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  2. Assessing and Managing Chemicals under TSCA

Risk Evaluation for 1,2-Dichloroethane

General Information for 1,2-Dichloroethane

Chemical Group: Solvents

CASRN: 107-06-2

Risk Evaluation Initiated: December 2019

Dockets: EPA-HQ-OPPT-2018-0427; EPA-HQ-OPPT-2024-0114

Staff Contact: Simon Regenold
Email:  1.2.Dichloroethane.TSCA@epa.gov
Phone: (202) 566-1537

In May 2026, EPA released the final risk evaluation and associated technical support documents for 1,2-dichloroethane under the Toxic Substances Control Act (TSCA) for public comment. EPA designated 1,2-dichloroethane as a high priority chemical in December 2019. 

Read a prepublication version of the Federal Register notice announcing the final risk evaluation for 1,2-dichloroethane. (pdf) (701.41 KB)

Find information about other chemicals undergoing risk evaluations under TSCA. 

On this page:

  • What is 1,2-Dichloroethane?
  • Risk Evaluation for 1,2-Dichloroethane
  • Detailed Findings
  • Frequently Asked Questions
  • EPA’s Commitment to Gold Standard Science
  • Changes from Draft to Final 
  • Risk Evaluation and Supporting Documents
  • Draft Risk Evaluation and Supporting Documents 

What is 1,2-Dichloroethane?

Also known as ethylene dichloride, 1,2-dichloroethane (CASRN 107-06-2) is a volatile, colorless, oily liquid with a chloroform-like odor, and is miscible in most organic solvents. The primary use of 1,2-dichloroethane is in plastic material manufacturing to manufacture vinyl chloride. Information from the 2016 Chemical Data Reporting (CDR) for 1,2-dichloroethane indicates the reported volume is between 30 and 40 billion lbs/year.  

Risk Evaluation for 1,2-Dichloroethane

EPA completed a thorough review of 1,2-DCA using gold standard science. We used the best research, data, and information to evaluate this chemical that's used to make many products we use every day. We also listened carefully to input from the public and independent expert reviewers.  

EPA determined that 1,2-DCA presents an unreasonable risk of injury to human health driven by inhalation and dermal risks to workers under 15 of 20 total conditions of use (COUs); 12 of these COUs also present unreasonable risk to occupational non-users (ONUs). The risk determination reflects baseline workplace exposures; however, specified respirators and other workplace controls can reduce worker exposures such that the risk would no longer be unreasonable. 

EPA did not identify unreasonable risk to consumers, the general population, or the environment under any COU. 

As required by TSCA, EPA will now develop a rule to protect workers from the risks we identified. The agency will carefully consider health effects, exposure levels, how the chemical benefits society, and economic impacts. Input from workers, companies, and the public will be crucial to make sure our final rule protects health while being protective of vulnerable populations like women who are pregnant or of childbearing age and practical for businesses. 

This next step, when finalized, will give companies clear rules to follow and provide workers with the protections they need to stay safe on the job. 

Detailed Findings

EPA determined that 1,2-DCA presents an unreasonable risk to human health driven by worker inhalation and dermal exposures under 15 of 20 total COUs. Twelve of these 15 COUs also present unreasonable risk to occupational nonusers—workers who are in the workplace but do not directly handle the chemical. EPA did not identify unreasonable risk to consumers, the general population, or the environment under any COU evaluated. 

The health evidence that informed EPA’s conclusions includes laboratory studies indicating kidney toxicity following ingestion and respiratory (nasal) and male reproductive system toxicity following inhalation. Based on these animal data, EPA concluded that repeated workplace inhalation or dermal exposure over a working lifetime can cause cancer, including for occupational nonusers. 

The risk determination reflects baseline workplace exposures and does not assume the routine use of personal protective equipment or other engineered controls. However, the evaluation indicates that specified respirators and other workplace controls can reduce exposures such that the risk would no longer be unreasonable. Accordingly, EPA’s forthcoming risk management will focus on the specific COUs that drive these workplace risks. 

EPA also identified five COUs that do not significantly contribute to unreasonable risk to human health: distribution in commerce; industrial use as functional fluids in closed systems as a heat transferring agent; commercial use in plastic and rubber products; commercial use in fuels and related products; and consumer use in plastic and rubber products. 

