EPA Proposes Risk Management Rule for 1-Bromopropane

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On August 8, 2024, EPA published a proposed rule to restrict use of the solvent 1-bromopropane (1-BP) (CASRN 106-94-5).  The proposed rule is the result of the agency’s revised 2022 determination that 1-BP presents an unreasonable risk of injury to human health due to effects including neurotoxicity, developmental toxicity, and carcinogenicity.

According to EPA, 1-BP is used in a wide variety of applications, including “vapor degreasing, aerosol degreasing, adhesives and sealants, and in insulation.”  Data from the Chemical Data Reporting rule shows that annual production of the substance, also known as n-propyl bromide, increased from 15.4 to 25.8 million pounds between 2012 and 2015.  This increase was because 1-BP is “an alternative to ozone-depleting substances and chlorinated solvents,” according to a 2020 EPA risk evaluation.

Under the proposed rule, all consumer uses of 1-BP would be banned except for use in insulation.  EPA is also proposing to prohibit four industrial and commercial uses, including use in adhesives and sealants, dry cleaning solvents, and automotive care products.  EPA estimates that these banned uses represent about 3% of the current annual production of 1-BP.

Other industrial and commercial uses would be subject to a workplace chemical protection program (WCPP), which would implement an inhalation exposure concentration limit for 1-BP of 0.05 ppm as an eight-hour time weighted average.  Use of chemically resistant gloves would also be required for uses including manufacturing, processing, and disposal.

Notably, in an effort to protect fenceline communities, EPA is proposing to prohibit owners or operators from increasing releases of 1-BP to outdoor air to comply with WCPP requirements.

EPA is proposing staggered compliance dates for the prohibited uses, which would become effective in six months for manufacturers, nine months for processors, and in 12 months for distribution to retailers.  Non-federal entities subject to the WCPP would be required to conduct baseline airborne exposure testing within six months and ensure that the inhalation exposure limit is met within nine months.

1-BP was added to the Toxics Release Inventory list of reportable chemicals in 2015 and became the first addition to the list of hazardous air pollutants in 2022.  More on 1-BP’s addition to the list can be found in a previous blog post.

Comments on the proposed rule are due September 23, 2024.

EPA Proposes to Designate Five Substances as High Priority

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On July 25, 2024, EPA published a notice proposing to designate a new batch of existing chemicals as high priority substances under section 6 of the Toxic Substances Control Act (TSCA).  TSCA section 6 requires EPA to continually designate existing chemicals as “high-priority” based on factors including hazard and exposure potential.  Once a high priority designation is made, EPA is required to conduct a risk evaluation and regulate the chemical if it is found to present an unreasonable risk.

If the notice is finalized as proposed, EPA would immediately initiate risk evaluations for the following five substances:

  • Vinyl Chloride (CASRN 75-01-4)
  • Acetaldehyde (CASRN 75-07-0)
  • Acrylonitrile (CASRN 107-13-1)
  • Benzenamine (CASRN 62-53-3)
  • 4,4’-methylene bis(2-chloroaniline) (MBOCA) (CASRN 101-14-4)

According to an EPA press release, vinyl chloride is a known human carcinogen linked to liver, brain, and lung cancer in exposed workers.  In the release, EPA stated that vinyl chloride’s health hazards helped motivate the passage of TSCA in 1976.

The press release noted that the other four substances are probable human carcinogens and that some pose other types of hazards, such as respiratory and reproductive harms.  All five substances are used to make plastic; vinyl chloride is mostly used to make polyvinyl chloride, better known as PVC.

EPA announced that it was beginning the process of prioritizing these chemicals in December 2023.  In that announcement, EPA also stated that that it “expects to initiate prioritization on five chemicals every year, which will create a sustainable and effective pace for risk evaluations.”

Comments on the notice are due October 23, 2024.

EPA Proposes to Restrict Use of N-Methylpyrrolidone

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Multiple occupational uses of n-methylpyrrolidone (NMP) would be banned and others would be restricted under a proposed rule published by EPA on June 14, 2024.  The proposed rule follows EPA’s 2020 determination that NMP presents an unreasonable risk to human health due to health effects including fetal death and reduced fertility.

