rule” throughout this document. EPA finalized a separate rulemaking to update certain aspects of that regulatory framework (see final rule at 88 FR 46836, July 20, 2023)—referred to as the “2024 Allocation Rule” throughout this document.

    EPA has issued regulations addressing the framework for how EPA intends to implement its authority to restrict the use of HFCs in sectors and subsectors where they are used, as well as establishing certain restrictions on the use of HFCs in specific sectors or subsectors in which they are used, “Phasedown of Hydrofluorocarbons: Restrictions on the Use of Certain Hydrofluorocarbons Under the American Innovation and Manufacturing Act of 2020” (88 FR 73098, October 24, 2023)—referred to as the “2023 Technology Transitions Rule” throughout this document. EPA issued an interim final rule under the Technology Transitions program further addressing a particular subsector (88 FR 88825, December 26, 2023).

    More specifically, subsection (h) of the AIM Act, titled “Management of Regulated Substances,” directs EPA to promulgate regulations to control, where appropriate, any practice, process, or activity regarding the servicing, repair, disposal, or installation of equipment that involves: a regulated substance (used interchangeably with “HFCs” in this rulemaking), a substitute for a regulated substance, the reclaiming of a regulated substance used as a refrigerant, or the reclaiming of a substitute for a regulated substance used as a refrigerant.

    This rulemaking establishes the Emissions Reduction and Reclamation (ER&R) Program to implement the provisions of subsection (h), including its authority to issue regulations to control such practices, processes, or activities, particularly as related to the management, use, and reuse of HFCs and substitutes in equipment. Further, these regulations include provisions to support implementation of, compliance with, and enforcement of requirements under subsection (h) of the AIM Act.

    Additionally, EPA is establishing alternative RCRA standards for certain ignitable spent refrigerants being recycled for reuse, as that term is used under RCRA. These standards involve regulatory changes to 40 Code of Federal Regulations (CFR) parts 261 through 271 and are separate from the regulations under subsection (h)(1) of the AIM Act. These standards are established under a different set of statutory authorities than the ER&R regulations, and they are part of an independent and distinct regulatory regime. EPA is providing notice of the AIM Act regulations and the RCRA regulations in one Federal Register notice given both the RCRA regulations concerning the recovery and recycling of certain ignitable spent refrigerants and the AIM Act regulations concerning recovery and reclamation of refrigerants may be of interest to some of the same stakeholders.

    The terms “reclaim” and “recycle” have different regulatory purposes and definitions under RCRA than under the CAA and the AIM Act. Under RCRA, a material is “reclaimed” if it is processed to recover a usable product, or if it is regenerated. Examples are recovery of lead values from spent batteries and regeneration of spent solvents (See 40 CFR 261.1(c)(4)). Reclamation is one of the four types of “recycling” identified in 40 CFR 261.2(c) that can involve management of a solid waste under RCRA.

    B. What is the summary of the regulations finalized in this notice?

    EPA is promulgating two separate and distinct sets of regulations. First, EPA is establishing an ER&R program for the management of HFCs and certain substitutes under subsection (h) of the AIM Act. The Agency is including provisions that address the purposes identified in subsection (h)(1) of the AIM Act of maximizing reclamation, minimizing the release of HFCs from equipment, and ensuring the safety of technicians and consumers. Specifically, the AIM Act regulations include requirements for:

    • Leak repair of appliances that contain at least 15 pounds of a refrigerant that contains an HFC or a substitute for an HFC with a global warming potential (GWP) above 53, with specific exceptions;
    • Installation and use of an automatic leak detection (ALD) system for certain new and existing appliances containing 1,500 pounds or more of a refrigerant that contains an HFC or a substitute for an HFC with a GWP above 53;
    • A reclamation standard limiting the amount of virgin HFCs that can be contained in reclaimed HFC refrigerants;
    • The servicing and/or repair of existing equipment in certain refrigeration, air conditioning, and heat pumps (RACHP) subsectors to be done with reclaimed HFCs;
    • The servicing, repair, disposal, or installation of fire suppression equipment that contains HFCs, with the purpose of minimizing the release of HFCs from that equipment, including requirements for the initial installation and servicing and/or repair of fire suppression equipment to be done with recycled HFCs, as well as requirements related to technician training in the fire suppression sector;
    • Removal of HFCs from disposable cylinders before discarding; and
    • Recordkeeping, reporting, and labeling.

    Enforcement and compliance. To support compliance with these requirements, EPA is establishing labeling, reporting, and recordkeeping requirements as described in this rulemaking notice. The Agency intends to use a reporting platform the same as or similar to those used for prior AIM Act rules, and will consider making information not entitled to confidential treatment, as described in section V of this action, publicly available.

