# Potential Hydrofluorocarbon Phase Down: Issues for Congress

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URL: https://www.frixlaw.com/law-library/documents/crs%3AIF10904

## Record

- **Collection:** Congressional research report
- **Document type:** CRS In Focus
- **Published:** June 7, 2018
- **Citation:** IF10904

## Text

June 7, 2018

Potential Hydrofluorocarbon Phase Down: Issues for Congress
Potential Issues for Congress
Hydrofluorocarbons (HFCs), a potent set of greenhouse
gases (GHGs), are used in air conditioning, refrigeration,
foam blowing agents, insulation, and other applications.
While many nations are poised to phase down HFCs, U.S.
policies appear paused: Next steps in the executive branch
are unclear. Nonetheless, Congress may face several issues
related to possible phase down of HFCs both domestically
and internationally:

 The Senate may consider its advice and possible consent
to ratify a 2016 international treaty, the Kigali
Amendment, if the President submits it to the Senate.
Under the Kigali Amendment, Parties commit to
eventually phase out HFC production and consumption.

approved as replacements for more potent ODS, such as
chlorofluorocarbons (CFCs).
Although scientists believe HFCs would not significantly
deplete stratospheric ozone, they are GHGs, being efficient
absorbers of infrared radiation in the atmosphere. Their
potency, or Global Warming Potential, ranges from about
150 to 8,000 times more than the equivalent mass of carbon
dioxide (CO2), the principal human-related GHG. Once
emitted to the atmosphere, various HFCs persist there for
hundreds to thousands of years.
Figure 1. Estimated and Projected Emissions of ODS
and HFC Substitutes Without Kigali Amendment

 Industry and environmental groups seek, along with
U.S. ratification of the Kigali Amendment, clarification
of the U.S. Environmental Protection Agency’s (EPA)
authority to limit HFC use after a federal court in 2017
vacated part of an EPA rule.

 If the United States joins the Kigali Amendment,
Congress may consider appropriations of the U.S.
contribution, if any, to international “adequate
financing” of HFC reduction efforts by low-income
countries.

 Should the United States not join the Kigali
Amendment, whether adverse trade issues could emerge
under restrictions on trade with non-Parties.

 Should the United States seek to address the risks of
climate change by controlling GHG emissions, phasing
out HFCs—or not—could affect the distribution of
effort among emitting sectors and the economic costs
and benefits. HFC reductions can be achieved at very
low cost per ton compared to many other GHG
reduction options. Deciding not to abate HFC could
raise the costs, difficulty, and time required to avoid any
given level of climate change risk.
Several legislative proposals have been introduced in the
115th Congress, but none has seen committee action.

Emergence of HFCs as Pollutants
HFCs were first manufactured in the context of efforts,
described below, to reduce damage to the Earth’s
stratospheric ozone layer, which absorbs harmful incoming
solar radiation and also affects the Earth’s climate. HFCs
(and alternatives) replace ozone-depleting substances
(ODS), including hydrochlorofluorocarbons (HCFCs).
[Figure 1 illustrates how HFCs (red) replace HCFCs
(yellow) which replace CFCs (blue).] HCFC use began with
low levels in the 1970s and accelerated after they were

Source: Guus Velders, “Scenarios of ODSs and ODS Substitutes,”
Government of the Netherlands, presentation given May 2, 2011.
Notes: This 2011 analysis does not include control of HFC emissions
(red area), as would occur under the Kigali Amendment. Also,
depicting emissions of these gases by mass is not indicative of their
relative environmental impacts. “High” and “low” represent a range
of future emission projections.

From Protecting Stratospheric Ozone to
Phasing Down HFC
In the 1970s, scientists expected but had little evidence that
certain manufactured chemicals, including CFCs, would
damage the Earth’s protective stratospheric ozone layer.
Regulation began in 1978 with U.S. restrictions on CFCs in
aerosol sprays under EPA authority in the Toxic Substances
Control Act of 1976, as well as Food and Drug
Administration authority in the Federal Food, Drug, and
Cosmetic Act. The Clean Air Act Amendments (CAAA) of
1977 (P .L. 95-95) broadly authorized EPA to regulate any
activity that threatened the stratosphere and endangered
public health.
1985 Vienna Convention
In response to new scientific evidence in 1985 of the
springtime “ozone hole” over Antarctica, 20 nations,

https://crsreports.congress.gov

Potential Hydrofluorocarbon Phase Down: Issues for Congress

including the United States, agreed to the 1985 Vienna
Convention for the Protection of the Ozone Layer.

consume no more than 15%-20% of their respective
baselines.

