Risk Evaluation for 1,3-Butadiene
In December 2025, EPA released the final risk evaluation under the Toxic Substances Control Act (TSCA) for 1,3-butadiene. EPA designated 1,3-butadiene as a high priority chemical in December 2019.
Find other information about other chemicals undergoing risk evaluations under TSCA.
On this page:
- What is 1,3-Butdiene?
- Risk Evaluation
- Detailed Findings
- Frequently Asked Questions
- EPA’s Commitment to Gold Standard Science
- Further Background on Risk Evaluation
- Changes from Draft to Final
- Risk Evaluation and Supporting Documents
- Draft Risk Evaluation and Supporting Documents
What is 1,3-Butadiene?
1,3-Butadiene (CASRN 106-99-0), a colorless, flammable gas used in manufacturing polymers like plastic and synthetic rubber which are used to make products like:
- Car tires
- Adhesives and sealants
- Paints and coatings
- Automotive care products
- Lubricants
Consumer products only contain tiny amounts of this chemical (less than 0.001%), which is safe for everyday use.
Unreasonable risks are found in industrial settings where workers may be exposed to much higher levels. In these industrial workplaces where 1,3-butadiene is manufactured or used to make products, high levels of exposure can be unsafe and can cause health risks such as reduced birthweight pregnancies, anemia, leukemia, and bladder cancer. These risks are not seen when people use consumer products.
Risk Evaluation
EPA completed a thorough review of 1,3-butadiene 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 evaluated direct workplace exposure because that's where the highest potential exposures occur. The agency followed standard scientific practices by evaluating 1,3-butadiene exposures to provide clear results about this specific chemical's risks.
Our robust scientific review found that there are NO unreasonable risks for consumers or the general population (including people living near facilities), nor are there risks to environmental receptors.
EPA found that there could be health risks for workers who may breathe in this chemical at their jobs. This finding doesn't include any protective gear like masks, respirators or other safety equipment that workers might already be using.
As required by law under TSCA (Toxic Substances Control Act), 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’s risk evaluation found that there are health risks for workers who breathe in this chemical in 11 types of work scenarios. These include factories that make or use 1,3-butadiene to create rubber, plastics, and other products. Our findings don't include protections that workers might already be using, like masks or special equipment.
We found NO unreasonable risks to:
- Consumers using products with this chemical
- People living near facilities that use 1,3- butadiene
- The environment
This evaluation will help inform protections for American workers while allowing U.S. companies to continue making important products safely.
EPA will now develop a rule to protect workers from the unreasonable risks we identified. This process will include:
- Careful consideration of health effects and exposure levels
- Analysis of economic impacts
- Input from workers, companies, and the public
- Practical solutions that protect health while allowing important manufacturing to continue
The final rule will give companies clear direction and ensure workers have the protection they need while these important products continue to be made safely.
Frequently Asked Questions
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 1,3-butadiene?
A: We understand these communities have concerns, and we take them seriously. Our thorough analysis using the best available science shows that the chemical does not pose unreasonable risks to people living near facilities (fenceline communities). We considered air, water, and soil to reach this conclusion.
Q: Why did some of your findings change from the draft to the final evaluation?
A: We improved our evaluation by using real-world data, removing flawed assumptions from our first draft, and strengthening our methods and approaches. We also received updated information about how companies actually use this chemical. This made our science more accurate and reliable.
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 removed flawed assumptions from our first draft and used real-world data, including widely accepted approaches used by EPA’s Office of Air and Radiation, to strengthen our risk evaluation.
Further Background on Risk Evaluation
EPA evaluated 30 conditions of use (COU) and determined that 11 were significant contributors to unreasonable risk of injury to human health for workers due to inhalation exposure. For COUs with unreasonable risks to workers, these determinations do not reflect the use of personal protective equipment (PPE); however, PPE may reduce exposures and mitigate risk.
COUs Significantly Contributing to Unreasonable Risk:
Industrial Use:
Manufacturing - domestic manufacturing
Manufacturing - importing
Processing as a reactant - intermediate in various industries such as adhesive manufacturing and synthetic rubber manufacturing
Processing as a reactant - monomer used in polymerization process in synthetic rubber, plastic material, and resin manufacturing
Processing - incorporation into formulation, mixture, or reaction product - monomers in plastic, resin, and synthetic rubber manufacturing
Processing - incorporation into formulation, mixture, or reaction product - plasticizer in asphalt paving, roofing, and coating materials manufacturing
Processing - incorporation into article - monomer in rubber product manufacturing
Processing - use-non-incorporative activities - fuel in petroleum refineries
Processing - repackaging in wholesale and retail trade involving synthetic rubber and petrochemical manufacturing
Processing - recycling
Disposal
Changes from Draft to Final
28 COUs were evaluated in the draft RE compared to the 30 COUs that were evaluated in the final RE due to changes in the Chemical Data Reporting (CDR) .