According to the proposed rule, NMP is a widely used solvent with applications in the manufacturing of lithium-ion batteries, “semiconductors, polymers, petrochemical products, paints and coatings, and paint and coating removers.”  2020 Chemical Data Reporting rule data indicates that total annual production ranged from 100–250 million pounds from 2016 to 2019, EPA says.

The proposed rule would ban the manufacture, processing, distribution, and use of NMP for industrial and commercial use in lubricants, anti-freeze products, automotive care products, and cleaning products, among others.  All industrial and commercial uses not prohibited would be subject to a workplace chemical protection program (WCPP) to minimize direct dermal contact with NMP through incorporation of the hierarchy of controls.  Where controls are insufficient, EPA proposes to require implementation of a PPE program.

The proposed rule would also implement prescriptive controls for certain industrial and commercial uses, such as capping the allowed concentration of NMP in industrial and commercial paints and stains at 45%. Similar concentration maximums would apply to a handful of consumer products, including adhesives.

Although no consumer products would be banned, EPA proposes to implement container size limitations and labelling requirements for some consumer uses, including paint removers, paints, automotive care products, and cleaning products.

EPA proposes that the bans take effect under a staggered schedule, varying from one to two years after publication depending on whether an entity is a manufacturer, processor, distributor, or user of NMP.  Private entities subject to WCPP requirements would have one year to establish the program, and consumer product container size limitations and labelling requirements would also take effect after one year.

Comments on the proposed rule are due on July 29, 2024.

EPA Finalizes Changes to TSCA Risk Evaluation Procedures

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On May 3, 2024, EPA published a final rule amending the procedures for chemical risk evaluations under the Toxic Substances Control Act (TSCA).  The final rule is largely unchanged from the proposed rule, discussed in a previous Verdant Law blog post.

A key change in the final rule is the requirement that risk determinations end in a single risk determination rather than use-by-use determinations.  EPA previously referred to this approach as a “whole chemical” approach.  However, to address concerns that a single determination of unreasonable risk would mislead the public into believing that all uses present an unreasonable risk, EPA will no longer use the term “whole chemical.”  EPA additionally committed to “identify[ing] the conditions of use that significantly contribute” to the single determination.

Another important change reverts an EPA interpretation of TSCA to a previous interpretation.  EPA proposed that risk evaluations consider all conditions of use in 2017, but determined that the agency had discretion over conditions of use in the final regulation.  However, due to the Ninth Circuit’s 2019 decision in Safer Chemicals, Healthy Families v. EPA, the final rule now mandates the inclusion of all conditions of use in risk evaluations.

Other changes include the removal of the definitions of “best available science” and “weight of the scientific evidence” to allow the agency greater “flexibility to quickly adapt to and implement advancing scientific practices”; EPA’s decision to no longer assume use of personal protective equipment when calculating occupational exposure; and identification of “overburdened communities” as a potentially exposed or susceptible subpopulation.

The final rule, effective July 2, 2024, will apply to ongoing risk evaluations “only to the extent practicable.”

EPA Publishes Proposed Consent Decrees for Overdue Risk Evaluations

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EPA would be required to complete overdue risk evaluations by new deadlines if two proposed consent decrees, announced by EPA on April 26, 2024, are adopted.

Section 6(b)(4)(G) of the Toxic Substances Control Act (TSCA) requires EPA to complete risk evaluations within three years of initiation, with a six-month extension possible.  EPA has missed this 3.5-year deadline for 22 ongoing risk evaluations.  Twenty of these risk evaluations were initiated in December 2019 as a result of amended TSCA’s requirement that EPA designate 20 existing substances as “high-priority,” which automatically initiated risk evaluations.  The other two, which concern the substances DIDP and DINP, were requested by manufacturers.

The proposed consent decrees would resolve two consolidated lawsuits against the agency.  The first, brought by environmental groups, challenges EPA’s failure to complete all 22 overdue risk evaluations; a previous blog post on that case can be found here.  The American Chemistry Council filed the second, which only concerns the two manufacturer-requested risk evaluations.

Under the proposed consent decrees, linked here and here, EPA would be required to complete:

  • Draft risk evaluations for at least seven of the substances, including 1,3-butadiene, by December 31, 2024;
  • Final risk evaluations for DIDP, DINP, TCEP, formaldehyde, and 1,1-dichloroethane by December 31, 2024;
  • Final risk evaluations for seven of the remaining substances, including 1,3-butadiene, by December 31, 2025; and
  • Final risk evaluations for the remaining 10 substances by December 31, 2026.