    Exemptions for certain applications and other provisions. Provisions finalized in this action do not apply to two applications, mission-critical military end uses and on board aerospace fire suppression, as listed at 40 CFR 84.13(a), for a year or years for which that application receives an application-specific allowance as defined at 40 CFR 84.3. As such, the provisions established in this action include exemptions for the following applications, for a year or years for which that application receives an application-specific allowance:

    • Mission-critical military end uses and
    • On board aerospace fire suppression.

    Amendments to the RCRA hazardous waste regulations. Second, EPA is amending a separate set of regulations promulgated under RCRA, a separate statutory authority from the AIM Act, to establish alternative standards for ignitable spent refrigerants when “recycled for reuse,” as the term is to be defined under RCRA. EPA is establishing that the alternative standards at 40 CFR part 266, subpart Q, under RCRA, apply to HFCs and other substitutes that are lower flammability ( i.e., that do not belong to flammability Class 3 as classified by the American Society of Heating, Refrigerating and Air-Conditioning Engineers (ASHRAE) Standard 34-2022). EPA is limiting the alternative standards to lower flammability HFCs and substitutes (Class 1, 2, and 2L) because of the lower risk of fire from the collection and recycling for reuse of these refrigerants, and the greater market value of these refrigerants, which supports the conclusion that these spent refrigerants will be recycled for reuse and not stockpiled, mismanaged, or abandoned.

    ASHRAE Standard 34-2022 assigns a safety group classification for each refrigerant that consists of two alphanumeric characters ( e.g., A2 or B1). The capital letter indicates the toxicity class (“A” for lower toxicity) and the numeral denotes the flammability. ASHRAE recognizes three classifications and one subclass for refrigerant flammability. The three main flammability classifications are Class 1, for refrigerants that do not propagate a flame when tested as per the ASHRAE 34 standard, “Designation and Safety Classification of Refrigerants;” Class 2, for refrigerants of lower flammability; and Class 3, for highly flammable refrigerants, such as the hydrocarbon refrigerants. ASHRAE recently updated the safety classification matrix to include a new flammability subclass 2L, for flammability Class 2 refrigerants that burn very slowly.

    Other topics. Together with the proposal for this rule, EPA issued an advanced notice of proposed rulemaking (ANPRM) seeking information on approaches for establishing requirements for technician training and/or certification. As stated at proposal, EPA is not addressing technician training in this final rulemaking and accordingly is not responding to comments on the ANPRM in this final rule.

    Additionally, EPA is not finalizing as part of this action under the AIM Act the proposed provisions for container tracking of HFCs that could be used in the servicing, repair, and/or installation of refrigerant-containing or fire suppression equipment. EPA is also not finalizing in this action provisions requiring the initial installation of refrigerant-containing equipment in certain subsectors in the RACHP sector to be done with reclaimed refrigerant where HFCs or a blend containing HFCs are used. The Agency intends to further consider those provisions and the comments submitted on the proposed requirements before determining how to proceed. As such, EPA need not respond to public comments on those proposed requirements as part of this action.

    EPA received many comments on this rulemaking, including those that were in general support or opposition of the various provisions. Specific comments as relevant to provisions in this rulemaking are discussed in the respective sections of this rulemaking. Some comments raised issues that are beyond the scope of this rulemaking; because those comments require no response, EPA need not address them in this notice, though in many cases the Agency has noted the submission of such comments for informational purposes.

    C. What is the summary of the costs and benefits?

    The costs and benefits for the provisions related to managing regulated substances and their substitutes in this rule comes from the Analysis of the Economic Impact and Benefits of the Final Rule: Management of Certain Hydrofluorocarbons and Substitutes Under Subsection (h) of the American Innovation and Manufacturing Act of 2020 technical support document (TSD) (referred to as the “Economic Impact and Benefits TSD” in this rule) and the Regulatory Impact Analysis (RIA) Addendum for this rule (referred to in this rule as the “RIA addendum”) contained in the docket of this rule to provide the public with information on the relevant costs and benefits of this action, and to comply with executive orders. EPA notes that the costs and benefits associated with the management of regulated substances and their substitutes under the AIM Act are described and calculated separately from those associated with the amendments to the RCRA hazardous waste regulations. These analyses—as summarized later in this section—highlight the economic costs and benefits of the provisions in this rulemaking.

