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 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.

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 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.

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.

Manufacturer Request for Risk Evaluation of OTNE

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On November 20, 2020, EPA received a manufacturer request for risk evaluation for the chemical substances in the octahydro-tetramethyl-naphthalenyl-ethanone chemical category (OTNE).  These substances are used as fragrance ingredients.  The three manufacturers, International Flavors and Fragrances, Inc., Privi Organics USA Corporation, and DRT America, Inc., sent the request through the OTNE Consortium.

The risk evaluation request applies to four chemicals within OTNE.  The Toxic Substances Control Act (TSCA) considers two of the chemicals to be persistent, bioaccumulative and toxic (PBT) chemicals.  While completing the risk evaluation for the OTNE chemical, EPA is not allowed to consider costs or other non-risk factors (15 U.S.C. 2605(b)(4)(F)(iii)).  The request for evaluation also includes possible conditions of use for EPA to identify.

EPA has until no later than June 5, 2021 to either grant or deny the request to conduct the risk evaluation for the OTNE chemicals.  In order for EPA to grant the request, it must meet all of the requirements listed under 40 CFR 702.37(e)(6)(ii).  These conditions are that the request constitutes conditions of use that warrant inclusion in a risk evaluation, EPA has all the necessary information to conduct the risk evaluation, and all the remaining criteria of 40 CFR 702.37 are met, such as manufacturers paying fees to support the risk evaluations.

Systematic Review for TSCA Risk Evaluations

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On May 31, 2018 EPA released  Application of Systematic Review in TSCA Risk Evaluations.  The document presents a detailed description of EPA’s approach to the Risk Evaluations required by the Lautenberg amendments to TSCA.

The announcement by the Office of Pollution Prevention and Toxics (OPPT) explains that “[it] will guide EPA’s selection and review of studies in addition to providing the public with continued transparency regarding how the Agency plans to evaluate scientific information.”  In the document OPPT explains that the Agency intends to apply systematic review principles in the development of the risk evaluations required by the amended statute. The Application of Systematic Review in TSCA Risk Evaluations will serve as internal guidance for this process.  The document describes OPPT’s plan for identifying, evaluating and integrating evidence for the TSCA risk evaluation process.

The document includes chapters on scoping and problem formulation, integration of systematic review principles into TSCA risk evaluations, and appendices on strategy for assessing the quality of data supporting TSCA risk evaluations and data quality criteria for each of the categories of information considered in the evaluation (e.g., physical/chemical property data, occupational exposure and release data).  The Agency notes that this document is not necessarily applicable to risk assessments developed to support other EPA’s statutes or programs.  EPA invites the public to provide input on this document at www.regulations.gov, docket# EPA-HQ-OPPT-2018-0210.

For the risk evaluations, OPPT will first conduct scoping and problem formulation to develop an analytical framework.   Problem formulation will describe the exposure pathways, receptors and health endpoints that OPPT expects to consider in the risk evaluations.

The Agency will use “systematic review“ for problem formulation and the other stages of the risk evaluation process.  The Application of Systematic Review in TSCA Risk Evaluations explains that the risk evaluation process will rely on the National Academy of Sciences, Institute of Medicine’s definition of systematic review:  “a scientific investigation that focuses on a specific question and uses explicit, pre-specified scientific methods to identify, select, assess, and summarize the findings of similar but separate studies.”  OPPT reports that key elements of systematic review include:

  • A clearly stated set of objectives defining the research question,
  • Developing a protocol that describes the specific criteria and approaches that will be used throughout the process,
  • Applying the search strategy in a literature search,
  • Selecting the relevant papers using predefined criteria,
  • Assessing the quality of the studies using predefined criteria,
  • Analyzing and synthesizing the data using the predefined methodology, and
  • Interpreting the results and presenting a summary of findings.

Following problem formulation, OPPT will develop a protocol to specify the criteria, methods for data collection, data evaluation and data integration.

Data will be collected under a defined literature search strategy designed to collect information to evaluate the full life cycle of the chemical substance including exposure, human health hazard, and environmental hazard.  OPPT will use a comprehensive chemical-specific literature search of the open literature to identify relevant data.  OPPT will also use data that are submitted by the public and peer reviewers.  In addition, OPPT will search its internal databases for relevant data submitted under TSCA.  The Agency notes that data submitted under TSCA will be used in the risk evaluation whether or not they are claimed as confidential business information (CBI).  However, CBI data will be used in a manner that protects the confidentiality of the information.