Under the proposed decrees, EPA could file a motion to extend a deadline if the agency deems it necessary.  The proposed consent decrees also include a provision automatically extending these deadlines if the agency undergoes a lapse in appropriations.

Since the first lawsuit was filed in September 2023, EPA has completed draft risk evaluations for TCEP (more on that here) and formaldehyde.  However, EPA has yet to release draft risk evaluations for any of the other 22 overdue evaluations.

Comments on the proposed consent decrees are due May 28, 2024.

EPA Proposes to Revise Rules for PBTs DecaDBE and PIP (3:1)

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On November 24, 2023, EPA released a proposed rule to revise the final rules for decabromodiphenyl ether (“decaBDE”) and phenol, isopropylated phosphate (3:1) (“PIP (3:1)”), two persistent, bioaccumulative, and toxic substances (PBTs) subject to regulation under section 6 of the Toxic Substances Control Act (TSCA).

Section 6(h) of TSCA (as amended by the Lautenberg Amendments in 2016) required EPA to take expedited action to complete TSCA section 6(a) rules on certain PBTs.  In January 2021, EPA released final rules for decaBDE, PIP (3:1), and three other PBTs.  The final rules for decaBDE and PIP (3:1) generally prohibit their manufacture, processing, and use beginning in March 2021, though the rules contained phased-in prohibitions and exclusions for certain uses; EPA has extended certain phased-in prohibitions for PIP (3:1) multiple times since.

In light of new information and the Agency’s reinterpretation of the directive in TSCA section 6(h)(4) to “reduce exposures to the substance to the extent practicable,” EPA is proposing revisions to the final rules for decaBDE and PIP (3:1).  For decaBDE, the proposed revisions include:

  • Requiring a label on existing plastic shipping pallets containing decaBDE,
  • Requiring use of PPE for certain activities involving decaBDE,
  • Prohibiting releases to water during the manufacturing, processing, and commercial distribution of decaBDE and decaBDE-containing products,
  • Extending the current compliance extension for the processing and distribution in commerce of decaBDE-containing wire and cable insulation for use in nuclear power generation facilities, and
  • Requiring export notification for decaBDE-containing wire and cable for nuclear power generation facilities.

The proposed revisions to the PBT rule for PIP (3:1) include:

  • Narrowing the exclusion of prohibition for PIP (3:1) use in lubricants and greases to only include use in aerospace and turbine applications,
  • Replacing the exclusion from prohibition for motor and aerospace vehicle parts containing PIP (3:1) with phased-in prohibitions,
  • Excluding from prohibition the processing and commercial distribution of PIP (3:1) and PIP (3:1)-containing products for use in wire harnesses and circuit boards, and
  • Requiring PPE during manufacturing and processing of PIP (3:1).

In the proposed rule, EPA states that the Agency is not reconsidering the final rules for the other three PBTs–2,4,6-TTBP, HCBD, and PCTP–subject to final rules in January 2021.

According to EPA, decaBDE is a flame retardant that is used in textiles, plastics, adhesives, and polyurethane foam, and PIP (3:1) is a flame retardant, a plasticizer, and an anti-compressibility and anti-wear additive used in lubricants, hydraulic fluids, and in the manufacture of other compounds.

EPA Issues Draft Risk Evaluation for Flame Retardant TCEP

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EPA has preliminarily determined that tris(2-chloroethyl) phosphate (TCEP) presents an unreasonable risk to human health and the environment, according to its draft risk assessment of the flame retardant released on December 14, 2023.  Animal testing data revealed that exposure to TCEP may increase risk of kidney cancer and other cancers, and could harm neurological and reproductive systems, the draft states.

According to EPA, domestic production of TCEP has decreased by about 99 percent since 2014.  However, the agency notes that TCEP is still used in paints, coatings, and in certain aerospace applications, and that previously-manufactured products containing TCEP—such as fabrics, certain types of foam, and construction materials—may still be in use.  The draft also states that “TCEP may still be found in a wide range” of imported goods.

