EPA Sued Over Delayed Risk Evaluations

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Environmental groups have filed a lawsuit against EPA for failing to complete risk evaluations for 22 substances that may cause harm to humans and the environment.

Under section 6 of the Toxic Substances Control Act, EPA is required to conduct risk evaluations on “high priority” existing substances to determine whether they pose an unreasonable risk to human health or the environment.  Section 6(b)(4)(G) requires EPA to complete risk evaluations “as soon as practicable, but not later than 3 years after” they are initiated, with a one-time six-month extension possible.

According to the complaint, EPA missed this statutory 3.5-year deadline for 22 ongoing risk evaluations which were initiated in 2019 and early 2020.  Plaintiffs allege that this delay harms their members, staff, and children by prolonging their exposure to substances with serious health risks and by depriving them of information about their exposures.

The complaint seeks declaratory and injunctive relief, requesting that the U.S. District Court for the District of Columbia set deadlines for EPA to complete the risk evaluations.

The case is Community In-Power and Development Association v. EPA, No. 1:23‑cv‑02715-DLF.

EPA Proposes Ban on Perchloroethylene

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Using its authority under the Toxic Substances Control Act (TSCA), EPA has released a proposed rule to ban the use of perchloroethylene (“PCE”) for most commercial and industrial uses. (PCE is also referred to as perc and tetrachloroethylene.) PCE is used in a number of applications and industries, including petroleum manufacturing, aerosol degreasing, and dry cleaning.

The proposed rule follows the Agency’s assessment of the risk to human health presented by the substance. EPA conducted a risk evaluation of the substance under TSCA section 6(b). That assessment determined that PCE, as a whole chemical substance, presents an unreasonable risk of injury to human health as PCE exposure causes a variety of adverse health effects. PCE is a known carcinogen; it also causes neurotoxicity, including impaired visual and cognitive function. Various other health effects were noted by the risk evaluation, including central nervous system depression, kidney and liver effects, immune system toxicity, and developmental toxicity.

Under TSCA section 6(a), EPA is required to address, by rule, any unreasonable risk of injury to health or the environment found during a TSCA risk evaluation. Section 6(a) also requires the Agency to identify actions necessary to ensure the chemical does not continue presenting an unreasonable risk by either a) implementing “a requirement [either] prohibiting or otherwise restricting the manufacturing, processing, or distribution in commerce of such substance or mixture,” or b) “limiting the amount of such substance or mixture which may be manufactured, processed, or distributed in commerce.” To meet these requirements, EPA is proposing to prohibit the manufacture, import, processing, and distribution of PCE for a number of commercial and consumer uses, such as in dry cleaning, spot-cleaning operations and degreasing. The prohibition allows a 10-year phaseout period.

The Agency will still permit limited use of PCE for some uses, particularly those which help its efforts in addressing climate-damaging hydrofluorocarbons (an initiative happening under the American Innovation and Manufacturing Act of 2020). PCE will also be used in uses that are important for national security applications or to meet other critical national needs. In these cases, EPA would require the implementation of a PCE workplace chemical protection program. The chemical protection program would include requirements to meet an inhalation exposure concentration limit and prevent direct dermal contact. The Agency has also put forward prescriptive requirements for laboratory use, recordkeeping, and downstream notification.

EPA will permit certain time-limited exemptions from the ban for certain critical or essential emergency uses of PCE when no alternative is technically or economically feasible safer alternative is available.

EPA Proposes Methylene Chloride Ban

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On April 20, 2023, EPA released a proposed rule under Section 6(a) of the Toxic Substances Control Act (“TSCA”) that would drastically limit the use of methylene chloride. Section 6(a) of the statute provides EPA authority to ban or restrict the manufacture, processing, distribution, and use of chemical substances that pose an unreasonable risk of injury to human health or the environment. EPA explains that its decision is driven by concerns about the risks posed to workers, occupational non-users, consumers, and individuals in close proximity to consumer usage. The Agency stated that it is particularly concerned about adverse health effects such as neurotoxicity, liver damage, and cancer resulting from inhalation and dermal exposure to methylene chloride.

EPA’s proposed rule seeks to “rapidly phase down” the manufacturing, processing, and distribution of methylene chloride for consumer use, as well as most industrial and commercial uses. The phase down is expected to be completed within 15 months of the effective date of the final rule. EPA’s analysis indicates that alternative products with similar cost and effectiveness to methylene chloride are generally available for most of the that the Agency intends to prohibit.

