Protection of Stratospheric Ozone: Determination 37 for Significant New Alternatives Policy Program, 3037-3045 [2022-00998]
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Federal Register / Vol. 87, No. 13 / Thursday, January 20, 2022 / Rules and Regulations
This safety zone will prohibit entry into
certain navigable waters in the path of
these launches near Cape Canaveral, FL.
It is categorically excluded from further
review under paragraph L60(a) of
Appendix A, Table 1 of DHS Instruction
Manual 023–01–001–01, Rev. 1. A
Record of Environmental Consideration
supporting this determination is
available in the docket. For instructions
on locating the docket, see the
ADDRESSES section of this preamble.
G. Protest Activities
The Coast Guard respects the First
Amendment rights of protesters.
Protesters are asked to call or email the
person listed in the FOR FURTHER
INFORMATION CONTACT section to
coordinate protest activities so that your
message can be received without
jeopardizing the safety or security of
people, places or vessels.
List of Subjects in 33 CFR Part 165
Harbors, Marine safety, Navigation
(water), Reporting and recordkeeping
requirements, Security measures,
Waterways.
For the reasons discussed in the
preamble, the Coast Guard amends 33
CFR part 165 as follows:
designated by or assisting the Captain of
the Port Jacksonville (COTP) in the
enforcement of the safety zone.
(c) Regulations. (1) Under the general
safety zone regulations in subpart C of
this part, you may not enter the safety
zone described in paragraph (a) of this
section unless authorized by the COTP
or the COTP’s designated representative.
(2) To seek permission to enter, transit
through, anchor in, or remain within the
safety zone contact the COTP
Jacksonville by telephone at (904) 714–
7557 or the COTP’s representative via
VHF–FM radio on channel 16. Those in
the safety zone must comply with all
lawful orders or directions given to
them by the COTP or the COTP’s
designated representative.
(d) Enforcement period. This section
will be enforced from January 13, 2022,
through January 31, 2022, during times
when a Broadcast Notice to Mariners
informs mariners that space vehicles are
being launched in a direction resulting
in a southerly or polar orbit trajectory.
Dated: January 12, 2022.
J.D. Rose,
Commander, U.S. Coast Guard,Acting,
Captain of the Port.
[FR Doc. 2022–01004 Filed 1–19–22; 8:45 am]
BILLING CODE 9110–04–P
ENVIRONMENTAL PROTECTION
AGENCY
1. The authority citation for part 165
continues to read as follows:
lotter on DSK11XQN23PROD with RULES1
Authority: 46 U.S.C. 70034, 70051; 33 CFR
1.05–1, 6.04–1, 6.04–6, and 160.5;
Department of Homeland Security Delegation
No. 00170.1, Revision No. 01.2.
40 CFR Part 82
■
2. Add § 165.T07–0450 to read as
follows:
RIN 2060–AG12
§ 165.T07–0450 Safety Zone; Atlantic
Ocean, Cape Canaveral, FL.
Protection of Stratospheric Ozone:
Determination 37 for Significant New
Alternatives Policy Program
(a) Location. The following area is a
safety zone: All waters of the Atlantic
Ocean, from surface to bottom,
encompassed by a line connecting the
following points beginning at Point 1:
28°36′51.88″ N 80°35′57.33″ W, thence
to Point 2: 28°34′0.00″ 80°25′0.00″ W,
thence to Point 3: 28°14′0.00″
80°13′0.00″ W, thence to Point 4:
28°12′0.00″ N 80°23′0.00″ W, thence to
Point 5: 28°16′0.00″ N, 80°26′00.00″ W,
thence to point 6: 28°26′31.81″ N,
80°33′8.02″ W. These coordinates are
based on WGS 84.
(b) Definitions. As used in this
section, designated representative
means a Coast Guard Patrol
Commander, including a Coast Guard
coxswain, petty officer, or other officer
operating a Coast Guard vessel, and U.S.
Air Force range safety personnel, and a
Federal, State, and local officer
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All electronic documents in the docket
are listed in the index at
www.regulations.gov. Although listed in
the index, some information is not
publicly available, i.e., Confidential
Business Information (CBI) or other
information whose disclosure is
restricted by statute. Publicly available
docket materials are available either
electronically at www.regulations.gov or
in hard copy at the EPA Air Docket
(Nos. A–91–42 and EPA–HQ–OAR–
2003–0118), EPA Docket Center (EPA/
DC), William J. Clinton West, Room
3334, 1301 Constitution Avenue NW,
Washington, DC 20460. The telephone
number for the Public Reading Room is
(202) 566–1744, and the telephone
number for the Air Docket is (202) 566–
1742. Out of an abundance of caution
for members of the public and our staff,
the EPA Docket Center and Reading
Room are closed to public visitors, with
limited exceptions, to reduce the risk of
transmitting COVID–19. Our Docket
Center staff will continue to provide
remote customer service via email,
phone, and webform. For further
information on EPA Docket Center
services and the current status, please
visit us online at https://www.epa.gov/
dockets.
FOR FURTHER INFORMATION CONTACT:
PART 165—REGULATED NAVIGATION
AREAS AND LIMITED ACCESS AREAS
■
3037
[EPA–HQ–OAR–2003–0118; FRL–9445–01–
OAR]
Environmental Protection
Agency (EPA).
ACTION: Determination of acceptability.
AGENCY:
This determination of
acceptability expands the list of
acceptable substitutes pursuant to the
U.S. Environmental Protection Agency’s
Significant New Alternatives Policy
program. This action lists as acceptable
additional substitutes for use in the
refrigeration and air conditioning; foam
blowing; aerosols; cleaning solvents;
and adhesives, coatings, and inks
sectors.
SUMMARY:
This determination is applicable
on January 20, 2022.
ADDRESSES: EPA established a docket
for this action under Docket ID No.
EPA–HQ–OAR–2003–0118
(continuation of Air Docket A–91–42).
DATES:
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Gerald Wozniak by telephone at (202)
343–9624, by email at Wozniak.gerald@
epa.gov, or by mail at U.S.
Environmental Protection Agency, Mail
Code 6205T, 1200 Pennsylvania Avenue
NW, Washington, DC 20460. Overnight
or courier deliveries should be sent to
the office location at 1201 Constitution
Avenue NW, Washington, DC 20004.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Listing of New Acceptable Substitutes
A. Refrigeration and Air Conditioning
B. Foam Blowing
C. Aerosols
D. Cleaning Solvents
E. Adhesives, Coatings, and Inks
Appendix A: Summary of Decisions for New
Acceptable Substitutes
I. Listing of New Acceptable Substitutes
This action is listing as acceptable
additional substitutes for use in the
refrigeration and air conditioning; foam
blowing; aerosols; cleaning solvents;
and adhesives, coatings and inks
sectors. This action presents EPA’s most
recent decision under the Significant
New Alternatives Policy (SNAP)
program to list as acceptable several
substitutes in different end-uses. New
substitutes are:
• Hydrochlorofluoroolefin (HCFO)–
1233zd(E) in cold storage warehouses,
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ice skating rinks and industrial process
air conditioning (new equipment only);
• Blends of 10 to 90 percent
hydrofluoroolefin (HFO)–1234ze(E) by
weight and the remainder HCFO–
1233zd(E) in polystyrene: Extruded
boardstock and billet (XPS);
• Blends of 10 to 90 percent HFO–
1234ze(E) by weight and the remainder
hydrofluorocarbon (HFC)–152a in XPS;
• Blends of zero to 100 percent HFO–
1234ze(E), zero to 70 percent methyl
formate, zero to 60 percent HFC–152a,
zero to 60 percent carbon dioxide (CO2),
and zero to 60 percent water in XPS;
and
• HCFO–1233yd(Z) in electronics
cleaning, metals cleaning, precision
cleaning, aerosol solvents, and coatings.
EPA’s review of certain substitutes
listed in this document is pending for
other end-uses. Listing decisions in the
end-uses in this document do not
prejudge EPA’s listings of these
substitutes for other end-uses. While
certain substitutes being added through
this action to the acceptable lists for
specific end-uses may have a higher risk
in one or more SNAP criteria than
certain other substitutes already listed
as acceptable or acceptable subject to
restrictions, they have a similar or lower
overall risk than other acceptable
substitutes in those end-uses.
For additional information on SNAP,
visit the SNAP portion of EPA’s Ozone
Layer Protection website at:
www.epa.gov/snap. Copies of the full
lists of acceptable substitutes for ozonedepleting substances (ODS) in the
industrial sectors covered by the SNAP
program are available at www.epa.gov/
snap/substitutes-sector. For more
information on the Agency’s process for
administering the SNAP program or
criteria for evaluation of substitutes,
refer to the initial SNAP rulemaking
published March 18, 1994 (59 FR
13044), and the regulations codified at
40 CFR part 82, subpart G. SNAP
decisions and the appropriate Federal
Register citations are found at:
www.epa.gov/snap/snap-regulations.
Substitutes listed as unacceptable;
acceptable, subject to narrowed use
limits; or acceptable, subject to use
conditions are also listed in the
appendices to 40 CFR part 82, subpart
G.
The sections below discuss each
substitute listing in detail. Appendix A
contains tables summarizing each listing
decision in this action. The statements
in the ‘‘Further Information’’ column in
the tables provide additional
information but these are not legally
binding under section 612 of the Clean
Air Act (CAA). Although you are not
required to follow recommendations in
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the ‘‘Further Information’’ column of the
table under section 612 of the CAA,
some of these statements may refer to
obligations that are enforceable or
binding under federal or state programs
other than the SNAP program. The
identification of other enforceable or
binding requirements should not be
construed as a comprehensive list of
such obligations. In many instances, the
information simply refers to standard
operating practices in existing industry
standards and/or building codes. When
using these substitutes in the identified
end-use, EPA strongly encourages you
to apply the information in the ‘‘Further
Information’’ column. Many of these
recommendations, if adopted, would
not require significant changes to
existing operating practices.
You can find submissions to EPA for
the substitutes listed in this document,
as well as other materials supporting the
decisions in this action, in Docket EPA–
HQ–OAR–2003–0118 at
www.regulations.gov.
A. Refrigeration and Air Conditioning
1. HCFO–1233zd(E)
EPA’s decision: EPA finds HCFO–
1233zd(E) acceptable as a substitute for
use in:
• Cold storage warehouses (new
equipment only)
• Ice skating rinks (new equipment
only)
• Industrial process air conditioning
(new equipment only)
HCFO–1233zd(E), marketed under the
trade name Solstice®zd, is also known
as trans-1-chloro-3,3,3-trifluoroprop-1ene (Chemical Abstracts Service
Registry Number [CAS Reg. No.]
102687–65–0).
You may find a copy of the
applicant’s submission, with CBI
redacted, providing the required health
and environmental information for this
substitute in this end-use in Docket
EPA–HQ–OAR–2003–0118 at
www.regulations.gov under the name,
‘‘Supporting Materials for Notice 37
Listing of HCFO–1233zd(E) in
Refrigeration and Air Conditioning.
SNAP Submission Received October 7,
2019.’’ EPA performed an assessment to
examine the health and environmental
risks of this substitute. These
assessments are available in Docket
EPA–HQ–OAR–2003–0118:
• ‘‘Risk Screen on Substitutes in Cold
Storage Warehouses and Industrial
Process Air Conditioning. Substitute:
HCFO–1233zd(E).’’
• ‘‘Risk Screen on Substitutes in Ice
Skating Rinks. Substitute: HCFO–
1233zd(E).’’
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EPA previously listed HCFO–
1233zd(E) as acceptable for use in
several refrigeration and air
conditioning and foam blowing enduses (December 11, 2020, 85 FR 79863;
August 10, 2012, 77 FR 47768; October
21, 2014, 79 FR 62863).
Environmental information: HCFO–
1233zd(E) has an ozone depletion
potential (ODP) of less than 0.0004 and
a global warming potential (GWP) of
3.7.1 HCFO–1233zd(E) is excluded from
the definition of volatile organic
compounds (VOC) under CAA
regulations (see 40 CFR 51.100(s))
addressing the development of state
implementation plans (SIPs) to attain
and maintain the National Ambient Air
Quality Standards (NAAQS). Knowingly
venting or releasing this refrigerant
blend is limited by the venting
prohibition under section 608(c)(2) of
the CAA, codified in EPA’s regulations
at 40 CFR 82.154(a).
Flammability information: HCFO–
1233zd(E) is not flammable.
Toxicity and exposure data: Potential
health effects of exposure to this
substitute include drowsiness or
dizziness. The substitute may also
irritate the skin or eyes or cause
frostbite. The substitute could cause
asphyxiation if air is displaced by
vapors in a confined space. These
potential health effects are common to
many refrigerants.
The Workplace Environmental
Exposure Limit (WEEL) Committee of
the Occupational Alliance for Risk
Science (OARS) has established a WEEL
of 800 ppm on an eight-hour timeweighted average (8-hr TWA) for
HCFO–1233zd(E). EPA anticipates that
users will be able to meet the WEEL and
address potential health risks by
following requirements and
recommendations in the manufacturer’s
safety data sheet (SDS), American
Society of Heating, Refrigerating, and
Air-Conditioning Engineers (ASHRAE)
Standard 15, and other safety
precautions common to the refrigeration
and air conditioning industry.
Comparison to other substitutes in
these end-uses: HCFO–1233zd(E) has an
ODP of less than 0.0004, comparable to
or less than other listed substitutes in
these end-uses with ODPs ranging from
zero to 0.098.
For cold storage warehouses, HCFO–
1233zd(E)’s GWP of about 3.7 is
comparable to or lower than that of
1 WMO (World Meteorological Organization),
Scientific Assessment of Ozone Depletion: 2018,
Global Ozone Research and Monitoring Project—
Report No. 58, 588 pp., Geneva, Switzerland, 2018.
Available at: https://ozone.unep.org/sites/default/
files/2019-05/SAP-2018-Assessment-report.pdf. In
this action, the 100-year GWP values are used.
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other acceptable substitutes for new
equipment such as ammonia absorption,
CO2, R-450A, R-513A, and R-407C, with
GWPs 2 ranging from zero to 1,770.
For ice skating rinks and industrial
process air conditioning, HCFO–
1233zd(E)’s GWP of about 3.7 is
comparable to or lower than that of
other acceptable substitutes for new
equipment such as ammonia absorption,
CO2, R-450A, R-513A, and R-507A, with
GWPs ranging from zero to 3,990.
Flammability and toxicity risks are
comparable to or lower than
flammability and toxicity risks of other
available substitutes in the same enduses. Toxicity risks can be minimized
by use consistent with the OARS WEEL,
ASHRAE 15, and other industry
standards, recommendations in the
manufacturer’s SDS, and other safety
precautions common in the refrigeration
and air conditioning industry.