4 COUs were added as a result of the latest CDR and 2 COUs were removed due to stakeholder feedback regarding the use (or lack) of 1,3 butadiene in industrial production, and CDR , indicating use is no longer active.
In total, 13 COUs were updated based on additional information from stakeholder feedback clarifying activities under the COU and/or updated CDR (see Appendix D - Updates to the 1,3-Butadiene Conditions of Use Tables for details).
For workers, 11 COUs contributed to the unreasonable risk.
8 COUs were unchanged
3 new COUs not in the draft risk evaluation were included in the final risk evaluation as a result of updated CDR and were determined to contribute to the unreasonable risk
This change was due to updates based on new CDR. The CDR rule, under TSCA, requires manufacturers (including importers) to provide EPA with information on the production and use of chemicals in commerce when production volumes for a chemical are 25,000 pounds or greater. This reporting occurs on 4-year cycles and assures that EPA and (for non-confidential data) the public have access to up-to-date information on chemicals.
2 COUs in the draft risk evaluation were either reclassified or removed
This change was due to updates based on CDR that the use was no longer active and public comment providing clarification of activities under the COU.
One COU (commercial use-laboratory chemicals) changed from unreasonable risk to no unreasonable risk.
This change was due to changes based on information; EPA refined this analysis and determined that the full-shift assumption used for the draft risk evaluation was overly conservative. EPA estimates that there are 10 workers for this COU.
For occupational non-users (ONUs), 2 COUs changed from unreasonable risk to no unreasonable risk. EPA is still finding that 1 COU contributes to the unreasonable risk for ONUs .
In the draft risk evaluation, EPA preliminarily determined that Manufacturing-import, Processing-repackaging, and Processing as a reactant-monomer used in polymerization process contributed to unreasonable risk for ONUs.
In the final risk evaluation, EPA determined that Processing-repackaging contributed to the unreasonable risk for ONUs.
This change is based on information submitted on 1,3-butadiene industrial hygiene data. EPA refined the analysis and determined that the shift-length assumptions used for the draft risk evaluations were overly conservative.
For the general population, 3 COUs were changed from unreasonable risk to no unreasonable risk. In the final risk evaluation, EPA determined that no COU contributed to the unreasonable risk for the general population.
This change is due to refinements in the general population evaluation, including the use of an updated IUR and use of NEI data in the HEM analysis.
Instead of using basic facility information (TRI), EPA switched to a more detailed database (NEI) that includes specific details including stack height, what angle they release emissions at, and emission temperatures. This allowed our evaluation to move away from defaults to more accurate, facility-specific conditions. The database also provided exact coordinates of where emissions are released, rather than just general facility locations. This geographic precision gives a more accurate picture of actual exposure risks.
EPA also considered other risk-based factors, such as the size of population at increased risk, maximum risk, and uncertainty measures for making the unreasonable risk determination, based on learnings from the Office of Air and Radiation.