According to EPA, methylene chloride poses an unreasonable health risk, without considering costs or other non-risk factors, including an unreasonable risk to potentially exposed or vulnerable subpopulations identified as relevant in the 2020 methylene chloride risk evaluation, under specific conditions of use (“COU”). (EPA defines COU as the circumstances in which a chemical substance is intended, known, or reasonably foreseen to be manufactured, processed, distributed in commerce, used, or disposed of.) To address the unreasonable risk, EPA proposes the following restrictions:

  • Prohibit the manufacture, processing, and distribution of methylene chloride for all consumer use.
  • Prohibit most industrial and commercial uses of methylene chloride.
  • Enforce a workplace chemical protection program (“WCPP”) that includes inhalation exposure concentration limits, workplace exposure monitoring, and exposure controls for ten specific conditions of use of methylene chloride.
  • Require recordkeeping and downstream notification requirements for the manufacturing, processing, and distribution of methylene chloride in commerce.

The rule does provide an exemption to the prohibition on industrial uses for ten years for civilian aviation uses to prevent significant disruptions to critical infrastructure. This exemption will be subject to conditions such as compliance with the WCPP.  An exemption is also provided for emergency use of methylene chloride in support of the National Aeronautics and Space Administration’s mission. The exemption is limited to specific critical or essential conditions when no technically and economically feasible safer alternatives are available. This exemption will also require compliance with the WCPP. It too is time-limited to ten years.

EPA clarified that all COUs of methylene chloride under TSCA (except its use in consumer paint and coating removers, which was previously addressed under TSCA Section 6) will be covered by this proposal.

Regarding the WCPP for methylene chloride, EPA’s press release states that the agency collaborated with the Occupational Safety and Health Administration (OSHA) during the development of the proposed rule, taking into account existing OSHA requirements to ensure comprehensive worker protections. The Agency asserts that the proposed risk-based limits are based on up-to-date data and fulfill the TSCA mandate to eliminate unreasonable risks. If the rule is finalized, employers would have one year to comply with the WCPP and would be obligated to periodically monitor the workplace to ensure that workers are not exposed to methylene chloride at levels that pose an unreasonable risk.

In the Federal Register notice, EPA particularly requested comments on the feasibility and effectiveness of the proposed worker protection requirements from parties that would be responsible for implementing the program. (The comment period closed on July 3.) Additionally, EPA hosted a public webinar on June 7 to present overview of the proposed regulatory action and provide an opportunity for participation in discussion on the proposed WCCP. Materials from the webinar are available on EPA’s website.

EPA Finds TCE as a Whole Chemical Substance an Unreasonable Risk to Human Health

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Earlier this year, EPA announced the final revision to the risk determination for trichloroethylene (TCE) risk evaluation issued under the Toxic Substances Control Act (“TSCA”). EPA found that TCE presents unreasonable risks to the health of workers, occupational non-users, consumers, and bystanders. The risks identified include adverse human health effects unrelated to cancer, such as neurotoxicity and liver effects, from acute and chronic inhalation and dermal exposures to TCE and risks for cancer from chronic inhalation and dermal exposures to TCE. The revised risk determination supersedes the conditions of use (“COU”) specific “no unreasonable risk” determinations that the EPA previously issued in its 2020 TCE risk evaluation.

TCE is a volatile organic compound (“VOC”) used mostly in industrial and commercial processes. Consumer uses include cleaning and furniture care products, arts and crafts, spray coatings, and automotive care products like brake cleaners. EPA determined that 52 of the 54 COUs evaluated drive the unreasonable risk determination.

EPA states that it used the whole chemical risk determination approach for TCE because there are benchmark exceedances for multiple COUs spanning across most aspects of TCE’s life cycle, from manufacturing (including import), processing, commercial use, consumer use, and disposal for health of workers occupational non-users (workers nearby but not in direct contact with this chemical), consumers, and bystanders. EPA holds that this approach is appropriate because the health effects associated with TCE exposures are “severe and potentially irreversible,” including developmental toxicity, reproductive toxicity, liver toxicity, kidney toxicity, immunotoxicity, neurotoxicity, and cancer. EPA notes that the revised risk determination for TCE does not reflect an assumption that workers always and appropriately wear personal protective equipment (PPE). EPA states that as it moves forward with a risk management rulemaking for TCE, it will “strive for consistency with existing OSHA requirements or best industry practices when those measures would address the identified unreasonable risk.

Additionally, EPA stated it is conducting a screening-level approach to assess potential risks from the air and water pathways for several of the first 10 risk evaluation chemicals, including TCE. The goal of the screening approach is to evaluate the surface water, drinking water, and ambient air pathways for TCE that were excluded from the 2020 risk evaluation and to determine if there are risks that were unaccounted for in that risk evaluation. EPA expects to describe its findings regarding the chemical-specific application of this screening-level approach in its proposed risk management rule for TCE.