EPA finds HCFO–1233zd(E)
acceptable in the cold storage
warehouses (new equipment only), ice
skating rinks (new equipment only) and
industrial process air conditioning (new
equipment only) end-uses because it
does not pose greater overall
environmental and human health risk
than other available substitutes in the
same end-uses.
B. Foam Blowing
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1. Blends of 10 to 90 Percent HFO–
1234ze(E) by Weight and the Remainder
HCFO–1233zd(E)
EPA’s decision: EPA finds blends of
10 to 90 percent HFO–1234ze(E) by
weight and the remainder HCFO–
1233zd(E) acceptable as a substitute for
use as a blowing agent in:
• Polystyrene: Extruded boardstock and
billet
These blends range in composition
from 10 percent HFO–1234ze(E) and 90
percent HCFO–1233zd(E) to 90 percent
HFO–1234ze(E) and 10 percent HCFO–
1233zd(E). Accordingly, these blends
are referred to as blends of 10 to 90
percent by weight HFO–1234ze(E) and
the remainder HCFO–1233zd(E), or
2 Unless otherwise stated, all GWPs in this
document for individual chemicals are 100-year
values from: IPCC, 2007: Climate Change 2007: The
Physical Science Basis. Contribution of Working
Group I to the Fourth Assessment Report of the
Intergovernmental Panel on Climate Change
[Solomon, S., Qin, D., Manning, M., Chen, Z.,
Marquis, M., Averyt, K.B., Tignor M., and Miller,
H.L. (eds.)]. Cambridge University Press,
Cambridge, United Kingdom and New York, NY,
USA. This document is accessible at www.ipcc.ch/
publications_and_data/ar4/wg1/en/contents.html.
For blends of chemicals, such as R-507A, this
document weights the GWPs of each component of
the blend by their mass percentage in the blend,
based upon the 100-year GWPs in IPCC, 2007, if
available in that document.
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16:03 Jan 19, 2022
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hereafter in this action as ‘‘HFO–
1234ze(E)/HCFO–1233zd(E) co-blowing
blends’’; they also go by the trade name
of Solstice® XBA–1. HFO–1234ze(E) is
also called 1,3,3,3-tetrafluoropropene
(E), or trans-1,3,3,3-tetrafluoropropene
(CAS Reg. No. 29118–24–9). HCFO–
1233zd(E) is also called trans-1-chloro3,3,3-trifluoro-prop-1-ene (CAS Reg. No.
102687–65–0).
You may find a copy of the
applicant’s submission, with CBI
redacted, providing the required health
and environmental information for this
substitute in this end-use in Docket
EPA–HQ–OAR–2003–0118 at
www.regulations.gov under the name,
‘‘Supporting Materials for Notice 37
Listing Blends of 10 to 90 Percent HFO–
1234ze(E) by Weight and the Remainder
HCFO–1233zd(E) as a Foam Blowing
Agent. SNAP Submission Received
November 4, 2019.’’ EPA has performed
an assessment to examine the health
and environmental risks of this
substitute. This assessment is available
in docket EPA–HQ–OAR–2003–0118
under the name ‘‘Risk Screen on
Substitutes in Extruded Polystyrene
Boardstock and Billet Foam Substitute:
Blends of 10 to 90 Percent HFO–
1234ze(E) by Weight and the Remainder
HCFO–1233zd(E) (Solstice® XBA–1).’’
Environmental information: HFO–
1234ze(E) has an ODP of zero and
HCFO–1233zd(E) has an ODP of less
than 0.0004.3 If these values are
weighted by mass percentage, then these
HFO–1234ze(E)/HCFO–1233zd(E) coblowing blends have an ODP ranging
from less than 0.0004 to less than
0.00004. Their components, HFO–
1234ze(E) and HCFO–1233zd(E), have
GWPs of less than one 4 and 3.7,
respectively. If these values are
weighted by mass percentage, then the
blends range in GWP from about 1.3 to
about 3.4. Both components of the
blends are excluded from the definition
of VOC under CAA regulations (see 40
CFR 51.100(s)) addressing the
development of SIPs to attain and
maintain the NAAQS.
Flammability information: The
component HCFO–1233zd(E) is nonflammable. HFO–1234ze(E) is not
flammable at standard temperature and
pressure using the standard test method
American Society for Testing and
Materials (ASTM) E681. However, at
higher temperatures, such as the
3 WMO
(World Meteorological Organization),
Scientific Assessment of Ozone Depletion: 2018,
Global Ozone Research and Monitoring Project—
Report No. 58, 588 pp., Geneva, Switzerland, 2018.
Available at: https://ozone.unep.org/sites/default/
files/2019-05/SAP-2018-Assessment-report.pdf.
(WMO, 2018)
4 WMO, 2018.
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3039
temperatures typical for extruding XPS,
HFO–1234ze(E) may also be flammable,
particularly at higher humidity levels.5
Toxicity and exposure data: Potential
health effects of these substitutes at
lower concentrations include
drowsiness and dizziness. Potential
health effects also include skin or eye
irritation or frostbite. The components
of HFO–1234ze(E)/HCFO–1233zd(E) coblowing blends can cause symptoms of
asphyxiation when present at
sufficiently high concentrations.
Excessive inhalation of the substitute
may also result in an irregular heartbeat,
due to cardiac effects. These potential
health effects are common to many foam
blowing agents.
The American Industrial Hygiene
Association (AIHA) has established a
WEEL of 800 ppm as an 8-hr TWA for
HFO–1234ze(E), and OARS’s WEEL
committee has established a WEEL of
800 ppm for HCFO–1233zd(E). EPA
anticipates that users will be able to
meet the AIHA and OARS WEELs and
address potential health risks by
following requirements and
recommendations in the manufacturer’s
SDSs and other safety precautions
common to the foam blowing industry.
Comparison to other substitutes in
this end-use: These HFO–1234ze(E)/
HCFO–1233zd(E) co-blowing blends
have an ODP ranging from less than
0.0004 to less than 0.00004, comparable
to all other acceptable substitutes in this
end-use, such as blends of 10 to 99
percent by weight HFO–1336mzz(Z) and
the remainder HFC–152a (hereafter in
this action ‘‘HFO–1336mzz(Z)/HFC–
152a blends’’), HFO–1234ze(E), methyl
formate, and CO2. These HFO–
1234ze(E)/HCFO–1233zd(E) blends’
GWPs from about 1.3 to 3.4 are lower
than or comparable to those of other
acceptable substitutes in the same enduse for which we are finding it
acceptable, such as HFO–1336mzz(Z)/
HFC–152a blends, HFO–1234ze(E), light
saturated hydrocarbons C3–C6 6 and
methyl formate, with respective GWPs
5 Bellair and Hood, 2019. Comprehensive
evaluation of the flammability and ignitability of
HFO–1234ze, R.J. Bellair and L. Hood, Process
Safety and Environmental Protection 132 (2019)
273–284. Available online at doi.org/10.1016/
j.psep.2019.09.033.
6 That is, alkanes with three to six carbons such
as butane, n-pentane, isopentane, and cyclopentane.
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Federal Register / Vol. 87, No. 13 / Thursday, January 20, 2022 / Rules and Regulations
of approximately three to 110,7 124,
one,8 less than one,9 and 11.10
Flammability and toxicity risks are
comparable to or lower than
flammability and toxicity risks of other
available substitutes in the same enduse. Some acceptable substitutes in this
end-use are flammable, like HFC–152a,
light saturated hydrocarbons C3–C6,
and methyl formate, while others are
non-flammable. Toxicity risks can be
minimized by use consistent with the
AIHA’s and OARS’s WEELs,
recommendations in the SDS, and other
safety precautions common in the foam
blowing industry.
EPA finds blends of 10 to 90 percent
by weight HFO–1234ze(E) and the
remainder HCFO–1233zd(E) acceptable
in the XPS end-use because they do not
pose greater overall environmental and
human health risk than other available
substitutes in the same end-use.
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2. Blends of 10 to 90 Percent HFO–
1234ze(E) by Weight and the Remainder
HFC–152a
EPA’s decision: EPA finds blends of
10 to 90 percent HFO–1234ze(E) by
weight and the remainder HFC–152a
acceptable as a substitute for use as a
blowing agent in:
• Polystyrene: Extruded boardstock and
billet
These blends range in composition
from 10 percent HFO–1234ze(E) and 90
percent HFC–152a to 90 percent HFO–
1234ze(E) and 10 percent HFC–152a.
Accordingly, these blends are also
referred to as blends of 10 to 90 percent
by weight HFO–1234ze(E) and the
remainder HFC–152a, or hereafter in
this action as ‘‘HFO–1234ze(E)/HFC–
152a co-blowing blends’’; they also go
by the trade name of Solstice® XBA–2.
HFO–1234ze(E) is also called 1,3,3,3tetrafluoropropene (E), or trans-1,3,3,3tetrafluoropropene (CAS Reg. No.
29118–24–9). HFC–152a is also called
1,1-difluoroethane (CAS Reg. No. 75–
37–6).
You may find a copy of the
applicant’s submission, with CBI
redacted, providing the required health
and environmental information for this
substitute in this end-use in Docket
EPA–HQ–OAR–2003–0118 at
7 HFO–1336mzz(Z) and HFC–152a have GWPs of
about two (WMO, 2018) and 124 (IPCC, 2007),
respectively. If these values are weighted by mass
percentage, then the blends range in GWP from
about three to about 110.
8 WMO (World Meteorological Organization),
Scientific Assessment of Ozone Depletion: 2018,
Global Ozone Research and Monitoring Project—
Report No. 58, 588 pp., Geneva, Switzerland, 2018.
Available at: https://ozone.unep.org/sites/default/
files/2019-05/SAP-2018-Assessment-report.pdf.
9 Ibid.
10 Ibid.
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16:03 Jan 19, 2022
Jkt 256001
www.regulations.gov under the name,
‘‘Supporting Materials for Notice 37
Listing Blends of 10 to 90 Percent HFO–
1234ze(E) by Weight and the Remainder
HFC–152a as a Foam Blowing Agent.
SNAP Submission Received November
4, 2019.’’ EPA has performed an
assessment to examine the health and
environmental risks of this substitute.
This assessment is available in docket
EPA–HQ–OAR–2003–0118 under the
name ‘‘Risk Screen on Substitutes in
Extruded Polystyrene Boardstock and
Billet Foam Substitute: Blends of 10 to
90 Percent HFO–1234ze(E) by Weight
and the Remainder HFC–152a (Solstice®
XBA–2).’’
Environmental information: These
HFO–1234ze(E)/HFC–152a co-blowing
blends and their components have an
ODP of zero. Their components, HFO–
1234ze(E) and HFC–152a, have GWPs of
less than one 11 and 124, respectively. If
these values are weighted by mass
percentage, then the blends range in
GWP from about 13 to about 112. Both
components of the blends are excluded
from the definition of VOC under CAA
regulations (see 40 CFR 51.100(s))
addressing the development of SIPs to
attain and maintain the NAAQS.
Flammability information: The
component HFC–152a is flammable
while the component HFO–1234ze(E) is
not flammable at standard temperature
and pressure using the standard test
method ASTM E681. However, at higher
temperatures, such as the temperatures
typical for extruding XPS, HFO–
1234ze(E) may also be flammable,
particularly at higher humidity levels.12
Toxicity and exposure data: Potential
health effects of these substitutes at
lower concentrations include
drowsiness and dizziness. Potential
health effects also include skin or eye
irritation or frostbite. The components
of HFO–1234ze(E)/HFC–152a blends
can cause symptoms of asphyxiation
when present at sufficiently high
concentrations. Excessive inhalation of
the substitute may also result in an
irregular heartbeat, due to cardiac
effects. These potential health effects are
common to many foam blowing agents.
The AIHA has established WEELs of
1,000 ppm for HFC–152a, and of 800
ppm for HFO–1234ze(E), both as an 811 WMO
(World Meteorological Organization),
Scientific Assessment of Ozone Depletion: 2018,
Global Ozone Research and Monitoring Project—
Report No. 58, 588 pp., Geneva, Switzerland, 2018.
Available at: https://ozone.unep.org/sites/default/
files/2019-05/SAP-2018-Assessment-report.pdf.
12 Bellair and Hood, 2019. Comprehensive
evaluation of the flammability and ignitability of
HFO–1234ze, R.J. Bellair and L. Hood, Process
Safety and Environmental Protection 132 (2019)
273–284. Available online at doi.org/10.1016/
j.psep.2019.09.033.
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Sfmt 4700
hr TWA. EPA anticipates that users will
be able to meet the AIHA WEELs and
address potential health risks by
following requirements and
recommendations in the manufacturer’s
SDSs and other safety precautions
common to the foam blowing industry.
Comparison to other substitutes in
this end-use: These HFO–1234ze(E)/
HFC–152a co-blowing blends have an
ODP of zero, comparable to all other
acceptable substitutes in this end-use,
such as HFO–1336mzz(Z)/HFC–152a
blends, HFC–152a, HFO–1234ze(E),
methyl formate, and CO2. These HFO–
1234ze(E)/HFC–152a co-blowing blends’
GWPs from about 13 to 112 are lower
than or comparable to those of other
acceptable substitutes in the same enduse for which we are finding them
acceptable, such as HFO–1336mzz(Z)/
HFC–152a blends and HFC–152a with
respective GWPs of approximately three
to 110 13 and 124. The GWPs of the
HFO–1234ze(E)/HFC–152a co-blowing
blends of about 13 to 112 are higher
than those for acceptable alternatives
such as HFO–1234ze(E), light saturated
hydrocarbons C3–C6 and methyl
formate, with respective GWPs of one,14
less than one,15 and 11.16 Based on
current information, EPA anticipates
that HFO–1234ze(E), light saturated
hydrocarbons C3–C6 and methyl
formate are not currently being used as
the sole blowing agent by any U.S.
manufacturers in this end-use because
the individual chemicals have
drawbacks such as insufficient vapor
pressure, insufficient solubility in the
polystyrene matrix, or high permeability
resulting in low thermal resistance (‘‘Rvalue’’); blends such as these HFO–
1234ze(E)/HFC–152a co-blowing blends
are expected to result in a feasible
balance of blowing agent properties for
adequate or better performance.
Flammability and toxicity risks are
comparable to or lower than
flammability and toxicity risks of other
available substitutes in the same enduse. Some acceptable substitutes in this
end-use are flammable, like HFC–152a,
light saturated hydrocarbons C3–C6,
and methyl formate, while others are
non-flammable. Toxicity risks can be
minimized by use consistent with the
13 HFO–1336mzz(Z) and HFC–152a have GWPs of
about two (WMO, 2018) and 124 (IPCC, 2007),
respectively. If these values are weighted by mass
percentage, then the blends range in GWP from
about three to about 110.