    Given that the provisions being finalized concern the management of HFCs, and HFCs are subject to the phasedown of production and consumption under the AIM Act, the Agency relied on its previous analyses as a starting point for the assessment of costs and benefits of this rule. Specifically, the Allocation Framework Rule, “Phasedown of Hydrofluorocarbons: Establishing the Allowance Allocation and Trading Program Under the American Innovation and Manufacturing Act” (86 FR 55116, October 5, 2021), the 2024 Allocation Rule, “Phasedown of Hydrofluorocarbons: Allowance Allocation Methodology for 2024 and Later Years” (88 FR 46836, July 20, 2023), and the 2023 Technology Transitions Rule, “Phasedown of Hydrofluorocarbons: Restrictions on the Use of Certain Hydrofluorocarbons Under the American Innovation and Manufacturing Act of 2020” (88 FR 73098, October 24, 2023) are assumed as a baseline for this rule. In this way, EPA analyzed the potential incremental impacts of the rule, attributing benefits only insofar as they are additional to those already assessed in the Allocation Framework Rule RIA, the 2024 Allocation Rule RIA Addendum, and the 2023 Technology Transitions Rule RIA Addendum (collectively referred to as “Allocation and 2023 Technology Transitions Rules” in this discussion).

    This rule established the methodology for allocating HFC production and consumption allowances starting with calendar year 2024 allowances and adjusted the consumption baseline downward by less than 0.5 percent to reflect corrected data, among other changes (88 FR 46836, July 20, 2023). EPA also finalized another rulemaking in 2023 to update the regulations established in the HFC Allocation Framework Rule. That rule “Phasedown of Hydrofluorocarbons: Adjustment to the Hydrofluorocarbon Baseline,” amended the production baseline downward by 0.005 percent to reflect corrected data (88 FR 44220, July 12, 2023).

    As detailed in the RIA addendum and the Economic Impact and Benefits TSD, the number, charge sizes, leak rates, and other characteristics of potentially affected RACHP equipment were estimated using EPA's Vintaging Model. These estimates served as a basis for calculating the reductions in HFC consumption and emissions from the various requirements of the final rule. As described in the RIA addendum and the Economic Impact and Benefits TSD, the leak repair and ALD system provisions finalized in this rule are assumed to result in the repair of leaking systems earlier than they otherwise would have, leading to reduced emissions of HFCs. Provisions requiring reclaimed refrigerant, requirements for the fire suppression sector, and provisions related to the handling of disposable cylinders are further estimated to result in incremental reductions in HFC emissions.

    U.S. EPA. 2023. EPA's Vintaging Model representing the Allocation Framework Rule as modified by the 2024 Allocation Rule RIA Addendum and the 2023 Technology Transitions Rule RIA Addendum. VM IO file_v4.4_02.04.16_Final TT Rule 2023 High Addition.

    Estimated reductions in HFC releases from equipment result in climate benefits due to reduced climate forcing, which have been monetized in the RIA addendum by multiplying avoided emissions by estimates of the social cost of each HFC (collectively referred to as SC-HFC) affected by the rule. The RIA addendum includes these SC-HFC estimates and uses them in some of the analyses for the purpose of providing information to the public and to comply with executive orders. Although we utilized the SC-HFC estimates for purposes of those analyses, this action does not rely on those values or the resulting quantification of climate benefits as a record basis for this rule, and we would reach the same conclusions in absence of the social costs of HFCs. In the years 2026 through 2050, EPA estimates the rule will prevent approximately 120 million metric tons of carbon dioxide equivalent (MMTCO2 e) in HFC emissions, and the present value of economic benefit of avoiding the damages associated with those emissions is estimated at $8.4 billion (discounted to 2024 dollars using a three percent discount rate). The annual benefits are estimated to decrease over time due to the HFC phasedown and the transition out of the higher-GWP HFCs, lowering the average GWP of later emissions. For example, it is estimated that the leak repair and ALD system provisions will prevent approximately 5.6 MMTCO2 e of HFC emissions in 2030 and 3.0 MMTCO2 e in 2040.

    Unless stated otherwise, costs and benefits in this section are presented in 2022 dollars.

    Reducing HFC emissions due to fixing leaks earlier is also anticipated to lead to savings for some system owners and operators, as less new refrigerant needs to be purchased to replace leaked refrigerant. In 2026, it is estimated that the leak repair and ALD provisions will lead to savings of $19.5 million (2022$) based on reduced HFC refrigerant needed to maintain the equipment. We also are aware that a refrigerant-containing appliance would operate less efficiently if not properly charged and maintained, leading to increased energy costs; however, we have not quantified such savings in our analysis. EPA acknowledges that these $19.5 million in savings may not completely offset leak repair compliance costs and may not accrue uniformly to all regulated entities. Further, while these provisions have been estimated to result in savings, EPA understands that entities that may be affected by these regulations might not perform the practices, processes, or activities that would result in cost savings absent regulation. When entities are reviewing their own economic analyses, some factors may be pertinent that make new technologies or economically favorable best practices less attractive than existing practices, or some market failure may exist that acts as a barrier to businesses' adoption of the most profitable course. For example, market failures may exist where there is imperfect information or split incentives, such as decision-makers not knowing the percentage of energy use associated with refrigeration or the costs of replacing refrigerant lost from leaking appliances.

