Key takeaway
What This Development Means
EPA's draft evaluation does not yet impose new controls, but it preliminarily finds unreasonable human-health risk from certain trans-DCE uses. Manufacturers, importers, formulators, industrial users and waste operators should test EPA's exposure assumptions against site data and submit material evidence by 26 October 2026.
Does EPA's draft make trans-DCE illegal?
No. The draft is a risk evaluation, not a prohibition or risk-management rule. Existing obligations continue while EPA considers comments and peer review. Any future restrictions would require a final unreasonable-risk determination and a separate rulemaking process.
What evidence is EPA requesting?
EPA highlights personal protective equipment, blowing-agent and vapour-degreasing uses, by-product manufacture, batch frequency and semiconductor formulations. Stakeholders should provide quality-assured exposure, control, release and use data that clearly identifies facilities, tasks, assumptions and supporting methods.
Source basis: US Environmental Protection Agency, draft risk evaluation for trans-1,2-dichloroethylene (27 August 2026)
The US Environmental Protection Agency (EPA) has published a draft Toxic Substances Control Act (TSCA) risk evaluation for trans-1,2-dichloroethylene, preliminarily finding that certain conditions of use present an unreasonable risk to human health. Published on 27 August 2026, the assessment is open for comment until 26 October and gives chemical manufacturers, processors, users and worker representatives a defined opportunity to challenge or strengthen EPA's evidence.
EPA trans-1,2-dichloroethylene risk evaluation identifies workplace concerns
Trans-1,2-dichloroethylene, often abbreviated to trans-DCE, is a volatile chlorinated solvent used as a cleaner and degreaser, processing aid, reaction product, surface modifier and in other industrial applications. EPA evaluated inhalation and dermal exposures, releases from industrial and commercial activities and risks across the chemical's lifecycle.
The agency's preliminary unreasonable-risk conclusion is driven by particular conditions of use rather than every use of trans-DCE. The draft therefore does not amount to a general ban, a new occupational exposure limit or an immediate restriction. It is the scientific and legal assessment that may support a later risk-management rule.
EPA is particularly seeking information on personal protective equipment, use as a blowing agent, vapour-degreasing operations, manufacture as a by-product, batch frequency and semiconductor formulations. Businesses with representative monitoring, process and control data should assess whether the assumptions reflect actual operations.
What changed and what remains unchanged
The new trigger is the publication of the complete draft evaluation and preliminary risk determination. Foresight previously covered EPA's June peer-review plans for five high-priority chemicals, including trans-DCE. This notice advances that process by exposing EPA's full analysis and opening a formal comment period.
Current TSCA duties, hazard communication requirements and applicable workplace controls remain unchanged. EPA must review comments and peer-review input before issuing a final evaluation. If the agency finalises an unreasonable-risk finding, TSCA then requires a separate risk-management process in which EPA can propose controls for the contributing conditions of use.
Implications across the trans-DCE value chain
Manufacturers and importers should trace volumes and downstream uses, while formulators and distributors should confirm that exposure information follows the product. Industrial users should compare EPA's scenarios with ventilation, enclosure, respiratory protection and dermal controls. Waste operators should review handling and release assumptions for residues and spent solvent.
Inference: the targeted data requests indicate where uncertainty could most influence EPA's final conclusions. Detailed, quality-assured evidence on exposure frequency, engineering controls and protective-equipment performance is therefore likely to be more useful than broad assertions that operations are safe.
Practical stakeholder actions
Identify all trans-DCE uses and suppliers, download the draft and supporting files, and map each relevant condition of use to site evidence. Validate exposure measurements, personal protective equipment programmes, release estimates and waste routes. Where the record is incomplete or materially unrepresentative, prepare a source-referenced submission to docket EPA-HQ-OPPT-2018-0465 by 26 October 2026.
Related Articles

EPA Opens New Rulemaking Path For Carbon Tetrachloride TSCA Amendments
EPA is considering changes to its December 2024 carbon tetrachloride rule while current controls and compliance dates remain the legal baseline.

PCE And Carbon Tetrachloride Compliance Dates Extended By US EPA
Selected PCE and carbon tetrachloride deadlines move into 2027, but the underlying TSCA risk-management rules and existing dermal-protection duties remain in place.

EPA Flags 1,2-Dichloroethane As Unreasonable Risk To Workers Under TSCA
The EPA has concluded that 1,2-dichloroethane poses unreasonable risks to workers under 15 industrial use conditions, launching the TSCA risk management phase for PVC and chlorinated chemical supply chains.