In assessing potentially exposed or susceptible subpopulations, EPA evaluated workers; consumers; members of the general population who may be exposed through environmental releases; people who may be at greater risk due to age, genetics, or preexisting health conditions; and communities with high fish consumption, including some Tribal and subsistence communities. High fish consumption was considered because, if a chemical reaches surface waters, people who eat a lot of locally caught fish may be exposed through their diet. EPA did not identify unreasonable risk through this pathway for 1,2DCA under any COU. 

For the environment, EPA did not identify unreasonable risk under any COU. The evaluation considered aquatic vertebrates, aquatic invertebrates, algae, and land animals at environmentally relevant concentrations. EPA also evaluated several byproducts formed during the manufacture of 1,2-DCA; two byproducts—trans1,2dichloroethylene and 1,1,2trichloroethane—will be evaluated in separate TSCA risk evaluations. 

Frequently Asked Questions

Q: Who is most affected—and who wasn’t found to face unreasonable risk?  

A: Most affected: Workers (and nearby ONUs) in certain manufacturing, processing, industrial use, and disposal settings. Not found to significantly contribute to unreasonable risk in this evaluation: Consumers and the general public—including high fish consuming Tribal and subsistence communities—and the environment, under the TSCA COUs evaluated. 

Q: Why did EPA focus on direct workplace exposure?  

A: TSCA requires us to evaluate the manufacturing, processing, distribution, use, and disposal of chemicals in a risk evaluation. We evaluated all these uses.  We found that the highest risks occur in the workplace. Our gold standard science approach requires us to look at all sources of exposure covered by TSCA.  

Q: What about communities near facilities using 1,2-DCA?  

A: EPA evaluated potential exposures to the general population from releases to air, water/sediment, and land under each condition of use, including people who live near facilities. Based on best available science at environmentally relevant concentrations, EPA did not identify unreasonable risk to the general population or the environment under any condition of use. EPA also assessed dietary exposure for communities with high fish consumption and did not identify unreasonable risk. Upcoming risk management will focus on workplace exposures, and EPA will continue coordinating with other programs and welcomes community data. 

Q: Why did some of your findings change from the draft to the final evaluation?  

A: The final evaluation incorporates public comments and external peer review by the Science Advisory Committee on Chemicals (SACC). EPA updated and clarified methods, considered new or refined workplace and use information, and replaced overly conservative assumptions where better real-world data were available. These improvements led to refined exposure estimates and risk conclusions—most notably, the final determination that EPA did not identify unreasonable environmental risk under any condition of use. The final reflects the weight of the scientific evidence and best available science. 

Q: Will workers be protected even though you found risks? 

A: Yes. Part of EPA’s statutory obligations include the requirement to develop rules to protect workers from the unreasonable risks we identified. These rules will ensure that companies’ workers are kept safe.

EPA’s Commitment to Gold Standard Science   

We made our evaluation better based on: 

  • Updated data informing actual workplace conditions 

  • Public comments that helped us understand how the chemical is really used 

  • New reporting from companies about their current uses 

  • Expert peer review to make sure our methods were sound 

EPA used real-world data, including widely accepted approaches used by EPA’s Office of Air and Radiation, to strengthen our risk evaluation. 

Changes from Draft to Final

Environmental risk determination 

  • Draft: Preliminary determination of unreasonable risk to the environment, driven by chronic exposure to aquatic invertebrates in 2 COUs. 

  • Final: EPA did not identify unreasonable environmental risk under any COU; the nontechnical summary states the chemical “is not harmful to the environment” at environmentally relevant concentrations.  

This was driven by refinements to the surface water assessment and additional tiering that resulted in reduced aquatic media concentrations. Part of the reduction in risk comes from using higher plant effluent flow rates instead of lower receiving waterbody flow rates, and part comes from considering concentrations from effluent monitoring. 

Consumers and general population 

  • Draft: Consumer/general population exposure from any COU “does not significantly contribute” to unreasonable risk. 

  • Final: No changes to the risk conclusions, with the consideration of more recent ambient air release data. 

Risk Evaluation and Supporting Documents

View the supporting documents in docket EPA-HQ-OPPT-2018-0427.