    Klemick, Heather & Kopits, Elizabeth & Wolverton, Ann. “Potential Barriers to Improving Energy Efficiency in Commercial Buildings: The Case of Supermarket Refrigeration.” Journal of Benefit-Cost Analysis. 8, 2017, pp. 1-31.

    The compliance costs of the rule include recordkeeping and reporting costs, the costs of purchasing and operating ALD systems, costs of required inspections, the cost of repairing leaks earlier than would have been necessary without the provisions, the costs associated with using reclaimed HFCs in certain RACHP subsectors for the servicing of existing equipment (vis a vis virgin manufactured HFCs), the costs associated with minimizing releases of HFCs from fire suppression equipment (including using recycled HFCs in the initial and servicing and/or repair of fire suppression equipment), and the cost of disposable cylinder management requirements. In the years 2026 through 2050, these provisions would result in compliance costs (inclusive of refrigerant savings) with a present value estimated at $1.5 billion (in 2022 dollars discounted to 2024) at a two percent discount rate, $1.3 billion at a three percent discount rate, or $0.9 billion at a seven percent discount rate.

    Taking into account both benefits and compliance costs over the 2026 through 2050 time period, it is estimated that the rule results in present value net benefit (climate benefits, as monetized by application of SC-HFCs, discounted at three percent, minus compliance costs) of $6.9 billion (with compliance costs discounted at two percent) to $7.5 billion (with compliance costs discounted at seven percent).

    As detailed in the RIA addendum and the Economic Impact and Benefits TSD, these values represent an estimate of potential incremental benefits and assume that industry would comply with previous AIM Act regulations as outlined in the 2023 Technology Transitions RIA Addendum but would not undertake certain improvements to leak repair and refrigerant recovery practices in the absence of this rulemaking that were not required by those regulations. Since these assumptions are ultimately uncertain, in the RIA addendum and the Economic Impact and Benefits TSD, EPA has also provided estimates under an additional scenario in which leak repair and recovery improvements do occur in the baseline, thus resulting in lower incremental benefits. The assumptions in this alternative scenario translate into reduced estimates of the incremental effect of the provisions of this final rule since additional impacts are only quantified insofar as they go beyond baseline assumptions of existing policy and industry practice.

    In the 2023 Technology Transitions RIA Addendum, EPA analyzed a “base case” and a “high additionality” scenario. The former is used as the baseline to analyze the base case scenario for this rule. See the RIA addendum and Economic Impact and Benefits TSD for additional details.

    Some of the information regarding projected impacts of certain aspects of the action was considered by EPA as it finalized this rulemaking. To the extent that EPA has considered such information, it is compiled in the Economic Impact and Benefits TSD, which is in the docket for this rulemaking. While EPA has included estimates of the costs and benefits of this rulemaking in the RIA addendum to provide the public with information on the relevant costs and benefits of this action and to comply with Executive Orders, the analysis in the RIA addendum does not form a basis or rationale for any of the provisions EPA is promulgating in this rulemaking.

    Further, as explained previously in this section, although EPA is using the SC-HFCs for purposes of some of the analysis in the RIA addendum, this action does not rely on those SC-HFC estimates as a record basis for the Agency's action. EPA would reach the conclusions in this rule even in the absence of the SC-HFCs. Additional information on these analyses can be found in section VI of this preamble, as well as the RIA addendum, which is in the docket for this rulemaking.

    II. General information

    A. Do these regulations apply to me?

    You may be potentially affected by the regulations established in this final rule if you own, operate, service, repair, recycle, dispose, or install equipment containing HFCs or their substitutes, as well as if you recover, recycle, or reclaim HFCs or their substitutes. You may also be potentially affected if you manufacture or sell equipment containing HFCs or their substitutes. Potentially affected categories, by North American Industrial Classification System (NAICS) code, are included in Table 1.