EPA Releases Proposed Approach for Considering Cumulative Risks Under TSCA

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EPA recently released two documents regarding cumulative risk assessments under TSCA section 6, Draft Proposed Principles of Cumulative Risk Assessment Under the Toxic Substances Control Act, and Draft Proposed Approach for Cumulative Risk Assessment of High-priority Phthalates and Manufacturer-Requested Phthalate under the Toxic Substances Control Act. The first document details a set of principles for evaluating the cumulative risk of substances under TSCA; the second document presents a proposed approach for applying those principles to the evaluation of the cumulative risk posed by certain phthalate chemicals which are currently undergoing TSCA section 6 risk evaluation.

In the  Draft Proposed Principles of Cumulative Risk Assessment Under TSCA, EPA explained that it plans to alter its approach to individual substance evaluations under TSCA section 6 by taking a cumulative assessment approach when appropriate. Previously, the Agency looked at the risks posed by a single substance under its specific conditions of use. The Agency now intends to implement a new approach to evaluating human health effects, which it believes is more appropriate when considering human exposure to these substances. People are often exposed to many chemical substances with similar effects at the same time, and looking at the combined exposure health risk will paint a more complete picture. The Agency believes that this approach will allow for more effective mitigation of identified unreasonable risks and provide particularly useful information for communities that face higher than normal levels of chemical pollution.

Phthalates will be subjected to a cumulative risk assessment because the group of substances has similar effects on human health and has generally been found concurrently in the human body. The phthalates to be assessed as a group include DEHP, BBP, DBP, DIBP, DCHP, DINP, and DIDP. The chemical group is often used in industrial and consumer products to make plastics more flexible and durable. The draft proposal requests comment and peer review on its assessment that six phthalate substances are toxicologically similar, and the U.S. population is frequently co-exposed to these substances, making a cumulative risk assessment the most appropriate course of review action under TSCA.

The Agency is accepting comments on these documents through April 28, 2023.

EPA Releases Draft Revised Risk Determination for PV29

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On March 7, 2022, EPA released a draft revision to the risk determination for C.I. Pigment Violet 29 (PV29).  Manufacturers and commercial clients use PV 29 as a weather fast and heat stable pigment in paints and coatings.  These paints and coatings are primarily used in automobiles and industrial carpeting.  The draft revision comes as part of the path forward EPA released in June 2021 for the first 10 risk evaluations under TSCA.

Risk evaluations are conducted under TSCA section 6.  TSCA requires the Agency to conduct risk evaluations to determine whether high priority substances present an unreasonable risk of injury to health or the environment.  EPA has determined that PV29, presents an unreasonable risk of injury to health.  This determination regarding PV29, evaluated the substance as a “whole chemical,” replaces previous determinations which were based on evaluations of individual conditions of use.

The draft revision risk determination for PV29 does not include an assumption of personal protective equipment (PPE) for workers. Instead, EPA stated that the Agency would consider the use of PPE, and any other potential mitigating factors, during its determination of risk management measures.  Note that the January 2021 risk evaluation for PV29found an unreasonable risk to workers, even when proper use of PPE is assumed.  The January 2021 risk evaluation identified 14 categories of use and found unreasonable risk exists in 10 of those categories including:

  • manufacture,
  • processing,
  • paints/coatings and merchant ink for commercial printing categories of Industrial/commercial use, and
  • disposal.

The draft revision states these same conditions of use will continue to drive EPA’s determination of unreasonable risk for PV 29.  The categories of use that were not found to present an unreasonable risk are: distribution in commerce, industrial/commercial use in plastic and rubber products, and consumer uses.

EPA Releases Final Scope Document for Manufacturer-Requested Risk Evaluation of D4

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On March 7, 2022, EPA published the final scope of the risk evaluation for octamethylcyclotetra-siloxane (D4). This risk evaluation may affect producers of goods comprised of and/or utilizing the following: adhesives, sealants, synthetic rubber, electrical equipment, appliances, paint, ink/toner, aircraft maintenance components, automotive care components, cleaning products, fabrics/textile products. This is not intended to serve as an exhaustive list. The publication of this risk evaluation originated from a request made by the American Chemistry Council’s Silicones Environmental, Health, and Safety Center (SEHSC). The scoping document addresses conditions of use, exposures, hazards, and potentially exposed or susceptible subpopulations.

Conditions of Use

Conditions of use for D4 risk evaluation can be sub-divided into the following life cycle stages: manufacturing, processing, distribution in commerce, industrial use, commercial uses, consumer uses, and disposal. EPA’s evaluation will address each of the aforementioned life cycle stages. Notably, processing is the most nuanced of these stages. Specifically, the processing stage is comprised of three subcategories: processing as a reactant; incorporation into formulation, mixture, or reaction product; and repackaging.