Factors for inclusion in the evaluation include whether the data contain information on: 

  • Environmental fate, transport, partitioning and degradation behavior across environmental media of interest,
  • Environmental exposure of ecological receptors to the chemical substance and/or its degradation products and metabolites,
  • Environmental exposure of human receptors to the substance and/or its degradation products and metabolites,
  • Scenarios resulting in releases of the substance into the environment that would expose ecological or human receptors,
  • Quantitative estimates of worker exposures and of environmental releases from occupational settings for the substance, and
  • Human health and environmental hazards.

OPPT explains that the evaluation stage will assess the quality of individual studies.   For this process the Agency will use the criteria identified in the data quality criteria appendices to the Application of Systematic Review in TSCA Risk Evaluations.  The appendices specify criteria for evaluating data on:

  • Physical and chemical properties,
  • Occupational exposure and release,
  • Fate,
  • Consumer, general population, and environmental exposure,
  • Ecological hazards,
  • Animal and in vitro toxicity, and
  • Epidemiology.

The data will then be integrated to evaluate and synthesize multiple evidence streams.  Data integration includes analysis and synthesis of the evidence and development of weight of evidence conclusions.  As part of this process OPPT will document any underlying assumptions that are used to support the risk evaluation.

TSCA requires that EPA make decisions about these data based on the weight of the scientific evidence.  OPPT reports that under TSCA, the weight of the scientific evidence is defined as “a systematic review method, applied in a manner suited to the nature of the evidence or decision, that uses a pre-established protocol to comprehensively, objectively, transparently, and consistently identify and evaluate each stream of evidence, including strengths, limitations, and relevance of each study and to integrate evidence as necessary and appropriate based upon strengths, limitations, and relevance.”   This approach presents the significant issues, strengths, and limitations of the data and the uncertainties that require consideration, in addition to highlighting the major points of interpretation.

OPPT explains that the last step of the systematic review process will be to develop a summary of findings.  The findings summarize the evidence, describe the methods used to weigh evidence, and articulate the basis for the conclusion(s), recommendation(s), and any uncertainties.  Both exposure assessment and hazard assessment will be discussed.

EPA Releases the 2018 Plan for Chemical Risk Evaluations under TSCA

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As required under the Frank R. Lautenberg Chemical Safety for the 21st Century Act, EPA has released its annual plan for chemical risk evaluations. The annual plan identifies the next steps for the first 10 chemical reviews currently underway, and describes EPA’s work in 2018 to prepare for future risk evaluations.

EPA was required to initiate ten risk evaluations in 2016, and is required to initiate at least 20 more within 3 years after enactment of the Lautenberg Act, or by December 2019. EPA designated the first ten chemical substances on December 19, 2016. By the end of 2018, the EPA will initiate prioritization for 40 chemicals – at least 20 Low-Priority and 20 High-Priority candidates. By December 22, 2019, EPA will designate 20 substances as Low-Priority and initiated risk evaluations on 20 High-Priority substances.

In order to support these risk evaluations and other key aspects of TSCA implementation, EPA stated that it will be proposing a draft TSCA Fees Rule in early 2018, which will provide estimates of the resources required to undertake risk evaluations.

EPA to Hold Public Meeting on Identifying Potential Candidates for Prioritization for Risk Evaluation

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EPA is holding two meetings in December to discuss ongoing implementation activities under the Frank R. Lautenberg Chemical Safety Act, which amended Toxic Substances Control Act (TSCA). On December 11, 2017 EPA is holding the second public meeting on possible approaches for identifying potential candidate chemicals for EPA’s prioritization process under TSCA. The meeting will be held December 11, 2017, 8:30 a.m. to 5:00 p.m. at the Ronald Reagan Building and International Trade Center, Horizon Ballroom, 1300 Pennsylvania Avenue, N.W., Washington, DC 20004.

As amended, TSCA required that EPA establish processes for prioritizing and evaluating risks from existing chemicals. EPA will describe and take comment on a number of possible approaches that could guide the Agency in the identification of potential candidate chemicals for prioritization.

EPA will accept questions from the public in advance of the meeting, and will respond to these questions at the meeting as time allows. To register to attend, submit questions, and learn more follow this link.