    Table 1—NAICS Classification of Potentially Affected Entities

    NAICS Code NAICS industry description
    236118 Residential Remodelers.
    236220 Commercial and Institutional Building Construction.
    238220 Plumbing, Heating, and Air-Conditioning Contractors.
    238990 All Other Specialty Trade Contractors.
    311812 Commercial Bakeries.
    321999 All Other Miscellaneous Wood Product Manufacturing.
    322299 All Other Converted Paper Product Manufacturing.
    324191 Petroleum Lubricating Oil and Grease Manufacturing.
    324199 All Other Petroleum and Coal Products 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.
    326299 All Other Rubber Product Manufacturing.
    327999 All Other Miscellaneous Nonmetallic Mineral Product Manufacturing.
    332812 Metal Coating, Engraving (except Jewelry and Silverware), and Allied Services to Manufacturers.
    332999 All Other Miscellaneous Fabricated Metal Product Manufacturing.
    333415 Air-Conditioning and Warm Air Heating Equipment and Commercial and Industrial Refrigeration Equipment Manufacturing.
    333511 Industrial Mold Manufacturing.
    333912 Air and Gas Compressor Manufacturing.
    333999 All Other Miscellaneous General Purpose Machinery Manufacturing.
    334413 Semiconductor and Related Device Manufacturing.
    334419 Other Electronic Component Manufacturing.
    334516 Analytical Laboratory Instrument Manufacturing.
    335220 Major Household Appliance Manufacturing.
    336120 Heavy-Duty Truck Manufacturing.
    336212 Truck Trailer Manufacturing.
    336214 Travel Trailer and Camper Manufacturing.
    3363 Motor Vehicle Parts Manufacturing.
    3364 Aerospace Product and Parts Manufacturing.
    336411 Aircraft Manufacturing.
    336611 Ship Building and Repairing.
    336612 Boat Building.
    339112 Surgical and Medical Instrument Manufacturing.
    339113 Surgical Appliance and Supplies Manufacturing.
    339999 All Other Miscellaneous Manufacturing.
    423120 Motor Vehicle Supplies and New Parts Merchant Wholesalers.
    423450 Medical, Dental, and Hospital Equipment and Supplies Merchant Wholesalers.
    423610 Electrical Apparatus and Equipment, Wiring Supplies, and Related Equipment Merchant Wholesalers.
    423620 Household Appliances, Electric Housewares, and Consumer Electronics Merchant Wholesalers.
    423690 Other Electronic Parts and Equipment Merchant Wholesalers.
    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.
    423850 Service Establishment Equipment and Supplies Merchant Wholesalers.
    423860 Transportation Equipment and Supplies (except Motor Vehicle) Merchant Wholesalers.
    423990 Other Miscellaneous Durable Goods Merchant Wholesalers.
    424690 Other Chemical and Allied Products Merchant Wholesalers.
    424820 Wine and Distilled Alcoholic Beverage Merchant Wholesalers.
    441310 Automotive Parts and Accessories Stores.
    443141 Household Appliance Stores.
    444190 Other Building Material Dealers.
    445110 Supermarkets and Other Grocery (except Convenience) Stores.
    445131 Convenience Retailers.
    445298 All Other Specialty Food Retailers.
    446191 Food (Health) Supplement Stores.
    449210 Electronics and Appliance Retailers.
    452311 Warehouse Clubs and Supercenters.
    453998 All Other Miscellaneous Store Retailers (except Tobacco Stores).
    45711 Gasoline Stations With Convenience Stores.
    481111 Scheduled Passenger Air Transportation.
    488510 Freight Transportation Arrangement.
    493110 General Warehousing and Storage.
    531120 Lessors of Nonresidential Buildings (except Mini warehouses).
    541330 Engineering Services.
    541380 Testing Laboratories.
    541512 Computer Systems Design Services.
    541519 Other Computer Related Services.
    541620 Environmental Consulting Services.
    561210 Facilities Support Services.
    561910 Packaging and Labeling Services.
    561990 All Other Support Services.
    562111 Solid Waste Collection.
    562211 Hazardous Waste Treatment and Disposal.
    562920 Materials Recovery Facilities.
    621498 All Other Outpatient Care Centers.
    621999 All Other Miscellaneous Ambulatory Health Care Services.
    72111 Hotels (Except Casino Hotels) and Motels.
    72112 Casino Hotels.
    72241 Drinking Places (Alcoholic Beverages).
    722511 Full-service Restaurants.
    722513 Limited-service Restaurants.
    722514 Cafeterias, Grill Buffets, and Buffets.
    722515 Snack and Nonalcoholic Beverage Bars.
    81119 Other Automotive Repair and Maintenance.
    811219 Other Electronic and Precision Equipment Repair and Maintenance.
    811412 Appliance Repair and Maintenance.
    922160 Fire Protection.