Risk Evaluation and Supporting Documents
- Risk Evaluation for 1,3-Butadiene (pdf)
- Non Technical Summary for Risk Evaluation of 1,3-Butadiene (pdf)
- Summary of and Response to External Peer Review and Public Comments on the Risk Evaluation and Technical Support Documents for 1,3-Butadiene (pdf)
- Physical Chemistry, Fate, and Transport Assessment for 1,3-Butadiene - Technical Support Document for the Risk Evaluation (pdf)
- Environmental Release and Occupational Exposure Assessment for 1,3-Butadiene - Technical Support Document for the Risk Evaluation (pdf)
- Environmental Media Concentrations for 1,3-Butadiene - Technical Support Document for the Risk Evaluation (pdf)
- General Population Exposure for 1,3-Butadiene - Technical Support Document for the Risk Evaluation (pdf)
- Human Health Hazard Assessment for 1,3-Butadiene - Technical Support Document for the Risk Evaluation (pdf)
- Systematic Review Protocol for 1,3-Butadiene (pdf)
- Data Quality Evaluation and Data Extraction Information for Physical and Chemical Properties for 1,3-Butadiene - Systematic Review Support Document for the Risk Evaluation (pdf)
- Data Quality Evaluation and Data Extraction Information for Environmental Fate and Transport for 1,3-Butadiene - Systematic Review Support Document for the Risk Evaluation (pdf)
- Data Quality Evaluation and Data Extraction Information for Environmental Release and Occupational Exposure for 1,3-Butadiene - Systematic Review Support Document for the Risk Evaluation (pdf)
- Data Quality Evaluation Information for General Population, Consumer, and Environmental Exposure for 1,3-Butadiene - Systematic Review Support Document for the Risk Evaluation (pdf)
- Data Extraction Information for General Population, Consumer, and Environmental Exposure for 1,3-Butadiene - Systematic Review Support Document for the Risk Evaluation (pdf)
- Further Filtering Results for Human Health Hazard Animal Toxicology and Epidemiology for 1,3-Butadiene - Systematic Review Support Document for the Risk Evaluation (pdf)
- Data Quality Evaluation Information for Human Health Hazard Epidemiology for 1,3-Butadiene - Systematic Review Support Document for the Risk Evaluation (pdf)
- Data Quality Evaluation Information for Human Health Hazard Animal Toxicology for 1,3-Butadiene - Systematic Review Support Document for the Risk Evaluation (pdf)
- Data Extraction Information for Environmental Hazard and Human Health Hazard Animal Toxicology and Epidemiology for 1,3-Butadiene - Systematic Review Support Document for the Risk Evaluation (pdf)
- EPI Suite Modeling Results Supporting Fate Assessment for 1,3-Butadiene (pdf)
- Ambient Monitoring Technology Information Center (AMTIC) Monitoring Data 2016 to 2022 for 1,3-Butadiene (xlsx)
- Water Quality Portal (WQP) Monitoring Data 2004 to 2025 for 1,3-Butadiene (xlsx)
- Land Releases for 1,3-Butadiene (xlsx)
- Water Releases for 1,3-Butadiene (xlsx)
- Air Releases (TRI) for 1,3-Butadiene (xlsx)
- Air Releases (NEI 2017) for 1,3-Butadiene (xlsx)
- Air Releases (NEI 2020) for 1,3-Butadiene (xlsx)
- Application of Adhesives and Sealants Environmental Release Modeling Results for 1,3-Butadiene (xlsx)
- Number of Sites for 1,3-Butadiene (xlsx)
- Benchmark Dose Modeling Results for 1,3-Butadiene (pdf)
- Lifetable Analysis of Leukemia and Bladder Cancer for 1,3-Butadiene (xlsx)
- Risk Calculator for Occupational Exposures for 1,3-Butadiene (xlsx)
- Integrated Indoor Outdoor Air Calculator (IIOAC) TRI 2016-2021 Exposure and Risk Analysis for 1,3-Butadiene (xlsx)
- Human Exposure Model (HEM) TRI 2016 to 2021 Exposure and Risk Analysis for 1,3-Butadiene (xlsx)
- Human Exposure Model (HEM) NEI 2017 to 2020 General Population Exposure for 1,3-Butadiene (xlsx)
- Human Exposure Model (HEM) NEI 2017 to 2020 Exposure and Risk Analysis for 1,3-Butadiene (xlsx)
- Risk Evaluation for 1,3-Butadiene: Supplemental Information on the Human Exposure Modeling Results for 1,3-Butadiene (TRI) (pdf)
- Risk Evaluation for 1,3-Butadiene: Supplemental Information on the Human Exposure Modeling Results for 1,3-Butadiene (NEI) (pdf)
- Third Unregulated Contaminant Monitoring Rule Data for 1,3-Butadiene (xlsx)
- Inhalation Monitoring Data Summary for 1,3-Butadiene (xlsx)
- Appendix H Attachment of Occupational Exposure Assessment for 1,3-Butadiene (xlsx)
Draft Risk Evaluation and Supporting Documents
In December 2024, EPA released the draft risk evaluation for 1,3-butadiene public comment and peer review. In March 2025, EPA released a supplement to the risk evaluation describing a preliminary refinement of cancer risk estimates from exposure to 1,3-butadiene in air from releasing facilities. These refined facility specific risk estimates provide important updated estimates for incorporation into the risk evaluation.
For more information, please visit the draft risk evaluation webpage.