14 WMO (World Meteorological Organization),
Scientific Assessment of Ozone Depletion: 2018,
Global Ozone Research and Monitoring Project—
Report No. 58, 588 pp., Geneva, Switzerland, 2018.
Available at: https://ozone.unep.org/sites/default/
files/2019-05/SAP-2018-Assessment-report.pdf.
15 Ibid.
16 Ibid.
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AIHA’s WEELs, recommendations in the
SDS, and other safety precautions
common in the foam blowing industry.
EPA finds blends of 10 to 90 percent
by weight HFO–1234ze(E) and the
remainder HFC–152a acceptable in the
XPS end-use because they do not pose
greater overall environmental and
human health risk than other available
substitutes in the same end-use.
lotter on DSK11XQN23PROD with RULES1
3. Blends of Zero to 100 Percent HFO–
1234ze(E), Zero to 70 Percent Methyl
Formate, Zero to 60 Percent HFC–152a,
Zero to 60 Percent CO2 and Zero to 60
Percent Water
EPA’s decision: EPA finds blends of
zero to 100 percent HFO–1234ze(E),
zero to 70 percent methyl formate, zero
to 60 percent HFC–152a, zero to 60
percent CO2 and zero to 60 percent
water acceptable as a substitute for use
as a blowing agent in:
• Polystyrene: Extruded boardstock and
billet
These blends are hereafter referred to
as ‘‘HFO–1234ze(E)/methyl formate/
HFC–152a/CO2/water co-blowing
blends.’’ The components of the blends
are co-blown and component
percentages are by weight.
HFO–1234ze(E) is also known as
HFC–1234ze, HFO–1234ze or trans1,3,3,3-tetrafluoroprop-1-ene (CAS Reg.
No. 29118–24–9). Methyl formate is also
known as methyl methanoate or formic
acid, methyl ester (CAS Reg. No. 107–
31–3). HFC–152a, also known as 1,1difluoroethane, has CAS Reg. No. 75–
37–6. CO2 has CAS Reg. No. 124–38–9,
and water has CAS Reg. No. 7732–18–
5.
You may find a copy of the
applicant’s submission, with CBI
redacted, providing the required health
and environmental information for this
substitute in this end-use in Docket
EPA–HQ–OAR–2003–0118 at
www.regulations.gov under the name,
‘‘Supporting Materials for Notice 37
Listing Blends of 0–100% HFO–
1234ze(E), 0–70% Methyl Formate, 0–
60% HFC–152a, 0–60% CO2 and 0–60%
Water as a Foam Blowing Agent. SNAP
Submission Received January 26, 2021.’’
EPA has performed an assessment to
examine the health and environmental
risks of this substitute. This assessment
is available in docket EPA–HQ–OAR–
2003–0118 under the name ‘‘Risk
Screen on Substitutes in Extruded
Polystyrene Boardstock and Billet Foam
Substitute: HFO–1234ze(E)/Methyl
Formate/HFC–152a/CO2/Water Coblowing Blends for Extruded
Polystyrene Foam Insulation (HFO–
1234ze(E)/Methyl Formate/HFC–152a/
CO2/Water Co-blowing Blends).’’
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Environmental information: The
blends have an ODP of zero. Their
components, HFO–1234ze(E), methyl
formate, HFC–152a, CO2, and water have
GWPs of one,17 11,18 124,19 one,20 and
less than one,21 respectively. If these
values are weighted by mass percentage,
then the blends could have a GWP
ranging from one to 80. HFO–1234ze(E),
methyl formate, HFC–152a, CO2, and
water—components of the blends—are
excluded from EPA’s regulatory
definition of VOC under CAA
regulations that address the
development of SIPs to attain and
maintain the NAAQS. See 40 CFR
51.100(s).
Flammability information: The
components HFC–152a and methyl
formate are flammable while the other
components of the blends are nonflammable at standard temperature and
pressure using the standard test method
ASTM E681. However, at higher
temperatures, such as the temperatures
typical for extruding XPS, HFO–
1234ze(E) may also be flammable,
particularly at higher humidity levels.22
Toxicity and exposure data: Potential
health effects of these substitutes at
lower concentrations include headache,
nausea, drowsiness, and dizziness. The
substitutes may also irritate the skin or
eyes or cause frostbite. Excessive
inhalation of the substitutes may also
result in an irregular heartbeat, due to
cardiac effects. At sufficiently high
concentrations, they may cause central
nervous system depression and affect
respiration. The substitutes could cause
asphyxiation if air is displaced by
vapors in a confined space. These health
effects are common to many foam
blowing agents.
The AIHA has established WEELs of
1,000 ppm as an eight-hour timeweighted average for HFC–152a and 800
ppm for HFO–1234ze(E). Methyl
formate has an Occupational Safety and
17 WMO (World Meteorological Organization),
Scientific Assessment of Ozone Depletion: 2018,
Global Ozone Research and Monitoring Project—
Report No. 58, 588 pp., Geneva, Switzerland, 2018.
Available at: https://ozone.unep.org/sites/default/
files/2019-05/SAP-2018-Assessment-report.pdf. In
this action, the 100-year GWP values are used.
18 WMO, 2018.
19 IPCC, 2007.
20 IPCC, 2007.
21 Sherwood et al. 2018. This paper estimated that
water vapor emitted near Earth’s surface due to
anthropogenic sources (e.g., irrigation) would have
a GWP of ¥10¥3 to 5 × 10¥4. ‘‘The global warming
potential of near-surface emitted water vapour,’’
Steven C. Sherwood, Vishal Dixit and Chryse´is
Salomez. Environ. Res. Lett. 13 (2018) 104006.
22 Bellair and Hood, 2019. Comprehensive
evaluation of the flammability and ignitability of
HFO–1234ze, R.J. Bellair and L. Hood, Process
Safety and Environmental Protection 132 (2019)
273–284. Available online at doi.org/10.1016/
j.psep.2019.09.033.
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Sfmt 4700
3041
Health Administration (OSHA)
permissible exposure limits (PEL) of 100
ppm on an 8-hr TWA. CO2 has an OSHA
PEL of 5,000 ppm on an 8-hr TWA, and
a 15-minute recommended short-term
exposure limit (STEL) of 30,000 ppm
established by the National Institute for
Occupational Safety and Health
(NIOSH). EPA anticipates that users will
be able to meet the AIHA WEELs, OSHA
PELs, and NIOSH STEL and address
potential health risks by following
requirements and recommendations in
the manufacturer’s SDSs and other
safety precautions common to the foam
blowing industry.
Comparison to other substitutes in
this end-use: HFO–1234ze(E)/methyl
formate/HFC–152a/CO2/water coblowing blends have ODPs of zero,
comparable to all other acceptable
substitutes in this end-use, such as
HFO–1336mzz(Z)/HFC–152a blends,
HFC–152a, HFO–1234ze(E), methyl
formate, and CO2.
The GWPs of the HFO–1234ze(E)/
methyl formate/HFC–152a/CO2/water
co-blowing blends, ranging from
approximately one to 80, are lower than
HFC–152a’s GWP of 124 and are
comparable to or lower than those for
HFO–1336mzz(Z)/HFC–152a blends
(three to 110 23). The worst-case GWPs
of the HFO–1234ze(E)/methyl formate/
HFC–152a/CO2/water co-blowing blends
are higher than those for acceptable
alternatives such as HFO–1234ze(E),
light saturated hydrocarbons C3–C6 and
methyl formate, with respective GWPs
of less than one,24 less than one,25 and
11,26 while the GWP at the low end of
the range of approximately one is
comparable to those acceptable
alternatives. Based on current
information, EPA anticipates that HFO–
1234ze(E), light saturated hydrocarbons
C3–C6 and methyl formate are not
currently being used as the sole blowing
agent by any U.S. manufacturers in this
end-use because the individual
chemicals have drawbacks such as
insufficient vapor pressure, insufficient
solubility in the polystyrene matrix, or
high permeability resulting in low
thermal resistance (‘‘R-value’’); blends
such as these HFO–1234ze(E)/methyl
formate/HFC–152a/CO2/water coblowing blends are expected to result in
a feasible balance of blowing agent
23 HFO–1336mzz(Z) and HFC–152a have GWPs of
about two (WMO, 2018) and 124 (IPCC, 2007),
respectively. If these values are weighted by mass
percentage, then the blends range in GWP from
about three to about 110.
24 WMO, 2018.
25 WMO, 2018.
26 WMO, 2018.
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properties for adequate or better
performance.
Flammability and toxicity risks of the
HFO–1234ze(E)/methyl formate/HFC–
152a/CO2/water co-blowing blends are
comparable to or lower than
flammability and toxicity risks of other
available substitutes in the same enduse. Some acceptable substitutes in this
end-use are flammable, like HFC–152a,
light saturated hydrocarbons C3–C6,
and methyl formate, while others are
non-flammable. Toxicity risks can be
minimized by use consistent with the
AIHA WEELs, OSHA PELs, NIOSH
STEL, recommendations in the
manufacturer’s SDSs, and other safety
precautions common in the foamblowing industry.
EPA finds HFO–1234ze(E)/methyl
formate/HFC–152a/CO2/water coblowing blends acceptable in the XPS
end-use because they do not pose
greater overall environmental and
human health risk than other available
substitutes in the same end-use.
lotter on DSK11XQN23PROD with RULES1
C. Aerosols
1. HCFO–1233yd(Z)
EPA’s decision: EPA finds HCFO–
1233yd(Z) acceptable as a substitute for
use in:
• Aerosol solvents
HCFO–1233yd(Z) is also known as
(Z)-1-Chloro-2,3,3-trifluoropropene
(CAS Reg. No. 1263679–68–0).
You may find a copy of the
applicant’s submission, with CBI
redacted, providing the required health
and environmental information for this
substitute in this end-use in Docket
EPA–HQ–OAR–2003–0118 at
www.regulations.gov under the name,
‘‘Supporting Materials for Notice 37
Listing of HCFO–1233yd(Z) in Cleaning
Solvents, Aerosol Solvents, and
Coatings. SNAP Submission Received
March 12, 2019.’’ EPA performed an
assessment to examine the health and
environmental risks of this substitute.
This assessment is available in Docket
EPA–HQ–OAR–2003–0118:
• ‘‘Risk Screen on Substitutes in
Aerosol Solvents. Substitute: HCFO–
1233yd(Z).’’
Environmental information: HCFO–
1233yd(Z) has an ODP of 0.00003 and
a GWP of less than 1.27 Under CAA
regulations (see 40 CFR 51.100(s))
defining VOC for the purpose of
addressing the development of SIPs to
attain and maintain the NAAQS, HCFO–
27 Kazuaki Tokuhashi, Tadafumi Uchimaru, Kenji
Takizawa, and Shigeo Kondo, 2018. Rate Constants
for the Reactions of OH Radical with the (E)/(Z)
Isomers of CF3CF=CHCl and CHF2CF=CHCl (J.Phys.
Chem. A 2018, 122, 3120–3127) (Tokuhashi et al.,
2018).
VerDate Sep<11>2014
16:03 Jan 19, 2022
Jkt 256001
1233yd(Z) would be considered a VOC.
That definition provides that ‘‘any
compound of carbon’’ which
‘‘participates in atmospheric
photochemical reactions’’ is considered
a VOC unless expressly excluded in that
provision based on a determination of
‘‘negligible photochemical reactivity.’’
The manufacturer has petitioned EPA to
exclude HCFO–1233yd(Z) from the
definition of VOC under those
regulations. EPA has not yet taken
action on that petition. This substitute
is subject to a Toxic Substance Control
Act (TSCA) section 5(a)(2) Significant
New Use Rule (SNUR).
Flammability information: HCFO–
1233yd(Z) is not flammable.
Toxicity and exposure data: Potential
health effects of exposure to this
substitute include drowsiness or
dizziness. The substitute may also
irritate the skin or eyes. The substitute
could cause asphyxiation if air is
displaced by vapors in a confined space.
These potential health effects are
common to many aerosol solvents.
The manufacturer recommends an
acceptable exposure limit (AEL) for the
workplace of 250 ppm on an 8-hr TWA
for HCFO–1233yd(Z). EPA anticipates
that users will be able to meet the
manufacturer’s AEL and address
potential health risks by following
requirements and recommendations in
the manufacturer’s SDS, and other
safety precautions common to the
aerosol industry.
Comparison to other substitutes in
this end-use: HCFO–1233yd(Z) has an
ODP of less than 0.00003, comparable to
or less than other listed substitutes in
this end-use with ODPs ranging from
zero to 0.033.
HCFO–1233yd(Z)’s GWP of less than
one is lower than that of other
acceptable substitutes such as HFE–
7200, HFE–347mcc3, HFC–365mfc and
HFC–4310mee with GWPs ranging from
59 to 1,640. HCFO–1233yd(Z)’s GWP is
lower than or comparable to the GWPs
of other acceptable substitutes for
aerosol solvents, including acetone,
methoxytridecafluoroheptene isomers
(MPHE), and trans-1-chloro-3,3,3trifluoroprop-1-ene with GWPs ranging
from less than one to seven.
Some acceptable substitutes in this
end-use are VOC, like HCFO–1233yd(Z),
while others are excluded from the
definition of VOC.
Flammability and toxicity risks are
comparable to or lower than
flammability and toxicity risks of other
available substitutes in the same enduse. Toxicity risks can be minimized by
use consistent with the manufacturer’s
AEL, industry standards,
recommendations in the manufacturer’s
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Fmt 4700
Sfmt 4700
SDS, and other safety precautions
common in the aerosol industry.
EPA finds HCFO–1233yd(Z)
acceptable in the aerosol solvent enduse because it does not pose greater
overall environmental and human
health risk than other available
substitutes in the same end-use.
D. Cleaning Solvents
1. HCFO–1233yd(Z)
EPA’s decision: EPA finds HCFO–
1233yd(Z) acceptable as a substitute for
use in:
• Electronics cleaning
• Metals cleaning
• Precision cleaning
HCFO–1233yd(Z) is also known as
(Z)-1-chloro-2,3,3-trifluoropropene (CAS
Reg. No. 1263679–68–0).
You may find a copy of the
applicant’s submission, with CBI
redacted, providing the required health
and environmental information for this
substitute in this end-use in Docket
EPA–HQ–OAR–2003–0118 at
www.regulations.gov under the name,
‘‘Supporting Materials for Notice 37
Listing of HCFO–1233yd(Z) in Cleaning
Solvents, Aerosol Solvents, and
Coatings. SNAP Submission Received
March 12, 2019.’’ EPA performed an
assessment to examine the health and
environmental risks of this substitute.