    Table 2—Determination of Confidentiality Status for Data Elements Related to Reports on Chronically Leaking Appliances

    Description of data element Confidentiality status and rationale
    Identification information (owner or operator, facility name, facility address where appliance is located) No confidential treatment/Emission data.
    Appliance ID or description (for facilities with multiple appliances) No confidential treatment/Emission data.
    Refrigerant-containing appliance type (comfort cooling or other, IPR, or commercial refrigeration) No confidential treatment/Emission data.
    Refrigerant type No confidential treatment/Emission data.
    Full charge of appliance (pounds) No confidential treatment/Emission data.
    Annual percent refrigerant loss No confidential treatment/Emission data.
    Dates of refrigerant addition No confidential treatment/Emission data.
    Amounts of refrigerant added No confidential treatment/Emission data.
    Date of last successful follow-up verification test No confidential treatment/Emission data.
    Explanation of cause of refrigerant losses (Narrative) No confidential treatment/Emission data.
    Description of the repair actions taken (Narrative) No confidential treatment/Emission data.
    Whether a retrofit or retirement plan has been developed for the appliance, and, if so, the anticipated date of retrofit or retirement No confidential treatment/Emission data.
    EPA provides rationale of the confidentiality determination in the memorandum titled Confidentiality Determinations and Emission Data Designations for Data Elements in the Final Rule entitled “Phasedown of Hydrofluorocarbons: Management of Certain Hydrofluorocarbons and Substitutes under Subsection (h) of the American Innovation and Manufacturing Act of 2020”, which is available in the docket (EPA-HQ-OAR-2022-0606) of this rulemaking at https://www.regulations.gov.

    Table 3—Determination of Confidentiality Status for Data Elements Related to Other Leak Repair Notifications and Extension Requests

    Description of data element Confidentiality status and rationale
    Extension of time to complete repairs: Identification and address of the facility; the name of the owner or operator of the refrigerant-containing appliance; the leak rate; the method used to determine the leak rate and full charge; the date the refrigerant-containing appliance exceeded the applicable leak rate; the location of leak(s) to the extent determined to date; any repairs that have been performed thus far, including the date that repairs were completed; the reasons why more than 30 days (or 120 days if an industrial process shutdown is required) are needed to complete the repairs; and an estimate of when the repairs will be completed. If the estimated completion date is to be extended, a new estimated date of completion and documentation of the reason for that change must be submitted to EPA within 30 days of identifying that the completion date must be extended No confidential treatment/Emission data.
    Relief from the obligation to retrofit or retire a refrigerant-containing appliance: The date that the requirement to develop a retrofit or retirement plan was triggered; the leak rate; the method used to determine the leak rate and full charge; the location of the leak(s) identified in the leak inspection; a description of repair work that has been completed; a description of the repairs that have not been completed; a description of why repairs were not conducted within the applicable time frame; and a statement signed by an authorized company official that all identified leaks will be repaired and an estimate of when those repairs will be completed (not to exceed one year from date of the plan) No confidential treatment/Emission data.
    Extension of time to complete the retrofit or retirement of a refrigerant-containing appliance: Identification of the refrigerant-containing appliance; name of the owner or operator; the leak rate; the method used to determine the leak rate and full charge; the date the refrigerant-containing appliance exceeded the applicable leak rate; the location of leak(s) to the extent determined to date; any repairs that have been finished thus far, including the date that repairs were finished; a plan to finish the retrofit or retirement of the refrigerant-containing appliance; the reasons why more than one year is necessary to retrofit or retire the refrigerant-containing appliance; the date of notification to EPA; and an estimate of when retrofit or retirement work will be finished No confidential treatment/Emission data.
    Notification of exclusion of purged refrigerants that are destroyed from annual leak rate calculations: The identification of the facility and a contact person, including the address and telephone number; a description of the refrigerant-containing appliance, focusing on aspects relevant to the purging of refrigerant and subsequent destruction; a description of the methods used to determine the quantity of refrigerant sent for destruction and type of records that are being kept by the owners or operators where the appliance is located; the frequency of monitoring and data-recording; and a description of the control device, and its destruction efficiency No confidential treatment/Emission data.
    EPA provides the rationale for the confidentiality determination in the memorandum titled Confidentiality Determinations and Emission Data Designations for Data Elements in the Final Rule entitled “Phasedown of Hydrofluorocarbons: Management of Certain Hydrofluorocarbons and Substitutes under Subsection (h) of the American Innovation and Manufacturing Act of 2020 ”, which is available in the docket (EPA-HQ-OAR-2022-0606) of this rulemaking at https://www.regulations.gov.