Exposures

In the forthcoming risk evaluation, EPA will evaluate human and environmental exposures as well as releases into the environment resulting from these conditions of use identified in the scoping document. The evaluation will contemplate the physical and chemical properties of D4; environmental fate and transport processes, exposure pathways, and potential human and environmental receptors; releases to the environment; environmental exposures (both aquatic and terrestrial); occupational exposures; consumer exposures; and general population exposures.

Hazards

Regarding environmental hazards, EPA will assess the following potential hazard effects of D4 to aquatic and terrestrial organisms including: absorption, distribution, metabolism, and excretion (collectively referred to as “ADME”), developmental, gastrointestinal, mortality, neurological, nutritional, metabolic, reproductive, and respiratory. The scoping document notes that D4 can degrade into dimethylsilanediol (DMSD) under certain environmental conditions. Accordingly, EPA has indicated that it may factor toxicity information regarding DMSD into its risk evaluation.

With respect to human health hazards, EPA intends to examine the relation of D4 exposure to the following: ADME, cancer, endocrine, gastrointestinal, hematological, immunology, hepatic, mortality, neurological, nutritional/metabolic, ocular/sensory, renal, reproductive, developmental, respiratory, and skin/connective tissue. The scope of EPA’s assessment of the human health hazards of D4 may also contemplate hazards associated with exposure to DMSD as mentioned above.

Potentially Exposed or Susceptible Subpopulations (PESS)

In accordance with the requirement of TSCA section 6, the following groups will be considered potentially exposed or susceptible subpopulations in the D4 risk evaluation: children, women who may become pregnant, workers, occupational non-users (ONU), consumers, bystanders, fence line communities, and indigenous and native populations. Environmental justice considerations will also be factored into the PESS analysis. These considerations will follow the best practices discussed within EPA’s Technical Guidance for Assessing Environmental Justice in Regulatory Analysis.

PIP (3:1) Compliance Date Extended to October 31, 2024

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On January 6, 2021, EPA issued a rule limiting manufacturing, importing, processing, and distribution of products containing phenol, isopropylated phosphate (3:1) (PIP (3:1)).  That rule was scheduled to take effect on February 5, 2021, with a March 8, 2021, compliance date.  After this date, companies would be prohibited from processing and distributing PIP (3:1) and PIP (3:1)-containing products unless there was an applicable exclusion.  Furthermore, after the compliance date, the rule prohibited the release of PIP (3:1) into water during manufacturing, processing, and distribution.  This final rule also required commercial users to follow existing regulations and best practices to prevent the release of PIP (3:1) and products containing PIP (3:1) into water.  On March 8, 2022, the effective compliance date of the rule was extended to October 3, 2024.

The March 2022 extension applies to the following consumer and commercial goods: cellular telephones, laptop computers, electronic devices, and industrial and commercial equipment used in various sectors including transportation, life sciences, and semiconductor production.  Notably, this is not an exhaustive list of the goods affected by the rule.  This extension follows the publication of the initial rule in January 2021, no action assurance issued in March 2021, and the September 2021 extension which expired on March 8, 2022.  These milestones are discussed in greater detail below.

In January 2021, EPA released risk management rules under the Toxic Substances Control Act (TSCA) intended to mitigate exposure to five chemicals that are persistent, bioaccumulative and toxic (PBT).  The five chemicals listed under this rule are decabromodiphenyl ether (DecaBDE); phenol, isopropylated phosphate (3:1) (PIP (3:1)); 2,4,6-tris (tert-butyl) phenol (2, 4, 6-TTBP); hexachlorobutadiene (HCBD); and pentachlorothiophenol (PCTP).  The rules were designed to either limit or prohibit manufacturing, importing, processing, and distributing the aforementioned chemicals.  Following the publication of these rules, EPA received numerous comments from manufacturers and processors of PIP (3:1) asserting that the March 8, 2021, compliance date did not provide stakeholders with enough time to find viable chemical substitutes.  Consequently, on March 8, 2021, EPA provided a no action assurance letter on enforcement of the rule.  The no action assurance expired on September 4, 2021.  Subsequently, on September 17, 2021, EPA issued a short-term extension of specific compliance deadlines for the processing and distribution of PIP (3:1) and articles containing PIP (3:1) to March 8, 2022. On March 8, 2022, a further extension was granted, which moved the compliance deadline to October 31, 2024.

