v>EPA

December 2022
EPA Document #740-S-22-007
United States	Office of Chemical Safety and

Environmental Protection Agency	Pollution Prevention

Non-Technical Summary of the Risk Evaluation for

1-Bromopropane
(w-Propyl Bromide)

CASRN: 106-94-5

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December 2022

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BACKGROUND

•	The TSCA risk evaluation for 1-bromopropane (1-BP) was issued in August 2020.

•	Uses for 1-BP include use as a reactant in the manufacturing of other chemical substances, as a
solvent in vapor degreasing and aerosol degreasing operations, in spray adhesives and dry
cleaning, and in laboratory uses. Consumer and commercial uses of 1-BP include several
applications including aerosol degreaser, spot cleaner and stain removers, and in insulation for
building and construction materials.

•	The total annual aggregate production volume reported for 1-BP under the Chemical Data
Reporting (CDR) rule ranged from 31 million to 170 million pounds between 2016 and 2019.

ACTION

•	EPA is releasing a final revision to the risk determination on 1-BP with an order withdrawing
the TSCA section 6(i)(l) order previously included in the August 2020 risk evaluation. This
action follows issuance of a draft revised risk determination that EPA issued for comment in
July 2022 (87 FR 43265). EPA has determined that 1-BP presents an unreasonable risk of
injury to health under its conditions of use.

•	This final risk evaluation, which includes the 2020 risk evaluation and a 2022 final revised
unreasonable risk determination, is conducted pursuant to the Toxic Substances Control Act
(TSCA), as amended by the Frank R. Lautenberg Chemical Safety for the 21st Century Act,
which requires EPA to prioritize and evaluate the risk of existing chemicals to determine
whether a chemical presents an unreasonable risk of injury to health or the environment under
the conditions of use. Under TSCA, if a chemical is determined to present an unreasonable
risk, then EPA will propose risk management regulatory action to the extent necessary so that
the chemical substance no longer presents an unreasonable risk.

•	The 2020 risk evaluation, supplemental materials, 2022 revised unreasonable risk
determination and corresponding response to public comments can be found in dockets EPA-
HQ-OPPT-2019-023 5 and EPA-HQ-OPPT-2016-0741 on www.regulations.gov.

•	1-BP was selected in 2016 as one of the first 10 chemicals for risk evaluation under section 6
of TSCA.

KEY POINTS

•	EPA has identified risks for non-cancer adverse effects from acute and chronic inhalation and
dermal exposures to 1-BP, and for cancer from chronic inhalation and dermal exposures to 1-
BP. In the 1-BP risk characterization, developmental toxicity (i.e., post-implantation loss) was
identified as the most sensitive endpoint for non-cancer adverse effects from acute and chronic
inhalation and dermal exposures for all conditions of use.

•	Additional risks associated with other adverse effects (e.g., additional developmental toxicity,
reproductive toxicity, liver toxicity, kidney toxicity, and neurotoxicity) were identified for
acute and chronic inhalation and dermal exposures.

•	Public comments and external scientific peer review informed the development of the 1-BP
final risk evaluation. EPA published the 1-BP final revised unreasonable risk determination in
December 2022, the 1-BP draft revised unreasonable risk determination in July 2022, the 1-BP
risk evaluation in August 2020, the 1-BP draft risk evaluation in August 2019 (for a 60-day
public comment period), the 1-BP problem formulation document in May 2018, and the scope
document in June 2017.

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•	Additionally, EPA held a peer review meeting of the Science Advisory Committee on
Chemicals (SACC) on the draft risk evaluation of 1-BP on September 10-12, 2019.

•	In the revised unreasonable risk determination for 1-BP, EPA is making an unreasonable risk
determination for 1-BP as a whole chemical substance, rather than taking a condition of use-
specific approach. The whole chemical approach is appropriate for 1-BP because there are
benchmark exceedances for a substantial number of conditions of use for human health and
there are irreversible health effects (e.g., cancer) associated with 1-BP exposures.

•	After evaluating 25 conditions of use, EPA determined that 1-BP presents an unreasonable risk
to human health under its conditions of use based on risk of injury to health of workers,
occupational non-users (ONUs), consumers, and bystanders.

•	In addition, EPA is revising the assumption that workers always and properly use personal
protective equipment (PPE), although EPA does not question public comments received
regarding the occupational safety practices often followed by industry. Information on the use
of PPE as a means of mitigating risk will be considered during the risk management phase.
Removing the assumption that workers wear PPE in making the whole chemical risk
determination for 1-BP means that: seven conditions of use in addition to the original 16
conditions of use drive the unreasonable risk for 1-BP; additional risks of cancer from dermal
exposures is also identified as driving the unreasonable risk to workers in six conditions of use;
additional risks for acute and chronic non-cancer effects from inhalation exposures drive the
unreasonable risk to workers in two conditions of use; and additional risks for acute and
chronic non-cancer effects and cancer from inhalation and dermal exposures to workers drive
the unreasonable risk in one condition of use (where previously this condition of use was
identified as presenting unreasonable risk only to ONUs).