This assessment is available in Docket
EPA–HQ–OAR–2003–0118:
• ‘‘Risk Screen on Substitutes in
Electronics Cleaning, Metals Cleaning,
and Precision Cleaning. Substitute:
HCFO–1233yd(Z).’’
Environmental information: The
environmental information for this
substitute is set forth in the
‘‘Environmental information’’ section in
listing in I.C.1. above.
Flammability information: HCFO–
1233yd(Z) is not flammable.
Toxicity and exposure data: The
toxicity information for this substitute is
set forth in the ‘‘Toxicity and exposure
data’’ section in listing I.C.1. above.
Comparison to other substitutes in
these end-uses: HCFO–1233yd(Z) has an
ODP of less than 0.00003, comparable to
or less than other listed substitutes in
the metals cleaning, electronics
cleaning, and precision cleaning enduses with ODPs ranging from zero to
0.033.
HCFO–1233yd(Z)’s GWP of less than
1 is lower than that of other acceptable
substitutes such as HFE–7200, HFE–
7100, HFC–365mfc and HFC–4310mee
with GWPs ranging from 59 to 1,640.
HCFO–1233yd(Z)’s GWP is lower than
or comparable to the GWPs of other
acceptable substitutes for cleaning
solvents, including acetone, MPHE, and
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trans-1-chloro-3,3,3-trifluoroprop-1-ene
with GWPs ranging from less than one
to seven.
Some acceptable substitutes in these
end-uses are VOC, like HCFO–
1233yd(Z), while others are excluded
from the definition of VOC.
Flammability and toxicity risks are
comparable to or lower than
flammability and toxicity risks of other
available substitutes in the same enduse. Toxicity risks can be minimized by
use consistent with the manufacturer’s
AEL, recommendations in the
manufacturer’s SDS, and other safety
precautions common in the cleaning
solvents industry.
EPA finds HCFO–1233yd(Z)
acceptable in the end-uses listed above
because it does not pose greater overall
environmental and human health risk
than other available substitutes in the
same end-uses.
E. Adhesives, Coatings, and Inks
1. HCFO–1233yd(Z)
EPA’s decision: EPA finds HCFO–
1233yd(Z) acceptable as a substitute for
use as a carrier solvent in:
• Coatings
HCFO–1233yd(Z) is also known as
(Z)-1-chloro-2,3,3-trifluoropropene (CAS
Reg. No. 1263679–68–0).
You may find a copy of the
applicant’s submission, with CBI
redacted, providing the required health
and environmental information for this
substitute in this end-use in Docket
EPA–HQ–OAR–2003–0118 at
www.regulations.gov under the name,
‘‘Supporting Materials for Notice 37
Listing of HCFO–1233yd(Z) in Cleaning
Solvents, Aerosol Solvents, and
Coatings. SNAP Submission Received
March 12, 2019.’’ EPA performed an
assessment to examine the health and
environmental risks of this substitute.
This assessment is available in Docket
EPA–HQ–OAR–2003–0118:
• ‘‘Risk Screen on Substitutes in
Coatings. Substitute: HCFO–1233yd(Z).’’
Environmental information: The
environmental information for this
substitute is set forth in the
‘‘Environmental information’’ section in
listing I.C.1., above.
Flammability information: HCFO–
1233yd(Z) is not flammable.
Toxicity and exposure data: The
toxicity information for this substitute is
set forth in the ‘‘Toxicity and exposure
data’’ section in listing I.C.1., above.
Comparison to other substitutes in
these end-uses: HCFO–1233yd(Z) has an
ODP of less than 0.00003, comparable to
or less than other listed substitutes in
this end-use with ODPs ranging from
zero to 0.00034.
For coatings, HCFO–1233yd(Z)’s GWP
of less than one is lower than that of
other acceptable substitutes such as
HFE–7200 and HFE–7100 with GWPs
ranging from 59 to 297. HCFO–
1233yd(Z)’s GWP is lower than or
3043
comparable to the GWPs of other
acceptable substitutes for coatings,
including acetone, MPHE, and trans-1chloro-3,3,3-trifluoroprop-1-ene with
GWPs ranging from less than one to
seven. Some acceptable substitutes in
this end-use are VOC, like HCFO–
1233yd(Z), while others are excluded
from the definition of VOC.
Flammability and toxicity risks are
comparable to or lower than
flammability and toxicity risks of other
available substitutes in the same enduse. Toxicity risks can be minimized by
use consistent with the manufacturer’s
AEL, recommendations in the
manufacturer’s SDS, and other safety
precautions common in the coatings
industry.
EPA finds HCFO–1233yd(Z)
acceptable in the coatings end-use
because it does not pose greater overall
environmental and human health risk
than other available substitutes in the
same end-use.
List of Subjects in 40 CFR Part 82
Environmental protection,
Administrative practice and procedure,
Air pollution control, Reporting and
recordkeeping requirements.
Hans Christopher Grundler,
Director, Office of Atmospheric Programs.
Appendix A: Summary of Decisions for
New Acceptable Substitutes
REFRIGERATION AND AIR CONDITIONING
Substitute
Decision
Further information 1
Cold Storage Warehouses (new equipment only).
HCFO–1233zd(E) .......
Acceptable ............
Ice Skating Rinks (new
equipment only).
HCFO–1233zd(E) .......
Acceptable ............
Industrial Process Air
Conditioning (new
equipment only).
HCFO–1233zd(E) .......
Acceptable ............
HCFO–1233zd(E) is also known as trans-1-chloro-3,3,3-trifluoroprop-1-ene (Chemical Abstracts Service Registry Number [CAS Reg. No.] 102687–65–0).
HCFO–1233zd(E) has an ozone depletion potential (ODP) of less than 0.0004 and a 100year integrated global warming potential (GWP) of about 3.7.
HCFO–1233zd(E) is nonflammable.
The Workplace Environmental Exposure Limits (WEEL) committee of the Occupational Alliance for Risk Science (OARS) has established a WEEL of 800 ppm as an eight-hour
time-weighted average (8-hr TWA) for HCFO–1233zd(E).
HCFO–1233zd(E) is also known as trans-1-chloro-3,3,3-trifluoroprop-1-ene (CAS Reg. No.
102687–65–0).
HCFO–1233zd(E) has an ODP of less than 0.0004 and a GWP of about 3.7.
HCFO–1233zd(E) is nonflammable.
OARS has established a WEEL of 800 ppm on an 8-hr TWA for HCFO–1233zd(E).
HCFO–1233zd(E) is also known as trans-1-chloro-3,3,3-trifluoroprop-1-ene (CAS Reg. No.
102687–65–0).
HCFO–1233zd(E) has an ODP of less than 0.0004 and a GWP of about 3.7.
HCFO–1233zd(E) is nonflammable.
OARS has established a WEEL of 800 ppm on an 8-hr TWA for HCFO–1233zd(E).
End-use
1 See
recommendations in the manufacturer’s SDS and guidance for all listed refrigerants.
lotter on DSK11XQN23PROD with RULES1
FOAM BLOWING AGENTS
End-use
Substitute
Decision
Further information 1
Extruded Polystyrene:
Boardstock and Billet.
Blends of 10 to 90
percent HFO–
1234ze(E) by weight
and the remainder
HCFO–1233zd(E).
Acceptable ............
This substitute is blends of 10 to 90 percent HFO–1234ze(E) by weight and the remainder
HCFO–1233zd(E). HFO–1234ze(E) is also called 1,3,3,3-tetrafluoropropene(E), or trans1,3,3,3-tetrafluoropropene (Chemical Abstracts Service Registry Number [CAS Reg. No.]
29118–24–9). HCFO–1233zd(E) is also called trans-1-chloro-3,3,3-trifluoro-prop-1-ene
(CAS Reg. No. 102687–65–0).
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FOAM BLOWING AGENTS—Continued
End-use
Substitute
Further information 1
Decision
Extruded Polystyrene:
Boardstock and Billet.
Blends of 10 to 90
percent HFO–
1234ze(E) by weight
and the remainder
HFC–152a.
Acceptable ............
Extruded Polystyrene:
Boardstock and Billet.
Blends of 0–100%
HFO–1234ze(E), 0–
70% Methyl Formate, 0–60% HFC–
152a, 0–60% CO2
and 0–60% Water.
Acceptable ............
1 See
HFO–1234ze(E) has a 100-year integrated global warming potential (GWP) of less than
one.
HCFO–1233zd(E) has an ozone depletion potential (ODP) of less than 0.0004 and a GWP
of 3.7. The blends have an ODP ranging from less than 0.0004 to less than 0.00004 and
range in GWP from about 1.3 to about 3.4.
HFO–1234ze(E) is not flammable at standard temperature and pressure, however, however, at higher temperatures, such as the temperatures typical for extruding extruded polystyrene: boardstock and billet (XPS), HFO–1234ze(E) may be flammable, particularly at
higher humidity levels. HCFO–1233zd(E) is non-flammable.
The American Industrial Hygiene Association (AIHA) has established a Workplace Environmental Exposure Limit (WEEL) of 800 ppm as an eight-hour time-weighted average (8-hr
TWA) for HFO–1234ze(E), and the Occupational Alliance for Risk Sciences (OARS) has
established a WEEL of 800 ppm as an 8-hr TWA for HCFO–1233zd(E).
This substitute is blends of 10 to 90 Percent HFO–1234ze(E) by weight and the remainder
HFC–152a. HFO–1234ze(E) is also called 1,3,3,3-tetrafluoropropene (E), or trans-1,3,3,3tetrafluoropropene (CAS Reg. No. 29118–24–9). HFC–152a is also called 1,1difluoroethane (CAS Reg. No. 75–37–6).
The blend and its components have an ODP of zero. HFO–1234ze(E) has a GWP of less
than one and HFC–152a has a GWP of 124. The blends range in GWP from about 13 to
about 112.
HFO–1234ze(E) is not flammable at standard temperature and pressure, however, at higher temperatures, such as the temperatures typical for extruding XPS, HFO–1234ze(E)
may be flammable, particularly at higher humidity levels. HFC–152a is flammable at
standard temperature and pressure.
The AIHA has established a WEEL of 1,000 ppm for HFC–152a and a WEEL of 800 ppm
for HFO–1234ze(E), both as an 8-hr TWA.
This substitute is blends of 0–100% HFO–1234ze(E), 0–70% methyl formate, 0–60% HFC–
152a, 0–60% CO2 and 0–60% water. HFO–1234ze(E) is also called 1,3,3,3tetrafluoropropene (E), or trans-1,3,3,3-tetrafluoropropene (CAS Reg. No. 29118–24–9).
Methyl formate is also called methyl methanoate or formic acid, methyl ester (CAS Reg.
No. 107–31–3). HFC–152a is also called 1,1-difluoroethane, has CAS Reg. No. 75–37–6.
CO2 has CAS Reg. No. 124–38–9, and water has CAS Reg. No. 7732–18–5.
HFO–1234ze(E) and water have GWPs of less than one, CO2 has a GWP of one, methyl
formate has a GWP of 11, and HFC–152a has a GWP of 124. The blends range in GWP
from approximately one to 80.
HFO–1234ze(E) is not flammable at standard temperature and pressure; however, at higher temperatures, such as the temperatures typical for extruding XPS, HFO–1234ze(E)
may be flammable, particularly at higher humidity levels. HFC–152a and methyl formate
are flammable at standard temperature and pressure.
The AIHA has established a WEEL of 1,000 ppm for HFC–152a and a WEEL of 800 ppm
for HFO–1234ze(E), both as an 8-hr TWA.
recommendations in the manufacturer’s SDS and guidance for all listed foam blowing agents.
CLEANING SOLVENTS
End-use
Substitute
Decision
Further information 1
Electronics cleaning,
metals cleaning, precision cleaning.
HCFO–1233yd(Z) .......
Acceptable ............
HCFO–1233yd(Z) is also known as (Z)-1-chloro-2,3,3-trifluoropropene (CAS Reg. No.
1263679–68–0).
HCFO–1233yd(Z) has an ozone depletion potential (ODP) of 0.00003 and a global warming
potential (GWP) of less than 1.
This compound is nonflammable.
The manufacturer recommends an acceptable exposure limit (AEL) for the workplace for
HCFO–1233yd(Z) of 250 ppm on an eight-hour time-weighted average (8-hr TWA).
This substitute is subject to a Toxic Substances Control Act (TSCA) section 5(a)(2) Significant New Use Rule (SNUR).
1 See
recommendations in the manufacturer’s SDS and guidance for all listed cleaning solvents.
lotter on DSK11XQN23PROD with RULES1
AEROSOLS
End-use
Substitute
Decision
Further information 1
Aerosol solvents ............
HCFO–1233yd(Z) .......
Acceptable ............
HCFO–1233yd(Z) is also known as (Z)-1-chloro-2,3,3-trifluoropropene (CAS Reg. No.
1263679–68–0).
HCFO–1233yd(Z) has an ozone depleting potential (ODP) of 0.00003 and a global warming
potential (GWP) of less than 1.
This compound is nonflammable.
The manufacturer recommends an acceptable exposure limit (AEL) for the workplace for
HCFO–1233yd(Z) of 250 ppm on an eight-hour time-weighted average (8-hr TWA).
This substitute is subject to a Toxic Substances Control Act (TSCA) section 5(a)(2) Significant New Use Rule (SNUR).
1
See recommendations in the manufacturer’s SDS and guidance for all listed aerosols.
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ADHESIVES, COATINGS, AND INKS
End-use
Substitute
Decision
Further information 1
Coatings ........................
HCFO–1233yd(Z) .......
Acceptable ............
HCFO–1233yd(Z) is also known as (Z)-1-chloro-2,3,3-trifluoropropene (CAS Reg. No.
1263679–68–0).
HCFO–1233yd(Z) has an ozone depleting potential (ODP) of 0.00003 and a global warming
potential (GWP) of less than 1.
This compound is nonflammable.
The manufacturer recommends an acceptable exposure limit (AEL) for the workplace for
HCFO–1233yd(Z) of 250 ppm on an eight-hour time-weighted average (8-hr TWA).
This substitute is subject to a Toxic Substance Control Act (TSCA) section 5(a)(2) Significant New Use Rule (SNUR).
1 See
recommendations in the manufacturer’s SDS and guidance for all listed carrier solvents for adhesives, coatings, and inks.
[FR Doc. 2022–00998 Filed 1–19–22; 8:45 am]
BILLING CODE 6560–50–P
FEDERAL COMMUNICATIONS
COMMISSION
47 CFR Part 73
[MB Docket No. 21–126; RM–11893; DA 22–
25; FR ID 67334]
Television Broadcasting Services
Monroe, Louisiana
Federal Communications
Commission.
ACTION: Final rule.