  • Risk Evaluation for 1,2-Dichloroethane (pdf) (4.25 MB)
  • Nontechnical Summary of the TSCA Risk Evaluation for 1,2-Dichloroethane (pdf) (205.21 KB)
  • Response to Public Comments on the Risk Evaluation for 1,2-Dichloroethane (pdf) (1.77 MB)
  • Byproducts Assessment for 1,2-Dichloroethane (pdf) (1.9 MB)
  • Chemistry and Fate and Transport Assessment for 1,2-Dichloroethane (pdf) (1.13 MB)
  • Environmental Release Assessment for 1,2-Dichloroethane (pdf) (4.38 MB)
  • Environmental Media Assessment for 1,2-Dichloroethane (pdf) (2.04 MB)
  • Occupational Exposure Assessment for 1,2-Dichloroethane (pdf) (2.74 MB)
  • Consumer Exposure Assessment for 1,2-Dichloroethane (pdf) (1.42 MB)
  • General Population Exposure Assessment for 1,2-Dichloroethane (pdf) (938.23 KB)
  • Human Health Hazard Assessment for 1,2-Dichloroethane (pdf) (3.79 MB)
  • Environmental Exposure Assessment for 1,2-Dichloroethane (pdf) (927.41 KB)
  • Environmental Hazard Assessment for 1,2-Dichloroethane (pdf) (1.82 MB)
  • Systematic Review Protocol for 1,2-Dichloroethane (pdf) (2.19 MB)
  • Data Quality Evaluation and Data Extraction Information for Physical and Chemical Properties for 1,2-Dichloroethane (pdf) (1.16 MB)
  • Data Quality Evaluation and Data Extraction Information for Environmental Fate and Transport for 1,2-Dichloroethane (pdf) (1.48 MB)
  • Data Quality Evaluation and Data Extraction Information for Environmental Release and Occupational Exposure for 1,2-Dichloroethane (pdf) (1.81 MB)
  • Data Quality Evaluation Information for General Population, Consumer, and Environmental Exposure for 1,2-Dichloroethane (pdf) (1.32 MB)
  • Data Extraction Information for General Population, Consumer, and Environmental Exposure for 1,2-Dichloroethane (pdf) (245.67 KB)
  • Data Quality Evaluation Information for Human Health Hazard Animal Toxicology for 1,2-Dichloroethane (pdf) (3.11 MB)
  • Data Quality Evaluation Information for Human Health Hazard Epidemiology for 1,2-Dichloroethane (pdf) (725.59 KB)
  • Data Quality Evaluation Information for Environmental Hazard for 1,2-Dichloroethane (pdf) (922.24 KB)
  • Data Extraction Information for Environmental Hazard and Human Health Hazard Animal Toxicology and Epidemiology for 1,2-Dichloroethane (pdf) (1.25 MB)
  • Data Quality Evaluation Information for Dermal Absorption for 1,2-Dichloroethane (pdf) (590.33 KB)
  • Supplemental Information on EPI Suite Modeling Results in the Fate Assessment for 1,2-Dichloroethane (pdf) (292.52 KB)
  • Water Releases for 1,2-Dichloroethane (xlsx) (2.13 MB)
  • Air Releases for 1,2-Dichloroethane (xlsx) (32.19 MB)
  • Land Releases for 1,2-Dichloroethane (xlsx) (213.6 KB)
  • Byproducts Releases for 1,2-Dichloroethane (xlsx) (1.03 MB)
  • Number of Sites for 1,2-Dichloroethane (xlsx) (1.41 MB)
  • Estimates of Number of Workers and ONUs Model for 1,2-Dichloroethane (pdf) (143.89 KB)
  • Application of Adhesives Release Model for 1,2-Dichloroethane (xlsx) (103.44 KB)
  • Aerosol Products Release Model for 1,2-Dichloroethane (xlsx) (59.07 KB)
  • Aerosol Products Exposure Model for 1,2-Dichloroethane (xlsx) (215.86 KB)
  • Non-aerosol Cleaning and Degreasing Release Model for 1,2-Dichloroethane (xlsx) (97.69 KB)
  • Repackaging Release Model for 1,2-Dichloroethane (xltm) (75.06 KB)
  • Repackaging Exposure Model for 1,2-Dichloroethane (xltm) (78.13 KB)