•	Overall, 23 of the 25 conditions of use evaluated drive the 1-BP whole chemical unreasonable
risk determination due to risks identified for human health. These conditions of use include but
are not limited to: processing the chemical into formulation; use as solvent in industrial and
commercial cleaning and degreasing, including vapor degreasing, cold cleaning and spray and
aerosol degreasers; use in adhesives and sealants; use in dry cleaning and spot cleaning for
clothing; use in several specialty spray/aerosol applications. Additionally, the conditions of use
found to drive unreasonable risk to consumers include: solvent in aerosol spray
degreasers/cleaners, spot cleaners and stain removers, liquid cleaner used for coins or scissors,
liquid spray/aerosol cleaners, adhesive accelerants used in arts, crafts, and hobby materials,
automotive care products such as refrigerant flush, and anti-adhesive agents used in mold
cleaning and release products.

•	The conditions of use that do not drive EPA's unreasonable risk determination for 1-BP
are distribution in commerce and commercial and consumer use in insulation.

•	For 1-BP, the air exposure pathway was not fully assessed in the final risk evaluation (see
Sections 1.4.2 and 4.5.2.3 of the August 2020 1-BP risk evaluation). EPA is conducting a
screening approach to assess risks from the air and water pathways for several of the first 10
chemicals, including 1-BP. The goal of the recently-developed screening approach is to
remedy this exclusion and to determine if there may be risks that were unaccounted for in the
1-BP risk evaluation. EPA expects to describe its findings regarding the chemical-specific
application of this screening-level approach in the forthcoming proposed rule under TSCA
section 6(a) for 1-BP.

•	EPA did not identify risks of injury to the environment that drive the unreasonable risk
determination for 1-BP.

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•	As noted above, EPA is releasing a final revision to the unreasonable risk determination with
an order withdrawing the TSCA section 6(i)(l) order previously included in the August 2020
risk evaluation. EPA is also releasing a document with responses to public comments received
on the draft revised risk determination for 1-BP published in July 2022.

NEXT STEPS

•	EPA has issued the final risk evaluation (2020 risk evaluation and 2022 revised risk
determination) for 1-BP, meeting the requirements set forth in TSCA section 6(b) for chemical
risk evaluations. EPA is now initiating the process to address the unreasonable risk identified.
Following the issuance of the final risk evaluation, EPA will address, by rule, the unreasonable
risk identified. The public will have an opportunity to comment on a proposed rule before EPA
issues a final rule.

SUMMARY OF UNREASONABLE RISK DETERMINATION

EPA has determined that 1-BP presents an unreasonable risk of injury to human health under the
conditions of use.

EPA's unreasonable risk determination for 1-BP is driven by risks associated with the following
conditions of use, considered singularly or in combination with other exposures:

•	Manufacture (domestic manufacturing);

•	Manufacture (import);

•	Processing: as a reactant;

•	Processing: incorporation into formulation, mixture or reaction product;

•	Processing: incorporation into articles;

•	Processing: repackaging;

•	Processing: recycling;

•	Industrial and commercial use as solvent for cleaning and degreasing in vapor degreaser
(batch vapor degreaser - open-top, inline vapor degreaser);

•	Industrial and commercial use as solvent for cleaning and degreasing in vapor degreaser
(batch vapor degreaser - closed-loop);

•	Industrial and commercial use as solvent for cleaning and degreasing in cold cleaners;

•	Industrial and commercial use as solvent in aerosol spray degreaser/cleaner;

•	Industrial and commercial use in adhesives and sealants;

•	Industrial and commercial use in dry cleaning solvents, spot cleaners and stain removers;

•	Industrial and commercial use in liquid cleaners (e.g., coin and scissor cleaner) and liquid
spray/aerosol cleaners;

•	Other industrial and commercial uses: arts, crafts, hobby materials (adhesives accelerant);
automotive care products (engine degrease, brake cleaner, refrigerant flush); anti-adhesive
agents (mold cleaning and release product); electronic and electronic products and metal
products; functional fluids (close/open-systems) - refrigerant/cutting oils; asphalt
extraction; laboratory chemicals; and temperature indicator - coatings;

•	Consumer use as solvent in aerosol spray degreasers/cleaners;

•	Consumer use in spot cleaners and stain removers;

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•	Consumer use in liquid cleaners (e.g., coin and scissor cleaners);

•	Consumer use in liquid spray/aerosol cleaners;

•	Consumer use in arts, crafts, hobby materials (adhesive accelerant);

•	Consumer use in automotive care products (refrigerant flush);

•	Consumer use in anti-adhesives agents (mold cleaning and release product); and

•	Disposal.

The following conditions of use do not drive EPA's unreasonable risk determination for 1-BP:

•	Distribution in commerce; and

•	Commercial and consumer uses of building/construction materials (insulation).

EPA is not making condition of use-specific risk determinations for these conditions of use, is not
issuing a final order under TSCA section 6(i)(l) for these conditions of use, and does not consider
the revised risk determination for 1-BP to constitute a final agency action at this point in time.

Consistent with the statutory requirements of TSCA section 6(a), EPA will propose risk
management regulatory action to the extent necessary so that 1-BP no longer presents an
unreasonable risk. EPA expects to focus its risk management action on the conditions of use that
drive the unreasonable risk. However, it should be noted that, under TSCA section 6(a), EPA is not
limited to regulating the specific activities found to drive unreasonable risk and may select from
among a suite of risk management requirements in section 6(a) related to manufacture (including
import), processing, distribution in commerce, commercial use, and disposal as part of its
regulatory options to address the unreasonable risk. As a general example, EPA may regulate
upstream activities (e.g., processing, distribution in commerce) to address downstream activities
(e.g., consumer uses) driving unreasonable risk, even if the upstream activities do not drive the
unreasonable risk.

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