AGENCY:
On September 22, 2021, the
Media Bureau, Video Division (Bureau)
issued a Notice of Proposed Rulemaking
(NPRM) in response to a petition for
rulemaking filed by Gray Television
Licensee, LLC (Petitioner), the licensee
of KNOE–TV, channel 8, Monroe,
Louisiana, requesting the substitution of
channel 24 for channel 8 at Monroe in
the Table of Allotments. For the reasons
set forth in the Report and Order
referenced below, the Bureau amends
FCC regulations to substitute channel 24
for channel 8 at Monroe.
DATES: Effective January 20, 2022.
FOR FURTHER INFORMATION CONTACT:
Joyce Bernstein, Media Bureau, at (202)
418–1647 or Joyce.Bernstein@fcc.gov.
SUPPLEMENTARY INFORMATION: The
proposed rule was published at 86 FR
54417 on October 1, 2021. The
Petitioner filed comments in support of
the petition reaffirming its commitment
to apply for channel 24. The Petitioner
states that the Commission has
recognized the deleterious effects of
manmade noise from nearby electrical
devices including on the reception of
digital VHF signals and that the
propagation characteristics of VHF
channels allow undesired signals and
noise to be receivable at relatively
farther distances compared to UHF
channels. In addition, no existing
viewers will lose service and an
additional 12,868 persons would gain
lotter on DSK11XQN23PROD with RULES1
SUMMARY:
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service if the channel substitution is
granted.
This is a synopsis of the
Commission’s Report and Order, MB
Docket No. 21–126; RM–11893; DA 22–
25, adopted January 11, 2022, and
released January 11, 2022. The full text
of this document is available for
download at https://www.fcc.gov/edocs.
To request materials in accessible
formats for people with disabilities
(braille, large print, electronic files,
audio format), send an email to fcc504@
fcc.gov or call the Consumer &
Governmental Affairs Bureau at 202–
418–0530 (voice), 202–418–0432 (tty).
This document does not contain
information collection requirements
subject to the Paperwork Reduction Act
of 1995, Public Law 104–13. In addition,
therefore, it does not contain any
proposed information collection burden
‘‘for small business concerns with fewer
than 25 employees,’’ pursuant to the
Small Business Paperwork Relief Act of
2002, Public Law 107–198, see 44 U.S.C.
3506(c)(4). Provisions of the Regulatory
Flexibility Act of 1980, 5 U.S.C. 601–
612, do not apply to this proceeding.
The Commission will send a copy of
this Report and Order in a report to be
sent to Congress and the Government
Accountability Office pursuant to the
Congressional Review Act, see 5 U.S.C.
801(a)(1)(A).
■
List of Subjects in 47 CFR Part 73
Television.
Pacific Island Fisheries; Annual Catch
Limit and Accountability Measures;
Main Hawaiian Islands Deep 7
Bottomfish for Fishing Years 2021–
2024
Federal Communications Commission.
Thomas Horan,
Chief of Staff, Media Bureau.
Final Rule
For the reasons discussed in the
preamble, the Federal Communications
Commission amends 47 CFR part 73 as
follows:
PART 73—RADIO BROADCAST
SERVICE
1. The authority citation for part 73
continues to read as follows:
■
Authority: 47 U.S.C. 154, 155, 301, 303,
307, 309, 310, 334, 336, 339.
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2. In § 73.622(j), amend the Table of
Allotments, under Louisiana, by
revising the entry for Monroe to read as
follows:
§ 73.622 Digital television table of
allotments.
*
*
*
(j) * * *
*
*
Community
*
*
Channel No.
*
*
*
*
*
* 13, 24
*
*
LOUISIANA
*
*
*
Monroe ..................................
*
*
*
[FR Doc. 2022–01001 Filed 1–19–22; 8:45 am]
BILLING CODE 6712–01–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 665
[Docket No. 220113–0014]
RIN 0648- BK72
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
In this final rule, NMFS
implements an annual catch limit (ACL)
of 492,000 lb (223,167 kg) for Deep 7
bottomfish in the main Hawaiian
Islands (MHI) for each of the three
fishing years 2021–22, 2022–23, and
2023–24. As an in-season accountability
measure (AM), if NMFS projects that the
SUMMARY:
E:\FR\FM\20JAR1.SGM
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Agencies
[Federal Register Volume 87, Number 13 (Thursday, January 20, 2022)]
[Rules and Regulations]
[Pages 3037-3045]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2022-00998]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 82
[EPA-HQ-OAR-2003-0118; FRL-9445-01-OAR]
RIN 2060-AG12
Protection of Stratospheric Ozone: Determination 37 for
Significant New Alternatives Policy Program
AGENCY: Environmental Protection Agency (EPA).
ACTION: Determination of acceptability.
-----------------------------------------------------------------------
SUMMARY: This determination of acceptability expands the list of
acceptable substitutes pursuant to the U.S. Environmental Protection
Agency's Significant New Alternatives Policy program. This action lists
as acceptable additional substitutes for use in the refrigeration and
air conditioning; foam blowing; aerosols; cleaning solvents; and
adhesives, coatings, and inks sectors.
DATES: This determination is applicable on January 20, 2022.
ADDRESSES: EPA established a docket for this action under Docket ID No.
EPA-HQ-OAR-2003-0118 (continuation of Air Docket A-91-42). All
electronic documents in the docket are listed in the index at
www.regulations.gov. Although listed in the index, some information is
not publicly available, i.e., Confidential Business Information (CBI)
or other information whose disclosure is restricted by statute.
Publicly available docket materials are available either electronically
at www.regulations.gov or in hard copy at the EPA Air Docket (Nos. A-
91-42 and EPA-HQ-OAR-2003-0118), EPA Docket Center (EPA/DC), William J.
Clinton West, Room 3334, 1301 Constitution Avenue NW, Washington, DC
20460. The telephone number for the Public Reading Room is (202) 566-
1744, and the telephone number for the Air Docket is (202) 566-1742.
Out of an abundance of caution for members of the public and our staff,
the EPA Docket Center and Reading Room are closed to public visitors,
with limited exceptions, to reduce the risk of transmitting COVID-19.
Our Docket Center staff will continue to provide remote customer
service via email, phone, and webform. For further information on EPA
Docket Center services and the current status, please visit us online
at https://www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT: Gerald Wozniak by telephone at (202)
343-9624, by email at [email protected], or by mail at U.S.
Environmental Protection Agency, Mail Code 6205T, 1200 Pennsylvania
Avenue NW, Washington, DC 20460. Overnight or courier deliveries should
be sent to the office location at 1201 Constitution Avenue NW,
Washington, DC 20004.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Listing of New Acceptable Substitutes
A. Refrigeration and Air Conditioning
B. Foam Blowing
C. Aerosols
D. Cleaning Solvents
E. Adhesives, Coatings, and Inks
Appendix A: Summary of Decisions for New Acceptable Substitutes
I. Listing of New Acceptable Substitutes
This action is listing as acceptable additional substitutes for use
in the refrigeration and air conditioning; foam blowing; aerosols;
cleaning solvents; and adhesives, coatings and inks sectors. This
action presents EPA's most recent decision under the Significant New
Alternatives Policy (SNAP) program to list as acceptable several
substitutes in different end-uses. New substitutes are:
Hydrochlorofluoroolefin (HCFO)-1233zd(E) in cold storage
warehouses,
[[Page 3038]]
ice skating rinks and industrial process air conditioning (new
equipment only);
Blends of 10 to 90 percent hydrofluoroolefin (HFO)-
1234ze(E) by weight and the remainder HCFO-1233zd(E) in polystyrene:
Extruded boardstock and billet (XPS);
Blends of 10 to 90 percent HFO-1234ze(E) by weight and the
remainder hydrofluorocarbon (HFC)-152a in XPS;
Blends of zero to 100 percent HFO-1234ze(E), zero to 70
percent methyl formate, zero to 60 percent HFC-152a, zero to 60 percent
carbon dioxide (CO2), and zero to 60 percent water in XPS;
and
HCFO-1233yd(Z) in electronics cleaning, metals cleaning,
precision cleaning, aerosol solvents, and coatings.
EPA's review of certain substitutes listed in this document is
pending for other end-uses. Listing decisions in the end-uses in this
document do not prejudge EPA's listings of these substitutes for other
end-uses. While certain substitutes being added through this action to
the acceptable lists for specific end-uses may have a higher risk in
one or more SNAP criteria than certain other substitutes already listed
as acceptable or acceptable subject to restrictions, they have a
similar or lower overall risk than other acceptable substitutes in
those end-uses.
For additional information on SNAP, visit the SNAP portion of EPA's
Ozone Layer Protection website at: www.epa.gov/snap. Copies of the full
lists of acceptable substitutes for ozone-depleting substances (ODS) in
the industrial sectors covered by the SNAP program are available at
www.epa.gov/snap/substitutes-sector. For more information on the
Agency's process for administering the SNAP program or criteria for
evaluation of substitutes, refer to the initial SNAP rulemaking
published March 18, 1994 (59 FR 13044), and the regulations codified at
40 CFR part 82, subpart G. SNAP decisions and the appropriate Federal
Register citations are found at: www.epa.gov/snap/snap-regulations.
Substitutes listed as unacceptable; acceptable, subject to narrowed use
limits; or acceptable, subject to use conditions are also listed in the
appendices to 40 CFR part 82, subpart G.
The sections below discuss each substitute listing in detail.
Appendix A contains tables summarizing each listing decision in this
action. The statements in the ``Further Information'' column in the
tables provide additional information but these are not legally binding
under section 612 of the Clean Air Act (CAA). Although you are not
required to follow recommendations in the ``Further Information''
column of the table under section 612 of the CAA, some of these
statements may refer to obligations that are enforceable or binding
under federal or state programs other than the SNAP program. The
identification of other enforceable or binding requirements should not
be construed as a comprehensive list of such obligations. In many
instances, the information simply refers to standard operating
practices in existing industry standards and/or building codes. When
using these substitutes in the identified end-use, EPA strongly
encourages you to apply the information in the ``Further Information''
column. Many of these recommendations, if adopted, would not require
significant changes to existing operating practices.
You can find submissions to EPA for the substitutes listed in this
document, as well as other materials supporting the decisions in this
action, in Docket EPA-HQ-OAR-2003-0118 at www.regulations.gov.
A. Refrigeration and Air Conditioning
1. HCFO-1233zd(E)
EPA's decision: EPA finds HCFO-1233zd(E) acceptable as a substitute
for use in:
Cold storage warehouses (new equipment only)
Ice skating rinks (new equipment only)
Industrial process air conditioning (new equipment only)
HCFO-1233zd(E), marketed under the trade name Solstice[supreg]zd,
is also known as trans-1-chloro-3,3,3-trifluoroprop-1-ene (Chemical
Abstracts Service Registry Number [CAS Reg. No.] 102687-65-0).
You may find a copy of the applicant's submission, with CBI
redacted, providing the required health and environmental information
for this substitute in this end-use in Docket EPA-HQ-OAR-2003-0118 at
www.regulations.gov under the name, ``Supporting Materials for Notice
37 Listing of HCFO-1233zd(E) in Refrigeration and Air Conditioning.
SNAP Submission Received October 7, 2019.'' EPA performed an assessment
to examine the health and environmental risks of this substitute. These
assessments are available in Docket EPA-HQ-OAR-2003-0118:
``Risk Screen on Substitutes in Cold Storage Warehouses
and Industrial Process Air Conditioning. Substitute: HCFO-1233zd(E).''
``Risk Screen on Substitutes in Ice Skating Rinks.
Substitute: HCFO-1233zd(E).''
EPA previously listed HCFO-1233zd(E) as acceptable for use in
several refrigeration and air conditioning and foam blowing end-uses
(December 11, 2020, 85 FR 79863; August 10, 2012, 77 FR 47768; October
21, 2014, 79 FR 62863).
Environmental information: HCFO-1233zd(E) has an ozone depletion
potential (ODP) of less than 0.0004 and a global warming potential
(GWP) of 3.7.\1\ HCFO-1233zd(E) is excluded from the definition of
volatile organic compounds (VOC) under CAA regulations (see 40 CFR
51.100(s)) addressing the development of state implementation plans
(SIPs) to attain and maintain the National Ambient Air Quality
Standards (NAAQS). Knowingly venting or releasing this refrigerant
blend is limited by the venting prohibition under section 608(c)(2) of
the CAA, codified in EPA's regulations at 40 CFR 82.154(a).
---------------------------------------------------------------------------
\1\ WMO (World Meteorological Organization), Scientific
Assessment of Ozone Depletion: 2018, Global Ozone Research and
Monitoring Project--Report No. 58, 588 pp., Geneva, Switzerland,
2018. Available at: https://ozone.unep.org/sites/default/files/2019-05/SAP-2018-Assessment-report.pdf. In this action, the 100-year GWP
values are used.
---------------------------------------------------------------------------
Flammability information: HCFO-1233zd(E) is not flammable.
Toxicity and exposure data: Potential health effects of exposure to
this substitute include drowsiness or dizziness. The substitute may
also irritate the skin or eyes or cause frostbite. The substitute could
cause asphyxiation if air is displaced by vapors in a confined space.
These potential health effects are common to many refrigerants.
The Workplace Environmental Exposure Limit (WEEL) Committee of the
Occupational Alliance for Risk Science (OARS) has established a WEEL of
800 ppm on an eight-hour time-weighted average (8-hr TWA) for HCFO-
1233zd(E). EPA anticipates that users will be able to meet the WEEL and
address potential health risks by following requirements and
recommendations in the manufacturer's safety data sheet (SDS), American
Society of Heating, Refrigerating, and Air-Conditioning Engineers
(ASHRAE) Standard 15, and other safety precautions common to the
refrigeration and air conditioning industry.
Comparison to other substitutes in these end-uses: HCFO-1233zd(E)
has an ODP of less than 0.0004, comparable to or less than other listed
substitutes in these end-uses with ODPs ranging from zero to 0.098.
For cold storage warehouses, HCFO-1233zd(E)'s GWP of about 3.7 is
comparable to or lower than that of
[[Page 3039]]
other acceptable substitutes for new equipment such as ammonia
absorption, CO2, R-450A, R-513A, and R-407C, with GWPs \2\
ranging from zero to 1,770.
---------------------------------------------------------------------------
\2\ Unless otherwise stated, all GWPs in this document for
individual chemicals are 100-year values from: IPCC, 2007: Climate
Change 2007: The Physical Science Basis. Contribution of Working
Group I to the Fourth Assessment Report of the Intergovernmental
Panel on Climate Change [Solomon, S., Qin, D., Manning, M., Chen,
Z., Marquis, M., Averyt, K.B., Tignor M., and Miller, H.L. (eds.)].