    Table 4—Determination of Confidentiality Status for Data Elements Related to Reports on Fire Suppression

    Description of data element Confidentiality status and rationale
    Identification information (owner name, facility name, facility address where equipment is located) No confidential treatment/Emission data.
    For each regulated substance, quantity of material (the combined mass of regulated substance and contaminants) sold for the purpose of installation of new fire suppression equipment and servicing and/or repair of existing fire suppression equipment No confidential treatment/Emission data.
    For each regulated substance, quantity of material (the combined mass of regulated substance and contaminants) in inventory onsite for the purpose of installation of new fire suppression equipment and servicing and/or repair of existing fire suppression equipment broken out by recovered, recycled, and virgin No confidential treatment/Emission data.
    Total mass of each regulated substance sold for the purpose of installation of new fire suppression equipment and servicing and/or repair of existing fire suppression equipment No confidential treatment/Emission data.
    Total mass of each regulated substance in inventory onsite for the purpose of installation of new fire suppression equipment and servicing and/or repair of existing fire suppression equipment broken out by recovered, recycled, and virgin No confidential treatment/Emission data.
    Total mass of waste products the reporting entity sent for disposal, along with information about the disposal facility if waste is not processed by the reporting entity No confidential treatment/Emission data.
    EPA provides rationale of the confidentiality determination in the memorandum titled Confidentiality Determinations and Emission Data Designations for Data Elements in the Final Rule entitled “Phasedown of Hydrofluorocarbons: Management of Certain Hydrofluorocarbons and Substitutes under Subsection (h) of the American Innovation and Manufacturing Act of 2020”, which is available in the docket (EPA-HQ-OAR-2022-0606) of this rulemaking at https://www.regulations.gov.

    Table 5—Summary of Undiscounted Annual Values, Present Values, and Equivalent Annualized Values Select Years for the 2026 Through 2050 Timeframe for Estimated Compliance Costs, Benefits, and Net Benefits for the ER&R Rule (Millions of 2022$, Discounted to 2024)—Base Case Scenario

    Year Climate benefits Costs Net benefits
    2026 $428 $92 $336
    2030 676 102 574
    2035 613 86 526
    2040 466 67 399
    2045 315 51 264
    2050 263 52 211
    Discount rate 3% 2% 3% 7% 2% 3% 7%
    Present value $8,356 $1,499 $1,335 $884 $6,857 $7,021 $7,471
    Equivalent annualized value (EAV) 480 77 77 76 403 403 404
    Benefits include only those related to climate. Climate benefits are based on changes (reductions) in HFC emissions and are calculated using four different estimates of the social cost of HFCs (SC-HFCs): model average at 2.5 percent, three percent, and five percent discount rates; 95th percentile at three percent discount rate. For presentational purposes of this table, the benefits associated with the average SC-HFC are shown at a three percent discount rate. More details can be found in the RIA addendum for the final rule.
    Rows may not appear to add correctly due to rounding.
    The annualized present value of costs and benefits are calculated as if they occur over a 25-year period.
    The present value (PV) for the net benefits column is found by taking the difference between the PV of climate benefits at three percent and the PV of costs discounted at seven percent, three percent or two percent. Because the SC-HFC estimates reflect net climate change damages in terms of reduced consumption (or monetary consumption equivalents), the use of the social rate of return on capital (seven percent under OMB Circular A-4 (2003)) to discount damages estimated in terms of reduced consumption would inappropriately underestimate the impacts of climate change for the purposes of estimating the SC-HFC.
    Costs represent compliance with the regulations and include potential savings from reducing refrigerant purchases. See the RIA addendum and the Economic Impact and Benefits TSD for additional information.
    Present value and EAV are for the years 2026 through 2050.
    Benefits presented in this table do not include potential savings from amended RCRA regulations, which are separate from the regulations under subsection (h)(1) of the AIM Act. See Table 6 below for an estimate of combined AIM Act and RCRA net benefits.

    Table 6—Summary of Present Value Costs, Benefits, and Net Benefits by Regulatory Provision (Millions of 2022$, Discounted to 2024)—Base Case Scenario

    Provision Climate benefits (3%) Costs (savings) (2%) Costs (savings) (3%) Costs (savings) (7%) Net benefits (3% benefits, 2% costs) Net benefits (3% benefits, 3% costs) Net benefits (3% benefits, 7% costs)
    Leak Repair And ALD $6,176 $1,285 $1,146 $760 $4,891 $5,031 $5,417.
    Fire Suppression 14 $15 $13 $7 ($1) $1 $7.
    Cylinder Management 2,165 ($195) ($169) ($101) $2,360 $2,335 $2,266.
    Use of Reclaimed HFCs for Servicing $43 $38 $23 ($43) ($38) ($23).
    Recordkeeping & Reporting $350 $308 $195 ($350) ($308) ($195).
    Total (AIM Act) 8,356 $1,499 $1,335 $884 $6,857 $7,021 $7,471.
    RCRA Alternative Standard Requirements $0 to ($40) $0 to ($35) $0 to ($22) $0 to $40 $0 to $35 $0 to $22.
    Total (AIM Act + RCRA) $1,459 to $1,499 $1,300 to $1,335 $863 to $884 $6,857 to $6,897 $7,021 to $7,056 $7,471 to $7,493.
    As detailed in the RIA addendum, reclaim requirements may lead to additional emissions reductions by inducing increased recovery of refrigerant at servicing and disposal that may otherwise be released or vented. In the base case scenario, EPA does not estimate an increase in these avoided emissions beyond baseline assumptions. See the RIA addendum for additional analysis related to this assumption.
    Rows may not appear to add correctly due to rounding.
    RCRA alternative standard requirements are part of the RCRA regulations, which are separate from the regulations under subsection (h)(1) of the AIM Act. Potential RCRA-related benefits presented in this table are included here for informational purposes.