EPA Announces Improvements to the TSCA Risk Evaluation Process  

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On December 20, 2021, EPA released a draft TSCA Systematic Review Protocol. In its announcement on the new Protocol, the Agency explained that the Protocol will strengthen EPA’s approach to reviewing and selecting the scientific studies that are used to inform TSCA Risk Evaluations and ensure that EPA has the best tools under TSCA to protect human health and the environment.  The draft protocol comprises nearly 700 pages.

The draft Protocol notes that EPA’s Office of Pollution Prevention and Toxics (OPPT) applies systematic review principles in the development of its Risk Evaluations of existing chemicals.  It provides specific systematic review approaches which they use for identifying and evaluating evidence for the hazard and exposure assessments that support Risk Evaluations. OPPT added that the draft Protocol responds to key recommendations received from the National Academies of Sciences, Engineering, and Medicine (NASEM).

The Protocol was developed in response to NASEM’s critique that EPA had not previously documented how TSCA prioritization and problem formulation relate to the TSCA Systematic Review.  The Protocol aligns the TSCA prioritization and scoping processes with the steps of the Protocol.  In addition, the Protocol defines how EPA’s systematic review efforts will identify data gaps and data needs in the Risk Evaluations process.  OPPT explains that identifying these data gaps and data needs will provide the Agency with the information it needs “to strategically exercise TSCA authorities to require testing or information collection for use in TSCA prioritization and Risk Evaluation.”

The Protocol reports that for the 20 high-priority substances currently undergoing Risk Evaluation and substances undergoing manufacturer-requested Risk Evaluation, EPA has implemented a new, unified literature search process.  This process, as described in the Protocol, uses chemical identifiers to maximize the capture of relevant literature, which in turn provides consistency and efficiency to the literature search.  In addition, OPPT announced that the Protocol includes new methods to reduce bias and improve evaluation through the use of calibration exercises and data evaluation training for reviewers.  This is a response to NASEM recommendations, SACC comments, and public comments.

In addition, the Protocol includes a description of the evidence integration process.  A step that was not part of the 2018 TSCA systemic review document. This addition was also made in response to recommendations by the NASEM and the SACC. OPPT explains that the Protocol’s evidence integration approach relies on methods related to those in EPA’s IRIS Handbook.

The draft protocol will undergo peer review by at a meeting of the SACC on April 19-21, 2022.  OPPT noted that the agency will use this feedback to further improve the document. The date, time for the public peer review virtual meeting will be announced on the SACC website.

EPA Releases Final Scope Documents Under New Policy

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On August 31, 2021, EPA released Toxic Substance Control Act (TSCA) final scope documents for diisodecyl phthalate (DIDP) and diisononyl phthalate (DINP).  The final scope documents are the first to implement the Agency’s new policy for considering exposure to the chemicals from media that are regulated outside of TSCA including air and water, including drinking water.  In a press release on the path forward for risk evaluations, the Agency noted that the previous administration’s “…approach to exclude certain exposure pathways also resulted in a failure to consistently and comprehensively address potential exposures to potentially exposed or susceptible subpopulations, including fence-line communities (i.e., communities near industrial facilities).”  Both risk evaluations were requested by the manufacturer, ExxonMobil, through the American Chemistry Council’s High Phthalates Panel (ACC HPP).

The scope documents for these risk evaluations includes the following information: the conditions of use, potentially exposed or susceptible subpopulations (PESS), hazards, and exposures that EPA plans to consider, along with a description of the reasonably available information and science approaches EPA plans to use in the risk evaluations, a conceptual model, an analysis plan, and the plan for peer review of the draft risk evaluation for this category of chemical substances.

Some of these conditions of use were identified in the manufacturer request as circumstances on which EPA was requested to conduct a risk evaluation. EPA identified other conditions of use from information reported to EPA through Chemical Data Reporting (CDR), published literature, and consultation with stakeholders for both uses currently in production and uses whose production may have ceased

EPA plans to evaluate releases to the environment as well as human and environmental exposures resulting from the conditions of use of these substances that EPA plans to consider in the risk evaluation.  In addition to including occupational exposure, consumer and bystander exposure, and PESS, the scope of the risk evaluations will include general population exposures.  Specifically, EPA plans to evaluate general population exposure to the substances via the oral route from drinking water, surface water, groundwater, ambient air, soil, fish ingestion, and human breast milk; via the inhalation route from air and drinking water; and via the dermal route from contact with drinking water, surface water, groundwater and soil.

In addition to considering the data and information sources provided by the ACC HPP submissions, EPA conducted a comprehensive search to identify and screen multiple evidence streams (i.e., chemistry, fate, release and engineering, exposure, hazard) to inform the development of these scoping documents.