Cambridge University Press, Cambridge, United Kingdom and New York,
NY, USA. This document is accessible at www.ipcc.ch/
publications_and_data/ar4/wg1/en/contents.html. For blends of
chemicals, such as R-507A, this document weights the GWPs of each
component of the blend by their mass percentage in the blend, based
upon the 100-year GWPs in IPCC, 2007, if available in that document.
---------------------------------------------------------------------------
For ice skating rinks and industrial process air conditioning,
HCFO-1233zd(E)'s GWP of about 3.7 is comparable to or lower than that
of other acceptable substitutes for new equipment such as ammonia
absorption, CO2, R-450A, R-513A, and R-507A, with GWPs
ranging from zero to 3,990.
Flammability and toxicity risks are comparable to or lower than
flammability and toxicity risks of other available substitutes in the
same end-uses. Toxicity risks can be minimized by use consistent with
the OARS WEEL, ASHRAE 15, and other industry standards, recommendations
in the manufacturer's SDS, and other safety precautions common in the
refrigeration and air conditioning industry.
EPA finds HCFO-1233zd(E) acceptable in the cold storage warehouses
(new equipment only), ice skating rinks (new equipment only) and
industrial process air conditioning (new equipment only) end-uses
because it does not pose greater overall environmental and human health
risk than other available substitutes in the same end-uses.
B. Foam Blowing
1. Blends of 10 to 90 Percent HFO-1234ze(E) by Weight and the Remainder
HCFO-1233zd(E)
EPA's decision: EPA finds blends of 10 to 90 percent HFO-1234ze(E)
by weight and the remainder HCFO-1233zd(E) acceptable as a substitute
for use as a blowing agent in:
Polystyrene: Extruded boardstock and billet
These blends range in composition from 10 percent HFO-1234ze(E) and
90 percent HCFO-1233zd(E) to 90 percent HFO-1234ze(E) and 10 percent
HCFO-1233zd(E). Accordingly, these blends are referred to as blends of
10 to 90 percent by weight HFO-1234ze(E) and the remainder HCFO-
1233zd(E), or hereafter in this action as ``HFO-1234ze(E)/HCFO-
1233zd(E) co-blowing blends''; they also go by the trade name of
Solstice[supreg] XBA-1. HFO-1234ze(E) is also called 1,3,3,3-
tetrafluoropropene (E), or trans-1,3,3,3-tetrafluoropropene (CAS Reg.
No. 29118-24-9). HCFO-1233zd(E) is also called trans-1-chloro-3,3,3-
trifluoro-prop-1-ene (CAS Reg. No. 102687-65-0).
You may find a copy of the applicant's submission, with CBI
redacted, providing the required health and environmental information
for this substitute in this end-use in Docket EPA-HQ-OAR-2003-0118 at
www.regulations.gov under the name, ``Supporting Materials for Notice
37 Listing Blends of 10 to 90 Percent HFO-1234ze(E) by Weight and the
Remainder HCFO-1233zd(E) as a Foam Blowing Agent. SNAP Submission
Received November 4, 2019.'' EPA has performed an assessment to examine
the health and environmental risks of this substitute. This assessment
is available in docket EPA-HQ-OAR-2003-0118 under the name ``Risk
Screen on Substitutes in Extruded Polystyrene Boardstock and Billet
Foam Substitute: Blends of 10 to 90 Percent HFO-1234ze(E) by Weight and
the Remainder HCFO-1233zd(E) (Solstice[supreg] XBA-1).''
Environmental information: HFO-1234ze(E) has an ODP of zero and
HCFO-1233zd(E) has an ODP of less than 0.0004.\3\ If these values are
weighted by mass percentage, then these HFO-1234ze(E)/HCFO-1233zd(E)
co-blowing blends have an ODP ranging from less than 0.0004 to less
than 0.00004. Their components, HFO-1234ze(E) and HCFO-1233zd(E), have
GWPs of less than one \4\ and 3.7, respectively. If these values are
weighted by mass percentage, then the blends range in GWP from about
1.3 to about 3.4. Both components of the blends are excluded from the
definition of VOC under CAA regulations (see 40 CFR 51.100(s))
addressing the development of SIPs to attain and maintain the NAAQS.
---------------------------------------------------------------------------
\3\ WMO (World Meteorological Organization), Scientific
Assessment of Ozone Depletion: 2018, Global Ozone Research and
Monitoring Project--Report No. 58, 588 pp., Geneva, Switzerland,
2018. Available at: https://ozone.unep.org/sites/default/files/2019-05/SAP-2018-Assessment-report.pdf. (WMO, 2018)
\4\ WMO, 2018.
---------------------------------------------------------------------------
Flammability information: The component HCFO-1233zd(E) is non-
flammable. HFO-1234ze(E) is not flammable at standard temperature and
pressure using the standard test method American Society for Testing
and Materials (ASTM) E681. However, at higher temperatures, such as the
temperatures typical for extruding XPS, HFO-1234ze(E) may also be
flammable, particularly at higher humidity levels.\5\
---------------------------------------------------------------------------
\5\ Bellair and Hood, 2019. Comprehensive evaluation of the
flammability and ignitability of HFO-1234ze, R.J. Bellair and L.
Hood, Process Safety and Environmental Protection 132 (2019) 273-
284. Available online at doi.org/10.1016/j.psep.2019.09.033.
---------------------------------------------------------------------------
Toxicity and exposure data: Potential health effects of these
substitutes at lower concentrations include drowsiness and dizziness.
Potential health effects also include skin or eye irritation or
frostbite. The components of HFO-1234ze(E)/HCFO-1233zd(E) co-blowing
blends can cause symptoms of asphyxiation when present at sufficiently
high concentrations. Excessive inhalation of the substitute may also
result in an irregular heartbeat, due to cardiac effects. These
potential health effects are common to many foam blowing agents.
The American Industrial Hygiene Association (AIHA) has established
a WEEL of 800 ppm as an 8-hr TWA for HFO-1234ze(E), and OARS's WEEL
committee has established a WEEL of 800 ppm for HCFO-1233zd(E). EPA
anticipates that users will be able to meet the AIHA and OARS WEELs and
address potential health risks by following requirements and
recommendations in the manufacturer's SDSs and other safety precautions
common to the foam blowing industry.
Comparison to other substitutes in this end-use: These HFO-
1234ze(E)/HCFO-1233zd(E) co-blowing blends have an ODP ranging from
less than 0.0004 to less than 0.00004, comparable to all other
acceptable substitutes in this end-use, such as blends of 10 to 99
percent by weight HFO-1336mzz(Z) and the remainder HFC-152a (hereafter
in this action ``HFO-1336mzz(Z)/HFC-152a blends''), HFO-1234ze(E),
methyl formate, and CO2. These HFO-1234ze(E)/HCFO-1233zd(E)
blends' GWPs from about 1.3 to 3.4 are lower than or comparable to
those of other acceptable substitutes in the same end-use for which we
are finding it acceptable, such as HFO-1336mzz(Z)/HFC-152a blends, HFO-
1234ze(E), light saturated hydrocarbons C3-C6 \6\ and methyl formate,
with respective GWPs
[[Page 3040]]
of approximately three to 110,\7\ 124, one,\8\ less than one,\9\ and
11.\10\
---------------------------------------------------------------------------
\6\ That is, alkanes with three to six carbons such as butane,
n-pentane, isopentane, and cyclopentane.
\7\ HFO-1336mzz(Z) and HFC-152a have GWPs of about two (WMO,
2018) and 124 (IPCC, 2007), respectively. If these values are
weighted by mass percentage, then the blends range in GWP from about
three to about 110.
\8\ WMO (World Meteorological Organization), Scientific
Assessment of Ozone Depletion: 2018, Global Ozone Research and
Monitoring Project--Report No. 58, 588 pp., Geneva, Switzerland,
2018. Available at: https://ozone.unep.org/sites/default/files/2019-05/SAP-2018-Assessment-report.pdf.
\9\ Ibid.
\10\ Ibid.
---------------------------------------------------------------------------
Flammability and toxicity risks are comparable to or lower than
flammability and toxicity risks of other available substitutes in the
same end-use. Some acceptable substitutes in this end-use are
flammable, like HFC-152a, light saturated hydrocarbons C3-C6, and
methyl formate, while others are non-flammable. Toxicity risks can be
minimized by use consistent with the AIHA's and OARS's WEELs,
recommendations in the SDS, and other safety precautions common in the
foam blowing industry.
EPA finds blends of 10 to 90 percent by weight HFO-1234ze(E) and
the remainder HCFO-1233zd(E) acceptable in the XPS end-use because they
do not pose greater overall environmental and human health risk than
other available substitutes in the same end-use.
2. Blends of 10 to 90 Percent HFO-1234ze(E) by Weight and the Remainder
HFC-152a
EPA's decision: EPA finds blends of 10 to 90 percent HFO-1234ze(E)
by weight and the remainder HFC-152a acceptable as a substitute for use
as a blowing agent in:
Polystyrene: Extruded boardstock and billet
These blends range in composition from 10 percent HFO-1234ze(E) and
90 percent HFC-152a to 90 percent HFO-1234ze(E) and 10 percent HFC-
152a. Accordingly, these blends are also referred to as blends of 10 to
90 percent by weight HFO-1234ze(E) and the remainder HFC-152a, or
hereafter in this action as ``HFO-1234ze(E)/HFC-152a co-blowing
blends''; they also go by the trade name of Solstice[supreg] XBA-2.
HFO-1234ze(E) is also called 1,3,3,3-tetrafluoropropene (E), or trans-
1,3,3,3-tetrafluoropropene (CAS Reg. No. 29118-24-9). HFC-152a is also
called 1,1-difluoroethane (CAS Reg. No. 75-37-6).
You may find a copy of the applicant's submission, with CBI
redacted, providing the required health and environmental information
for this substitute in this end-use in Docket EPA-HQ-OAR-2003-0118 at
www.regulations.gov under the name, ``Supporting Materials for Notice
37 Listing Blends of 10 to 90 Percent HFO-1234ze(E) by Weight and the
Remainder HFC-152a as a Foam Blowing Agent. SNAP Submission Received
November 4, 2019.'' EPA has performed an assessment to examine the
health and environmental risks of this substitute. This assessment is
available in docket EPA-HQ-OAR-2003-0118 under the name ``Risk Screen
on Substitutes in Extruded Polystyrene Boardstock and Billet Foam
Substitute: Blends of 10 to 90 Percent HFO-1234ze(E) by Weight and the
Remainder HFC-152a (Solstice[supreg] XBA-2).''
Environmental information: These HFO-1234ze(E)/HFC-152a co-blowing
blends and their components have an ODP of zero. Their components, HFO-
1234ze(E) and HFC-152a, have GWPs of less than one \11\ and 124,
respectively. If these values are weighted by mass percentage, then the
blends range in GWP from about 13 to about 112. Both components of the
blends are excluded from the definition of VOC under CAA regulations
(see 40 CFR 51.100(s)) addressing the development of SIPs to attain and
maintain the NAAQS.
---------------------------------------------------------------------------
\11\ WMO (World Meteorological Organization), Scientific
Assessment of Ozone Depletion: 2018, Global Ozone Research and
Monitoring Project--Report No. 58, 588 pp., Geneva, Switzerland,
2018. Available at: https://ozone.unep.org/sites/default/files/2019-05/SAP-2018-Assessment-report.pdf.
---------------------------------------------------------------------------
Flammability information: The component HFC-152a is flammable while
the component HFO-1234ze(E) is not flammable at standard temperature
and pressure using the standard test method ASTM E681. However, at
higher temperatures, such as the temperatures typical for extruding
XPS, HFO-1234ze(E) may also be flammable, particularly at higher
humidity levels.\12\
---------------------------------------------------------------------------
\12\ Bellair and Hood, 2019. Comprehensive evaluation of the
flammability and ignitability of HFO-1234ze, R.J. Bellair and L.
Hood, Process Safety and Environmental Protection 132 (2019) 273-
284. Available online at doi.org/10.1016/j.psep.2019.09.033.
---------------------------------------------------------------------------
Toxicity and exposure data: Potential health effects of these
substitutes at lower concentrations include drowsiness and dizziness.
Potential health effects also include skin or eye irritation or
frostbite. The components of HFO-1234ze(E)/HFC-152a blends can cause
symptoms of asphyxiation when present at sufficiently high
concentrations. Excessive inhalation of the substitute may also result
in an irregular heartbeat, due to cardiac effects. These potential
health effects are common to many foam blowing agents.
The AIHA has established WEELs of 1,000 ppm for HFC-152a, and of
800 ppm for HFO-1234ze(E), both as an 8-hr TWA. EPA anticipates that
users will be able to meet the AIHA WEELs and address potential health
risks by following requirements and recommendations in the
manufacturer's SDSs and other safety precautions common to the foam
blowing industry.
Comparison to other substitutes in this end-use: These HFO-
1234ze(E)/HFC-152a co-blowing blends have an ODP of zero, comparable to
all other acceptable substitutes in this end-use, such as HFO-
1336mzz(Z)/HFC-152a blends, HFC-152a, HFO-1234ze(E), methyl formate,
and CO2. These HFO-1234ze(E)/HFC-152a co-blowing blends'
GWPs from about 13 to 112 are lower than or comparable to those of
other acceptable substitutes in the same end-use for which we are
finding them acceptable, such as HFO-1336mzz(Z)/HFC-152a blends and
HFC-152a with respective GWPs of approximately three to 110 \13\ and
124. The GWPs of the HFO-1234ze(E)/HFC-152a co-blowing blends of about
13 to 112 are higher than those for acceptable alternatives such as
HFO-1234ze(E), light saturated hydrocarbons C3-C6 and methyl formate,
with respective GWPs of one,\14\ less than one,\15\ and 11.\16\ Based
on current information, EPA anticipates that HFO-1234ze(E), light
saturated hydrocarbons C3-C6 and methyl formate are not currently being
used as the sole blowing agent by any U.S. manufacturers in this end-
use because the individual chemicals have drawbacks such as
insufficient vapor pressure, insufficient solubility in the polystyrene
matrix, or high permeability resulting in low thermal resistance (``R-
value''); blends such as these HFO-1234ze(E)/HFC-152a co-blowing blends
are expected to result in a feasible balance of blowing agent
properties for adequate or better performance.
---------------------------------------------------------------------------
\13\ HFO-1336mzz(Z) and HFC-152a have GWPs of about two (WMO,
2018) and 124 (IPCC, 2007), respectively. If these values are
weighted by mass percentage, then the blends range in GWP from about
three to about 110.