1987 Montreal Protocol (MP)
Parties to the Vienna Convention adopted the subsidiary
MP in 1987 to set binding, quantitative schedules for
countries to phase out listed ODS. The MP provides for
international cooperation on safer substitutes for ODS,
research cooperation, financial assistance, and trade
restrictions with non-Parties. A series of amendments to the
MP set specific schedules for freezing, reducing, and
prohibiting production and consumption of CFCs, HCFCs,
and additional ODS. There are 197 Parties to the Vienna
Convention and the MP, including the United States.

The Kigali Amendment also provides for an unspecified
amount of “adequate financing,” through a Multilateral
Fund, to support HFC reductions in low-income countries
and for research and development of affordable alternatives.

CAAA of 1990
To provide EPA authority beyond that in Section 157 of the
CAAA of 1977, Congress enacted the CAAA of 1990 (P.L.
101-549), Title VI, to protect stratospheric ozone. Under
Title VI, EPA allocated production and consumption
tradable allowances for ODS equal to the amounts accepted
by the United States under the MP. EPA developed a
complementary comprehensive program, including ODS
production and import limits; requirements for labeling,
recovery and recycling; and equipment technician
certification. It established the Significant New Alternatives
Policy (SNAP) to approve safer substitutes.
In 1994, SNAP—in accordance with the 1993 U.S. Climate
Change Action Plan—first listed HFCs as acceptable
substitutes for ODS in certain uses. At that time, EPA
concluded that the CAAA mandate to evaluate substitutes
based on reducing overall risk to human health and the
environment authorized impact on climate as a permissible
SNAP evaluation criterion.
In 2015, EPA concluded that other ODS substitutes posed
lower overall risks to the environment than did HFCs and
so listed HFCs as unacceptable in specified uses. EPA set
timetables to phase down HFC uses and listed some
acceptable alternatives. A federal court in 2017, in
Mexichem Fluor, Inc. v. EPA, took a narrower view,
vacating part of the 2015 EPA rule. EPA has not provided a
response to that ruling.
The Kigali Amendment to the MP
In 2007, MP Parties agreed to accelerate a phaseout of
HCFCs. Studies projected strong growth of HFCs as
replacements (Figure 1), particularly in developing
countries. A 2009 study projected that uncontrolled HFC
emissions could globally add as much climate forcing in
2050 as 9%-19% of business-as-usual CO2 emissions.
Consequently, in 2016, nearly 200 nations—including the
United States—agreed to the Kigali Agreement to the MP.
It contains commitments eventually to phase out HFC
production and consumption globally.
Developed countries are to begin to phase down HFCs by
2019. Most low-income countries freeze HFC consumption
levels in 2024, while certain low-income countries freeze
consumption in 2028. By the late 2040s, Parties agreed to

One widely cited estimate suggested that the Kigali
Amendment HFC phase-down schedule could avoid as
much as 0.5o Celsius of global warming by 2100.

Alternatives to HFCs
There are several means to reduce HFC production and
consumption. These include conserving and recycling
HFCs, substituting other substances (e.g., ammonia or CO2)
that are less potent GHG than HFCs, and modifying the
technologies that use HFCs, including energy efficiency.

Costs, Trade, and the Ratification
Question
Many industry and environmental groups support U.S.
ratification of the Kigali Amendment and EPA regulation to
assure compliance with it. Without those, certain U.S.
companies’ abilities to access international markets with
U.S.-developed ODS substitutes could be adversely
affected by the treaty’s trade restrictions. The costs are
expected to be low and some measures could yield net cost
savings, particularly through energy efficiency. Some
industry representatives urge careful monitoring of the
availability of substitutes. Experts expect the unit costs to
fall over time with technological advance and expansion of
the global market. Studies also concluded that delaying a
phasedown could significantly increase costs by increasing
the investment in equipment that would need to be replaced
once conversions to HFC-free technologies begin.
The Kigali Amendment is expected to enter into force on
January 1, 2019, having been ratified, accepted, or
approved by 37 nations. The United States signed the Kigali
Amendment in 2016. To become a Party, the United States
must ratify the treaty with the advice and consent of the
Senate. The Trump Administration has not submitted it to
the Senate and has not indicated its intentions. Some argue
that any treaty infringes on U.S. sovereignty or may be
wary of environmental treaties or regulation in particular.

For more information
CRS Legal Sidebar WSLG1868, D.C. Circuit Rejects
EPA’s Efforts to Ban Hydrofluorocarbons: Part 1, by Linda
Tsang
CRS Legal Sidebar WSLG1869, D.C. Circuit Rejects
EPA’s Efforts to Ban Hydrofluorocarbons: Part 2, by Linda
Tsang
Jane A. Leggett, Specialist in Energy and Environmental
Policy

https://crsreports.congress.gov

IF10904

Potential Hydrofluorocarbon Phase Down: Issues for Congress

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https://crsreports.congress.gov | IF10904 · VERSION 2 · NEW

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Source: Frix Law Library, https://www.frixlaw.com/law-library/documents/crs%3AIF10904. Public record. Not legal advice.