Because TCEP is mixed into materials rather than being chemically bonded, it can leach out of products, EPA said.  Infant and child exposure from mouthing consumer products containing TCEP was determined to present an unreasonable risk.  The agency also found unreasonable risk of health effects for breastfed infants, people who handle TCEP at work, people who inhale TCEP dust off consumer products, and people who eat TCEP-contaminated fish.

EPA determined that TCEP presents an unreasonable risk to the environment due to studies on chronic exposures in fish and sediment-dwelling organisms.  The draft identified a number of ways by which TCEP can enter the environment, including manufacturing processes, air emissions, and leaching from products and landfills.  Although TCEP is not considered bioaccumulative, it is persistent in the environment, EPA said.

The draft risk evaluation is open for public comment and will undergo peer review by independent scientific and technical experts starting in March 2024.  If EPA still concludes that TCEP presents an unreasonable risk after public comment and peer review, the Toxic Substances Control Act requires the agency to take steps to mitigate its risks.

EPA Proposes TCE Ban

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EPA has released a proposed rule, which, if implemented, would ban the use of trichloroethylene (“TCE”). The substance has numerous industrial, commercial, and consumer applications, including uses in vapor and aerosol degreasing and as lubricants, greases, adhesives, and sealants. Earlier this year, in its final revision to the TCE risk evaluation conducted under section 6(b) of the Toxic Substances Control Act (“TSCA”), EPA concluded that TCE presents an unreasonable risk of injury to human health due to both its carcinogenic and non-carcinogenic health effects including liver and kidney toxicity, and neurotoxicity. The risk evaluation found these effects resulted from both acute and chronic exposures and through all types of exposures, including inhalation and dermal exposure. TSCA section 6(a) requires EPA to impose restrictions on the manufacture, including import, processing, and distribution of substances that present an unreasonable risk of injury to human health or the environment.

The ban would apply to all manufacturing, import, processing, and distribution in commerce of TCE for all industrial and commercial uses. The rule would go into effect one year following the effective date of the final rule for consumer products and most commercial uses. Some commercial and industrial uses would have longer phaseout timelines and set exemption periods. (The difference between phaseouts and exemptions is that phaseouts are active timelines for the elimination of use, whereas the exemptions do not require current action to eliminate the use of TCE by a certain date; presumably, a determination will be made prior to the exemption period ending that will clarify if the exemption is to be extended or if a phaseout period will be established.)

TSCA section 6(g) allows EPA to grant an exemption from a requirement of a rule banning or restricting a chemical substance for a specific condition of use of a chemical substance if the Administrator finds that the specific condition of use is critical or essential and has no technically and economically feasible safer alternative. The phaseout and exemptions in the proposed rule are narrow in scope. They include the following:

  • An 8.5-year phaseout for the manufacture and processing of TCE as an intermediate in the manufacturing of hydrofluorocarbon134a (HFC-134a). HFC-134a is essential to the operation of refrigeration and air conditioning systems.
  • A 10-year phaseout for the manufacture and use of TCE as a solvent for closed-loop batch vapor degreasing for rayon fabric scouring for end use in the production of rocket booster nozzles. This exemption is limited to production by federal agencies and their contractors.
  • A 10-year TSCA Section 6(g) exemption for the manufacture and processing of TCE as a processing aid for battery separator manufacturing, battery separators are used to prevent short-circuiting in lithium-ion batteries.
  • A 50-year TSCA Section 6(g) exemption for the manufacture, processing, distribution in commerce, and use of TCE as a laboratory chemical for essential laboratory activities such as those associated with ongoing environmental cleanup projects under the CERCLA program and other EPA authorities, and some research and development activities being conducted by U.S. Federal Agencies including NASA.

The rule would also require strict workplace controls for those working with TCE for the uses allowed by the proposed rule.  These workplace controls would be detailed in EPA’s proposed  Workplace Chemical Protection Program (“WCPP”). To further reduce worker risks, the proposed rule would prohibit the disposal of TCE to industrial pre-treatment, industrial treatment, or publicly owned treatment works.

Under this rule, manufacturers, importers, processors, and distributors (excluding retailers) of TCE and TCE-containing products must provide downstream notification of the TCE prohibition. EPA is asking for comments on timeframes for downstream notification and recordkeeping requirements. EPA is proposing a two-month period for manufacturers and a six-month period for processors and distributors to make the required SDS changes. This notification will be provided through Safety Data Sheets (“SDS”). The suggested SDS language is stated within the proposed rule.