\14\ WMO (World Meteorological Organization), Scientific
Assessment of Ozone Depletion: 2018, Global Ozone Research and
Monitoring Project--Report No. 58, 588 pp., Geneva, Switzerland,
2018. Available at: https://ozone.unep.org/sites/default/files/2019-05/SAP-2018-Assessment-report.pdf.
\15\ Ibid.
\16\ Ibid.
---------------------------------------------------------------------------
Flammability and toxicity risks are comparable to or lower than
flammability and toxicity risks of other available substitutes in the
same end-use. Some acceptable substitutes in this end-use are
flammable, like HFC-152a, light saturated hydrocarbons C3-C6, and
methyl formate, while others are non-flammable. Toxicity risks can be
minimized by use consistent with the
[[Page 3041]]
AIHA's WEELs, recommendations in the SDS, and other safety precautions
common in the foam blowing industry.
EPA finds blends of 10 to 90 percent by weight HFO-1234ze(E) and
the remainder HFC-152a acceptable in the XPS end-use because they do
not pose greater overall environmental and human health risk than other
available substitutes in the same end-use.
3. Blends of Zero to 100 Percent HFO-1234ze(E), Zero to 70 Percent
Methyl Formate, Zero to 60 Percent HFC-152a, Zero to 60 Percent
CO2 and Zero to 60 Percent Water
EPA's decision: EPA finds blends of zero to 100 percent HFO-
1234ze(E), zero to 70 percent methyl formate, zero to 60 percent HFC-
152a, zero to 60 percent CO2 and zero to 60 percent water acceptable as
a substitute for use as a blowing agent in:
Polystyrene: Extruded boardstock and billet
These blends are hereafter referred to as ``HFO-1234ze(E)/methyl
formate/HFC-152a/CO2/water co-blowing blends.'' The
components of the blends are co-blown and component percentages are by
weight.
HFO-1234ze(E) is also known as HFC-1234ze, HFO-1234ze or trans-
1,3,3,3-tetrafluoroprop-1-ene (CAS Reg. No. 29118-24-9). Methyl formate
is also known as methyl methanoate or formic acid, methyl ester (CAS
Reg. No. 107-31-3). HFC-152a, also known as 1,1-difluoroethane, has CAS
Reg. No. 75-37-6. CO2 has CAS Reg. No. 124-38-9, and water
has CAS Reg. No. 7732-18-5.
You may find a copy of the applicant's submission, with CBI
redacted, providing the required health and environmental information
for this substitute in this end-use in Docket EPA-HQ-OAR-2003-0118 at
www.regulations.gov under the name, ``Supporting Materials for Notice
37 Listing Blends of 0-100% HFO-1234ze(E), 0-70% Methyl Formate, 0-60%
HFC-152a, 0-60% CO2 and 0-60% Water as a Foam Blowing Agent.
SNAP Submission Received January 26, 2021.'' EPA has performed an
assessment to examine the health and environmental risks of this
substitute. This assessment is available in docket EPA-HQ-OAR-2003-0118
under the name ``Risk Screen on Substitutes in Extruded Polystyrene
Boardstock and Billet Foam Substitute: HFO-1234ze(E)/Methyl Formate/
HFC-152a/CO2/Water Co-blowing Blends for Extruded
Polystyrene Foam Insulation (HFO-1234ze(E)/Methyl Formate/HFC-152a/
CO2/Water Co-blowing Blends).''
Environmental information: The blends have an ODP of zero. Their
components, HFO-1234ze(E), methyl formate, HFC-152a, CO2,
and water have GWPs of one,\17\ 11,\18\ 124,\19\ one,\20\ and less than
one,\21\ respectively. If these values are weighted by mass percentage,
then the blends could have a GWP ranging from one to 80. HFO-1234ze(E),
methyl formate, HFC-152a, CO2, and water--components of the
blends--are excluded from EPA's regulatory definition of VOC under CAA
regulations that address the development of SIPs to attain and maintain
the NAAQS. See 40 CFR 51.100(s).
---------------------------------------------------------------------------
\17\ WMO (World Meteorological Organization), Scientific
Assessment of Ozone Depletion: 2018, Global Ozone Research and
Monitoring Project--Report No. 58, 588 pp., Geneva, Switzerland,
2018. Available at: https://ozone.unep.org/sites/default/files/2019-05/SAP-2018-Assessment-report.pdf. In this action, the 100-year GWP
values are used.
\18\ WMO, 2018.
\19\ IPCC, 2007.
\20\ IPCC, 2007.
\21\ Sherwood et al. 2018. This paper estimated that water vapor
emitted near Earth's surface due to anthropogenic sources (e.g.,
irrigation) would have a GWP of -10-\3\ to 5 x 10-\4\.
``The global warming potential of near-surface emitted water
vapour,'' Steven C. Sherwood, Vishal Dixit and Chrys[eacute]is
Salomez. Environ. Res. Lett. 13 (2018) 104006.
---------------------------------------------------------------------------
Flammability information: The components HFC-152a and methyl
formate are flammable while the other components of the blends are non-
flammable at standard temperature and pressure using the standard test
method ASTM E681. However, at higher temperatures, such as the
temperatures typical for extruding XPS, HFO-1234ze(E) may also be
flammable, particularly at higher humidity levels.\22\
---------------------------------------------------------------------------
\22\ Bellair and Hood, 2019. Comprehensive evaluation of the
flammability and ignitability of HFO-1234ze, R.J. Bellair and L.
Hood, Process Safety and Environmental Protection 132 (2019) 273-
284. Available online at doi.org/10.1016/j.psep.2019.09.033.
---------------------------------------------------------------------------
Toxicity and exposure data: Potential health effects of these
substitutes at lower concentrations include headache, nausea,
drowsiness, and dizziness. The substitutes may also irritate the skin
or eyes or cause frostbite. Excessive inhalation of the substitutes may
also result in an irregular heartbeat, due to cardiac effects. At
sufficiently high concentrations, they may cause central nervous system
depression and affect respiration. The substitutes could cause
asphyxiation if air is displaced by vapors in a confined space. These
health effects are common to many foam blowing agents.
The AIHA has established WEELs of 1,000 ppm as an eight-hour time-
weighted average for HFC-152a and 800 ppm for HFO-1234ze(E). Methyl
formate has an Occupational Safety and Health Administration (OSHA)
permissible exposure limits (PEL) of 100 ppm on an 8-hr TWA.
CO2 has an OSHA PEL of 5,000 ppm on an 8-hr TWA, and a 15-
minute recommended short-term exposure limit (STEL) of 30,000 ppm
established by the National Institute for Occupational Safety and
Health (NIOSH). EPA anticipates that users will be able to meet the
AIHA WEELs, OSHA PELs, and NIOSH STEL and address potential health
risks by following requirements and recommendations in the
manufacturer's SDSs and other safety precautions common to the foam
blowing industry.
Comparison to other substitutes in this end-use: HFO-1234ze(E)/
methyl formate/HFC-152a/CO2/water co-blowing blends have
ODPs of zero, comparable to all other acceptable substitutes in this
end-use, such as HFO-1336mzz(Z)/HFC-152a blends, HFC-152a, HFO-
1234ze(E), methyl formate, and CO2.
The GWPs of the HFO-1234ze(E)/methyl formate/HFC-152a/
CO2/water co-blowing blends, ranging from approximately one
to 80, are lower than HFC-152a's GWP of 124 and are comparable to or
lower than those for HFO-1336mzz(Z)/HFC-152a blends (three to 110
\23\). The worst-case GWPs of the HFO-1234ze(E)/methyl formate/HFC-
152a/CO2/water co-blowing blends are higher than those for
acceptable alternatives such as HFO-1234ze(E), light saturated
hydrocarbons C3-C6 and methyl formate, with respective GWPs of less
than one,\24\ less than one,\25\ and 11,\26\ while the GWP at the low
end of the range of approximately one is comparable to those acceptable
alternatives. Based on current information, EPA anticipates that HFO-
1234ze(E), light saturated hydrocarbons C3-C6 and methyl formate are
not currently being used as the sole blowing agent by any U.S.
manufacturers in this end-use because the individual chemicals have
drawbacks such as insufficient vapor pressure, insufficient solubility
in the polystyrene matrix, or high permeability resulting in low
thermal resistance (``R-value''); blends such as these HFO-1234ze(E)/
methyl formate/HFC-152a/CO2/water co-blowing blends are
expected to result in a feasible balance of blowing agent
[[Page 3042]]
properties for adequate or better performance.
---------------------------------------------------------------------------
\23\ HFO-1336mzz(Z) and HFC-152a have GWPs of about two (WMO,
2018) and 124 (IPCC, 2007), respectively. If these values are
weighted by mass percentage, then the blends range in GWP from about
three to about 110.
\24\ WMO, 2018.
\25\ WMO, 2018.
\26\ WMO, 2018.
---------------------------------------------------------------------------
Flammability and toxicity risks of the HFO-1234ze(E)/methyl
formate/HFC-152a/CO2/water co-blowing blends are comparable
to or lower than flammability and toxicity risks of other available
substitutes in the same end-use. Some acceptable substitutes in this
end-use are flammable, like HFC-152a, light saturated hydrocarbons C3-
C6, and methyl formate, while others are non-flammable. Toxicity risks
can be minimized by use consistent with the AIHA WEELs, OSHA PELs,
NIOSH STEL, recommendations in the manufacturer's SDSs, and other
safety precautions common in the foam-blowing industry.
EPA finds HFO-1234ze(E)/methyl formate/HFC-152a/CO2/
water co-blowing blends acceptable in the XPS end-use because they do
not pose greater overall environmental and human health risk than other
available substitutes in the same end-use.
C. Aerosols
1. HCFO-1233yd(Z)
EPA's decision: EPA finds HCFO-1233yd(Z) acceptable as a substitute
for use in:
Aerosol solvents
HCFO-1233yd(Z) is also known as (Z)-1-Chloro-2,3,3-trifluoropropene
(CAS Reg. No. 1263679-68-0).
You may find a copy of the applicant's submission, with CBI
redacted, providing the required health and environmental information
for this substitute in this end-use in Docket EPA-HQ-OAR-2003-0118 at
www.regulations.gov under the name, ``Supporting Materials for Notice
37 Listing of HCFO-1233yd(Z) in Cleaning Solvents, Aerosol Solvents,
and Coatings. SNAP Submission Received March 12, 2019.'' EPA performed
an assessment to examine the health and environmental risks of this
substitute. This assessment is available in Docket EPA-HQ-OAR-2003-
0118:
``Risk Screen on Substitutes in Aerosol Solvents.
Substitute: HCFO-1233yd(Z).''
Environmental information: HCFO-1233yd(Z) has an ODP of 0.00003 and
a GWP of less than 1.\27\ Under CAA regulations (see 40 CFR 51.100(s))
defining VOC for the purpose of addressing the development of SIPs to
attain and maintain the NAAQS, HCFO-1233yd(Z) would be considered a
VOC. That definition provides that ``any compound of carbon'' which
``participates in atmospheric photochemical reactions'' is considered a
VOC unless expressly excluded in that provision based on a
determination of ``negligible photochemical reactivity.'' The
manufacturer has petitioned EPA to exclude HCFO-1233yd(Z) from the
definition of VOC under those regulations. EPA has not yet taken action
on that petition. This substitute is subject to a Toxic Substance
Control Act (TSCA) section 5(a)(2) Significant New Use Rule (SNUR).
---------------------------------------------------------------------------
\27\ Kazuaki Tokuhashi, Tadafumi Uchimaru, Kenji Takizawa, and
Shigeo Kondo, 2018. Rate Constants for the Reactions of OH Radical
with the (E)/(Z) Isomers of CF3CF=CHCl and
CHF2CF=CHCl (J.Phys. Chem. A 2018, 122, 3120-3127)
(Tokuhashi et al., 2018).
---------------------------------------------------------------------------
Flammability information: HCFO-1233yd(Z) is not flammable.
Toxicity and exposure data: Potential health effects of exposure to
this substitute include drowsiness or dizziness. The substitute may
also irritate the skin or eyes. The substitute could cause asphyxiation
if air is displaced by vapors in a confined space. These potential
health effects are common to many aerosol solvents.
The manufacturer recommends an acceptable exposure limit (AEL) for
the workplace of 250 ppm on an 8-hr TWA for HCFO-1233yd(Z). EPA
anticipates that users will be able to meet the manufacturer's AEL and
address potential health risks by following requirements and
recommendations in the manufacturer's SDS, and other safety precautions
common to the aerosol industry.
Comparison to other substitutes in this end-use: HCFO-1233yd(Z) has
an ODP of less than 0.00003, comparable to or less than other listed
substitutes in this end-use with ODPs ranging from zero to 0.033.
HCFO-1233yd(Z)'s GWP of less than one is lower than that of other
acceptable substitutes such as HFE-7200, HFE-347mcc3, HFC-365mfc and
HFC-4310mee with GWPs ranging from 59 to 1,640. HCFO-1233yd(Z)'s GWP is
lower than or comparable to the GWPs of other acceptable substitutes
for aerosol solvents, including acetone, methoxytridecafluoroheptene
isomers (MPHE), and trans-1-chloro-3,3,3-trifluoroprop-1-ene with GWPs
ranging from less than one to seven.
Some acceptable substitutes in this end-use are VOC, like HCFO-
1233yd(Z), while others are excluded from the definition of VOC.
Flammability and toxicity risks are comparable to or lower than
flammability and toxicity risks of other available substitutes in the
same end-use. Toxicity risks can be minimized by use consistent with
the manufacturer's AEL, industry standards, recommendations in the
manufacturer's SDS, and other safety precautions common in the aerosol
industry.
EPA finds HCFO-1233yd(Z) acceptable in the aerosol solvent end-use
because it does not pose greater overall environmental and human health
risk than other available substitutes in the same end-use.
D. Cleaning Solvents
1. HCFO-1233yd(Z)
EPA's decision: EPA finds HCFO-1233yd(Z) acceptable as a substitute
for use in:
Electronics cleaning
Metals cleaning
Precision cleaning
HCFO-1233yd(Z) is also known as (Z)-1-chloro-2,3,3-trifluoropropene
(CAS Reg. No. 1263679-68-0).
You may find a copy of the applicant's submission, with CBI
redacted, providing the required health and environmental information
for this substitute in this end-use in Docket EPA-HQ-OAR-2003-0118 at
www.regulations.gov under the name, ``Supporting Materials for Notice
37 Listing of HCFO-1233yd(Z) in Cleaning Solvents, Aerosol Solvents,
and Coatings. SNAP Submission Received March 12, 2019.'' EPA performed
an assessment to examine the health and environmental risks of this
substitute. This assessment is available in Docket EPA-HQ-OAR-2003-
0118:
``Risk Screen on Substitutes in Electronics Cleaning,
Metals Cleaning, and Precision Cleaning. Substitute: HCFO-1233yd(Z).''