    Table 10—Summary of Present Value Costs, Benefits, and Net Benefits by Regulatory Provision (Millions of 2022$, Discounted to 2024)—Base Case Scenario

    Provision Climate benefits (3%) Costs (savings) (2%) Costs (savings) (3%) Costs (savings) (7%) Net benefits (3% benefits, 2% costs) Net benefits (3% benefits, 3% costs) Net benefits (3% benefits, 7% costs)
    Leak Repair And ALD $6,176 $1,285 $1,146 $760 $4,891 $5,031 $5,417.
    Fire Suppression 14 $15 $13 $7 ($1) $1 $7.
    Cylinder Management 2,165 ($195) ($169) ($101) $2,360 $2,335 $2,266.
    Use of Reclaimed HFCs for Servicing $43 $38 $23 ($43) ($38) ($23).
    Recordkeeping & Reporting $350 $308 $195 ($350) ($308) ($195).
    Total (AIM Act) 8,356 $1,499 $1,335 $884 $6,857 $7,021 $7,471.
    RCRA Alternative Standard Requirements $0 to ($40) $0 to ($35) $0 to ($22) $0 to ($40) $0 to ($35) $0 to ($22).
    Total (AIM Act + RCRA) $1,459 to $1,499 $1,300 to $1,335 $863 to $884 $6,857 to $6,897 $7,021 to $7,056 $7,471 to $7,493.
    As detailed in the RIA addendum, reclaim requirements may lead to additional emissions reductions by inducing increased recovery of refrigerant at servicing and disposal that may otherwise be released or vented. In the base case scenario, EPA does not estimate an increase in these avoided emissions beyond baseline assumptions. See the RIA addendum for additional analysis related to this assumption.
    Rows may not appear to add correctly due to rounding.
    RCRA alternative standard requirements are part of the RCRA regulations, which are separate from the regulations under subsection (h)(1) of the AIM Act. Potential RCRA-related benefits presented in this table are included here for informational purposes.

    Table 1—Regulations Implementing the Hazardous and Solid Waste Amendments of 1984

    Promulgation date Title of regulation Federal Register reference Effective date
    *         *         *         *         *         *         *
    December 10, 2024 Standards for the Management of Ignitable Spent Refrigerants Recycled for Reuse [ Federal Register citation of the final rule] [Date of publication of the final rule in the Federal Register ].
    These regulations implement HSWA only to the extent that they apply to tank systems owned or operated by small quantity generators, establish leak detection requirements for all new underground tank systems, and establish permitting standards for underground tank systems that cannot be entered for inspection.
    These regulations, including test methods for benzo(k)fluoranthene and technical standards for drip pads, implement HSWA only to the extent that they apply to the listing of Hazardous Waste No. F032, and wastes that are hazardous because they exhibit the Toxicity Characteristic. These regulations, including test methods for benzo(k)fluoranthene and technical standards for drip pads, do not implement HSWA to the extent that they apply to the listings of Hazardous Waste Nos. F034 and F035.
    The following portions of this rule are not HSWA regulations: §§ 264.19 and 265.19 for final covers.
    The following portions of this rule are not HSWA regulations: §§ 260.30, 260.31, 261.2.
    These regulations implement HSWA only to the extent that they apply to the standards for staging piles and to §§ 264.1(j) and 264.101(d) of this chapter.

    Table 2—Self-Implementing Provisions of the Hazardous and Solid Waste Amendments of 1984

    Effective date Self-implementing provision RCRA citation Federal Register reference
    *         *         *         *         *         *         *
    December 10, 2024 Standards for the Management of Ignitable Spent Refrigerants Recycled for Reuse 3001(d)(4) 3004(n) [ Federal Register citation of the final rule].
    Note that the effective date was changed to Jan. 29, 1986 by the Nov. 29, 1985 rule.
    Note that the effective date was changed to Sept. 22, 1986 by the Mar. 24, 1986 rule.