Violations of the rule will be subject to TSCA section 16, which permits civil and criminal penalties, including a civil penalty of up to $46,989 per day for each violation of TSCA or TSCA rules. Comments on the proposed rule are due December 15, 2023.

EPA Proposes Changes to TSCA Risk Evaluation Procedures

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On October 30, 2023, EPA published a proposed rule altering the procedures for chemical risk evaluations under section 6 of the Toxic Substances Control Act (TSCA). The proposed rule revises the existing 2017 framework, which was adopted one year after Congress passed amendments to TSCA requiring EPA to evaluate whether existing chemicals that have been identified as “high priority” present an unreasonable risk of injury to health or the environment.

The rulemaking includes the following proposed changes:

  • The clarification that EPA will include all conditions of use (i.e., circumstances under which the chemical is “intended, known, or reasonably foreseen to be manufactured, processed, distributed in commerce, used, or disposed of”) in the scope of a risk evaluation.
  • The inclusion of all exposure pathways in the scope of a risk evaluation. EPA previously excluded exposure pathways covered under other EPA statutes in its risk evaluations for the first ten chemicals.
  • The removal of the definitions for “best available science” and “weight of the scientific evidence.” Though TSCA requires EPA to use the best available science and make decisions based on the weight of the scientific evidence at 15 U.S.C. 2625, EPA argues that the codification of these definitions inhibits the Agency’s ability to adapt to changing science.
  • The requirement that EPA make a single determination on whether the chemical presents an unreasonable risk. EPA initially made separate risk determinations for each condition of use in its risk evaluations for the first ten chemicals but later issued revised “whole substance” determinations.
  • The cessation of the consideration of “assumed” personal protective equipment (PPE) use when calculating exposure reduction due to PPE.
  • The addition of “overburdened communities” to the list of examples of potentially exposed or susceptible subpopulations.
  • A number of alterations to the process and requirements for manufacturer-requested risk evaluations.

The above changes would apply to all risk evaluations initiated on or after the date of the final rule.  For risk evaluations in progress on the date of the final rule, EPA expects to apply the changes “only to the extent practicable.”

The proposed clarification that EPA includes all conditions of use in the scope of a risk evaluation stems from the Ninth Circuit’s 2019 decision in Safer Chemicals, Healthy Families v. EPA. In the case, petitioners successfully challenged EPA’s exclusion of “legacy uses and associated disposals”—such as the use and future disposal of asbestos in previously installed insulation—from the scope of risk evaluations. Several of the other proposed changes would codify existing EPA practices introduced in 2021, including the requirement that risk evaluations end with a single determination rather than use-by-use determinations.

EPA requests public comments on all aspects of the proposed rulemaking. Comments are due on December 14, 2023.

EPA Releases Draft Supplement for 1,4-Dioxane

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In July 2023, EPA announced the release of a draft supplement to the Risk Evaluation for 1,4-dioxane for public comment and peer review.  1,4-dioxane is solvent used to manufacture other chemicals such as adhesives and sealants.  It is also used as a processing aid and laboratory chemical. In addition, some manufacturing processes, such as the process used for making commercial and consumer dish soaps, result in the chemical being present as a byproduct.

The draft supplement focuses on air and water exposure pathways that were not included in the 2020 Risk Evaluation.  The 2020 Risk Evaluation focused on health risks to workers, consumers, and the general public, but not from drinking water, the air, or exposure where 1,4-dioxane is present as a byproduct.  The omission was identified by the Scientific Advisory Committee on Chemicals (SACC) as an oversight.  The SACC informed EPA that failure to assess the risks posed to the general population from exposure to the chemical may present a risk to human health – with an emphasis on drinking water as an exposure pathway.

The draft supplement identified cancer risk estimates higher than 1 in 10,000 for 1,4-dioxane present as a byproduct and higher than 1 in 1 million for general population exposure scenarios associated with 1,4-dioxane in drinking water sourced downstream of release sites and in air within 1 km of releasing facilities.

The draft supplement did note that the risk estimates include inherent uncertainties and the overall confidence in specific risk estimates fluctuates.  However, the document also stated that the information is beneficial in helping the Agency make a determination on whether the chemical poses an unreasonable risk to people with occupational exposure, through sources of drinking water, and breathing air near release sites.