Environmental information: The environmental information for this
substitute is set forth in the ``Environmental information'' section in
listing in I.C.1. above.
Flammability information: HCFO-1233yd(Z) is not flammable.
Toxicity and exposure data: The toxicity information for this
substitute is set forth in the ``Toxicity and exposure data'' section
in listing I.C.1. above.
Comparison to other substitutes in these end-uses: HCFO-1233yd(Z)
has an ODP of less than 0.00003, comparable to or less than other
listed substitutes in the metals cleaning, electronics cleaning, and
precision cleaning end-uses with ODPs ranging from zero to 0.033.
HCFO-1233yd(Z)'s GWP of less than 1 is lower than that of other
acceptable substitutes such as HFE-7200, HFE-7100, HFC-365mfc and HFC-
4310mee with GWPs ranging from 59 to 1,640. HCFO-1233yd(Z)'s GWP is
lower than or comparable to the GWPs of other acceptable substitutes
for cleaning solvents, including acetone, MPHE, and
[[Page 3043]]
trans-1-chloro-3,3,3-trifluoroprop-1-ene with GWPs ranging from less
than one to seven.
Some acceptable substitutes in these end-uses are VOC, like HCFO-
1233yd(Z), while others are excluded from the definition of VOC.
Flammability and toxicity risks are comparable to or lower than
flammability and toxicity risks of other available substitutes in the
same end-use. Toxicity risks can be minimized by use consistent with
the manufacturer's AEL, recommendations in the manufacturer's SDS, and
other safety precautions common in the cleaning solvents industry.
EPA finds HCFO-1233yd(Z) acceptable in the end-uses listed above
because it does not pose greater overall environmental and human health
risk than other available substitutes in the same end-uses.
E. Adhesives, Coatings, and Inks
1. HCFO-1233yd(Z)
EPA's decision: EPA finds HCFO-1233yd(Z) acceptable as a substitute
for use as a carrier solvent in:
Coatings
HCFO-1233yd(Z) is also known as (Z)-1-chloro-2,3,3-trifluoropropene
(CAS Reg. No. 1263679-68-0).
You may find a copy of the applicant's submission, with CBI
redacted, providing the required health and environmental information
for this substitute in this end-use in Docket EPA-HQ-OAR-2003-0118 at
www.regulations.gov under the name, ``Supporting Materials for Notice
37 Listing of HCFO-1233yd(Z) in Cleaning Solvents, Aerosol Solvents,
and Coatings. SNAP Submission Received March 12, 2019.'' EPA performed
an assessment to examine the health and environmental risks of this
substitute. This assessment is available in Docket EPA-HQ-OAR-2003-
0118:
``Risk Screen on Substitutes in Coatings. Substitute:
HCFO-1233yd(Z).''
Environmental information: The environmental information for this
substitute is set forth in the ``Environmental information'' section in
listing I.C.1., above.
Flammability information: HCFO-1233yd(Z) is not flammable.
Toxicity and exposure data: The toxicity information for this
substitute is set forth in the ``Toxicity and exposure data'' section
in listing I.C.1., above.
Comparison to other substitutes in these end-uses: HCFO-1233yd(Z)
has an ODP of less than 0.00003, comparable to or less than other
listed substitutes in this end-use with ODPs ranging from zero to
0.00034.
For coatings, HCFO-1233yd(Z)'s GWP of less than one is lower than
that of other acceptable substitutes such as HFE-7200 and HFE-7100 with
GWPs ranging from 59 to 297. HCFO-1233yd(Z)'s GWP is lower than or
comparable to the GWPs of other acceptable substitutes for coatings,
including acetone, MPHE, and trans-1-chloro-3,3,3-trifluoroprop-1-ene
with GWPs ranging from less than one to seven. Some acceptable
substitutes in this end-use are VOC, like HCFO-1233yd(Z), while others
are excluded from the definition of VOC.
Flammability and toxicity risks are comparable to or lower than
flammability and toxicity risks of other available substitutes in the
same end-use. Toxicity risks can be minimized by use consistent with
the manufacturer's AEL, recommendations in the manufacturer's SDS, and
other safety precautions common in the coatings industry.
EPA finds HCFO-1233yd(Z) acceptable in the coatings end-use because
it does not pose greater overall environmental and human health risk
than other available substitutes in the same end-use.
List of Subjects in 40 CFR Part 82
Environmental protection, Administrative practice and procedure,
Air pollution control, Reporting and recordkeeping requirements.
Hans Christopher Grundler,
Director, Office of Atmospheric Programs.
Appendix A: Summary of Decisions for New Acceptable Substitutes
Refrigeration and Air Conditioning
----------------------------------------------------------------------------------------------------------------
End-use Substitute Decision Further information \1\
----------------------------------------------------------------------------------------------------------------
Cold Storage Warehouses (new HCFO-1233zd(E).. Acceptable........... HCFO-1233zd(E) is also known as trans-1-
equipment only). chloro-3,3,3-trifluoroprop-1-ene
(Chemical Abstracts Service Registry
Number [CAS Reg. No.] 102687-65-0).
HCFO-1233zd(E) has an ozone depletion
potential (ODP) of less than 0.0004 and
a 100-year integrated global warming
potential (GWP) of about 3.7.
HCFO-1233zd(E) is nonflammable.
The Workplace Environmental Exposure
Limits (WEEL) committee of the
Occupational Alliance for Risk Science
(OARS) has established a WEEL of 800
ppm as an eight-hour time-weighted
average (8-hr TWA) for HCFO-1233zd(E).
Ice Skating Rinks (new HCFO-1233zd(E).. Acceptable........... HCFO-1233zd(E) is also known as trans-1-
equipment only). chloro-3,3,3-trifluoroprop-1-ene (CAS
Reg. No. 102687-65-0).
HCFO-1233zd(E) has an ODP of less than
0.0004 and a GWP of about 3.7.
HCFO-1233zd(E) is nonflammable.
OARS has established a WEEL of 800 ppm
on an 8-hr TWA for HCFO-1233zd(E).
Industrial Process Air HCFO-1233zd(E).. Acceptable........... HCFO-1233zd(E) is also known as trans-1-
Conditioning (new equipment chloro-3,3,3-trifluoroprop-1-ene (CAS
only). Reg. No. 102687-65-0).
HCFO-1233zd(E) has an ODP of less than
0.0004 and a GWP of about 3.7.
HCFO-1233zd(E) is nonflammable.
OARS has established a WEEL of 800 ppm
on an 8-hr TWA for HCFO-1233zd(E).
----------------------------------------------------------------------------------------------------------------
\1\ See recommendations in the manufacturer's SDS and guidance for all listed refrigerants.
Foam Blowing Agents
----------------------------------------------------------------------------------------------------------------
End-use Substitute Decision Further information \1\
----------------------------------------------------------------------------------------------------------------
Extruded Polystyrene: Blends of 10 to Acceptable........... This substitute is blends of 10 to 90
Boardstock and Billet. 90 percent HFO- percent HFO-1234ze(E) by weight and the
1234ze(E) by remainder HCFO-1233zd(E). HFO-1234ze(E)
weight and the is also called 1,3,3,3-
remainder HCFO- tetrafluoropropene(E), or trans-1,3,3,3-
1233zd(E). tetrafluoropropene (Chemical Abstracts
Service Registry Number [CAS Reg. No.]
29118-24-9). HCFO-1233zd(E) is also
called trans-1-chloro-3,3,3-trifluoro-
prop-1-ene (CAS Reg. No. 102687-65-0).
[[Page 3044]]
HFO-1234ze(E) has a 100-year integrated
global warming potential (GWP) of less
than one.
HCFO-1233zd(E) has an ozone depletion
potential (ODP) of less than 0.0004 and
a GWP of 3.7. The blends have an ODP
ranging from less than 0.0004 to less
than 0.00004 and range in GWP from
about 1.3 to about 3.4.
HFO-1234ze(E) is not flammable at
standard temperature and pressure,
however, however, at higher
temperatures, such as the temperatures
typical for extruding extruded
polystyrene: boardstock and billet
(XPS), HFO-1234ze(E) may be flammable,
particularly at higher humidity levels.
HCFO-1233zd(E) is non-flammable.
The American Industrial Hygiene
Association (AIHA) has established a
Workplace Environmental Exposure Limit
(WEEL) of 800 ppm as an eight-hour time-
weighted average (8-hr TWA) for HFO-
1234ze(E), and the Occupational
Alliance for Risk Sciences (OARS) has
established a WEEL of 800 ppm as an 8-
hr TWA for HCFO-1233zd(E).
Extruded Polystyrene: Blends of 10 to Acceptable........... This substitute is blends of 10 to 90
Boardstock and Billet. 90 percent HFO- Percent HFO-1234ze(E) by weight and the
1234ze(E) by remainder HFC-152a. HFO-1234ze(E) is
weight and the also called 1,3,3,3-tetrafluoropropene
remainder HFC- (E), or trans-1,3,3,3-
152a. tetrafluoropropene (CAS Reg. No. 29118-
24-9). HFC-152a is also called 1,1-
difluoroethane (CAS Reg. No. 75-37-6).
The blend and its components have an ODP
of zero. HFO-1234ze(E) has a GWP of
less than one and HFC-152a has a GWP of
124. The blends range in GWP from about
13 to about 112.
HFO-1234ze(E) is not flammable at
standard temperature and pressure,
however, at higher temperatures, such
as the temperatures typical for
extruding XPS, HFO-1234ze(E) may be
flammable, particularly at higher
humidity levels. HFC-152a is flammable
at standard temperature and pressure.
The AIHA has established a WEEL of 1,000
ppm for HFC-152a and a WEEL of 800 ppm
for HFO-1234ze(E), both as an 8-hr TWA.
Extruded Polystyrene: Blends of 0-100% Acceptable........... This substitute is blends of 0-100% HFO-
Boardstock and Billet. HFO-1234ze(E), 1234ze(E), 0-70% methyl formate, 0-60%
0-70% Methyl HFC-152a, 0-60% CO2 and 0-60% water.
Formate, 0-60% HFO-1234ze(E) is also called 1,3,3,3-
HFC-152a, 0-60% tetrafluoropropene (E), or trans-
CO2 and 0-60% 1,3,3,3-tetrafluoropropene (CAS Reg.
Water. No. 29118-24-9). Methyl formate is also
called methyl methanoate or formic
acid, methyl ester (CAS Reg. No. 107-31-
3). HFC-152a is also called 1,1-
difluoroethane, has CAS Reg. No. 75-37-
6. CO2 has CAS Reg. No. 124-38-9, and
water has CAS Reg. No. 7732-18-5.
HFO-1234ze(E) and water have GWPs of
less than one, CO2 has a GWP of one,
methyl formate has a GWP of 11, and HFC-
152a has a GWP of 124. The blends range
in GWP from approximately one to 80.
HFO-1234ze(E) is not flammable at
standard temperature and pressure;
however, at higher temperatures, such
as the temperatures typical for
extruding XPS, HFO-1234ze(E) may be
flammable, particularly at higher
humidity levels. HFC-152a and methyl
formate are flammable at standard
temperature and pressure.
The AIHA has established a WEEL of 1,000
ppm for HFC-152a and a WEEL of 800 ppm
for HFO-1234ze(E), both as an 8-hr TWA.
----------------------------------------------------------------------------------------------------------------
\1\ See recommendations in the manufacturer's SDS and guidance for all listed foam blowing agents.
Cleaning Solvents
----------------------------------------------------------------------------------------------------------------
End-use Substitute Decision Further information \1\
----------------------------------------------------------------------------------------------------------------
Electronics cleaning, metals HCFO-1233yd(Z).. Acceptable........... HCFO-1233yd(Z) is also known as (Z)-1-
cleaning, precision cleaning. chloro-2,3,3-trifluoropropene (CAS Reg.
No. 1263679-68-0).
HCFO-1233yd(Z) has an ozone depletion
potential (ODP) of 0.00003 and a global
warming potential (GWP) of less than 1.
This compound is nonflammable.
The manufacturer recommends an
acceptable exposure limit (AEL) for the
workplace for HCFO-1233yd(Z) of 250 ppm
on an eight-hour time-weighted average
(8-hr TWA).
This substitute is subject to a Toxic
Substances Control Act (TSCA) section
5(a)(2) Significant New Use Rule
(SNUR).
----------------------------------------------------------------------------------------------------------------
\1\ See recommendations in the manufacturer's SDS and guidance for all listed cleaning solvents.
Aerosols
----------------------------------------------------------------------------------------------------------------
End-use Substitute Decision Further information \1\
----------------------------------------------------------------------------------------------------------------
Aerosol solvents............. HCFO-1233yd(Z).. Acceptable........... HCFO-1233yd(Z) is also known as (Z)-1-
chloro-2,3,3-trifluoropropene (CAS Reg.
No. 1263679-68-0).
HCFO-1233yd(Z) has an ozone depleting
potential (ODP) of 0.00003 and a global
warming potential (GWP) of less than 1.
This compound is nonflammable.
The manufacturer recommends an
acceptable exposure limit (AEL) for the
workplace for HCFO-1233yd(Z) of 250 ppm
on an eight-hour time-weighted average
(8-hr TWA).
This substitute is subject to a Toxic
Substances Control Act (TSCA) section
5(a)(2) Significant New Use Rule
(SNUR).
----------------------------------------------------------------------------------------------------------------
\1\ See recommendations in the manufacturer's SDS and guidance for all listed aerosols.
[[Page 3045]]
Adhesives, Coatings, and Inks
----------------------------------------------------------------------------------------------------------------
End-use Substitute Decision Further information \1\
----------------------------------------------------------------------------------------------------------------
Coatings..................... HCFO-1233yd(Z).. Acceptable........... HCFO-1233yd(Z) is also known as (Z)-1-
chloro-2,3,3-trifluoropropene (CAS Reg.
No. 1263679-68-0).
HCFO-1233yd(Z) has an ozone depleting
potential (ODP) of 0.00003 and a global
warming potential (GWP) of less than 1.
This compound is nonflammable.
The manufacturer recommends an
acceptable exposure limit (AEL) for the
workplace for HCFO-1233yd(Z) of 250 ppm
on an eight-hour time-weighted average
(8-hr TWA).
This substitute is subject to a Toxic
Substance Control Act (TSCA) section
5(a)(2) Significant New Use Rule
(SNUR).
----------------------------------------------------------------------------------------------------------------
\1\ See recommendations in the manufacturer's SDS and guidance for all listed carrier solvents for adhesives,
coatings, and inks.
[FR Doc. 2022-00998 Filed 1-19-22; 8:45 am]
BILLING CODE 6560-50-P