  • Laboratory Use Release Model for 1,2-Dichloroethane (xlsx) (99.99 KB)
  • Application of Lubricants and Greases Exposure Model for 1,2-Dichloroethane (xlsx) (223.2 KB)
  • Dermal Monte Carlo Exposure Model for 1,2-Dichloroethane (xlsx) (116.16 KB)
  • Risk Calculator for Occupational Exposure for 1,2-Dichloroethane (xlsx) (214.94 KB)
  • Risk Calculator for Consumer Exposure for 1,2-Dichloroethane (xlsx) (53.04 KB)
  • Byproducts Risk Calculator for Occupational Exposure for 1,2-Dichloroethane (xlsx) (330.09 KB)
  • Byproducts Risk Calculator for Occupational Exposure for 1,2-Dichloroethane with Adjusted Working Years (xlsx) (336.14 KB)
  • Byproducts General Population Exposures for 1,2-Dichloroethane (xlsx) (120.77 KB)
  • Ambient Monitoring Technology Information Center (AMTIC) Monitoring Data 2015 to 2022 for 1,2-Dichloroethane (xlsx) (20.14 MB)
  • Supplemental Information on HEM TRI Exposure and Risk Analysis for 1,2-Dichloroethane (xlsx) (20.14 MB)
  • HEM TRI Input Files for 1,2-Dichloroethane (xlsx) (2.86 MB)
  • Supplemental Information on AERMOD Generic Releases Exposure and Risk Analysis for 1,2-Dichloroethane (xlsx) (2.53 MB)
  • AERMOD Generic Facilities/Sites Files for 1,2-Dichloroethane (pdf) (161.25 KB)
  • HEM Input and Output Files for 1,2-Dichloroethane (pdf) (158.95 KB)
  • HEM Input and Output Files for 1,2-Dichloroethane-Byproducts (pdf) (160.01 KB)
  • Water Quality Portal Data for 1,2-Dichloroethane (xlsx) (1.09 MB)
  • Surface Water Concentration Estimates for 1,2-Dichloroethane (xlsx) (441.35 KB)
  • Fish Ingestion Risk Calculator for 1,2-Dichloroethane (xlsx) (86.66 KB)
  • Drinking Water Exposure Estimates for 1,2-Dichloroethane (xlsx) (182.81 KB)
  • Benchmark Dose Modeling for 1,2-Dichloroethane (pdf) (3.82 MB)
  • Human Health Hazard Exposure Response Array Data and Figures for 1,2-Dichloroethane (xlsx) (227.18 KB)
  • OPPT/ECRAD Review of OECD 428 Report Submission to EPA Test Order for 1,2-Dichloroethane (CAS No 107-06-2) (pdf) (198.38 KB)
  • in vitro Dermal Absorption Study Calculation for 1,2-Dichloroethane (xlsx) (164.44 KB)
  • Risk Evaluation for 1,1-Dichloroethane – Supplemental Information File: in vitro Dermal Absorption Study Analysis (pdf) (237.21 KB)
  • Risk Evaluation for 1,1-Dichloroethane – Supplemental Information File: in vitro Dermal Absorption Study Calculation Sheet (xltm) (1.28 MB)
  • OPPT/ECRAD Review of OECD 428 Report Submission to EPA Test Order for 1,1-Dichloroethane (CAS No 75-34-3) (pdf) (202.43 KB)
  • Mammalian TRV Calculator for 1,2-Dichloroethane (xltm) (1.28 MB)
  • Avian Hazard Value Calculator for 1,2-Dichloroethane (xltm) (319.28 KB)
  • Tool Settings and Analog List for Environmental Hazard Assessment for 1,2-Dichloroethane (xlsx) (55.31 KB)

Draft Risk Evaluation and Supporting Documents

In November 2025, EPA released the draft risk evaluation for 1,2-dichloroethane public comment and peer review. For more information, please visit the draft risk evaluation webpage.

Assessing and Managing Chemicals under TSCA

  • How EPA Evaluates the Safety of Existing Chemicals
  • Prioritizing Existing Chemicals for Risk Evaluation
  • Risk Evaluations for Existing Chemicals under TSCA
  • Risk Management for Existing Chemicals under TSCA
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Last updated on May 6, 2026
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