Toxic Chemicals › Carbon Tetrachloride › Regulatory History
EPA, OSHA, and State Regulatory Standards for Carbon Tetrachloride
Carbon Tetrachloride — CASRN 56-23-5
Carbon tetrachloride (CCl4), also known as tetrachloromethane, is a nonflammable, colorless chlorinated organic compound that was extensively used throughout the twentieth century as an industrial solvent, cleaning agent, degreaser, chemical intermediate, and fire suppressant. Because of its exceptional ability to dissolve oils, fats, waxes, resins, and other organic materials, carbon tetrachloride was widely employed in dry cleaning, metal degreasing, textile processing, laboratory applications, pesticide formulations, and refrigerant manufacturing. It also served as an important feedstock in the production of chlorofluorocarbons (CFCs) and other chlorinated chemicals. Although many commercial uses have been discontinued because of its toxicity and environmental impacts, historical releases remain widespread at industrial facilities, hazardous waste sites, chemical manufacturing plants, and former solvent storage areas. Carbon tetrachloride is moderately volatile, relatively persistent in groundwater, and capable of contaminating soil, groundwater, surface water, and ambient air, making it a common contaminant at legacy industrial sites.
Scientific concern regarding carbon tetrachloride developed early in the twentieth century when physicians and occupational health researchers recognized its severe hepatotoxic effects among workers and accidental poisonings. By the 1930s and 1940s, numerous reports documented acute liver failure, kidney injury, neurological impairment, and fatalities following occupational or accidental exposure. Experimental toxicology studies later demonstrated that carbon tetrachloride produces highly reactive free radicals during metabolism, leading to oxidative damage and extensive liver cell destruction. Throughout the latter half of the twentieth century, environmental investigations identified widespread groundwater contamination associated with historical solvent disposal, chemical manufacturing, military installations, and grain storage facilities where carbon tetrachloride-based fumigants had been used. These findings contributed to increasingly stringent regulatory controls and the eventual elimination of most commercial applications.
Carbon tetrachloride is regulated under numerous federal environmental and occupational programs because of its toxicity, persistence, and carcinogenic potential. It is regulated under the Clean Air Act, CERCLA, RCRA, TSCA, EPCRA, and the Safe Drinking Water Act because of its potential for air emissions, hazardous waste generation, and groundwater contamination. Carbon tetrachloride is also listed as a Hazardous Air Pollutant (HAP) under Section 112 of the Clean Air Act and is recognized as an ozone-depleting substance under the Montreal Protocol, resulting in the phaseout of nearly all production and dispersive commercial uses. Occupational exposure is regulated by the Occupational Safety and Health Administration (OSHA), which has established a permissible exposure limit (PEL) of 10 parts per million (ppm) as an 8-hour time-weighted average with a skin notation. The U.S. Environmental Protection Agency (EPA) has established a Maximum Contaminant Level (MCL) of 5 micrograms per liter (µg/L)for carbon tetrachloride in public drinking water systems.
Carbon tetrachloride has been extensively evaluated by regulatory and public health agencies because of its carcinogenicity and severe systemic toxicity. The International Agency for Research on Cancer (IARC) classifies carbon tetrachloride as Group 2B (possibly carcinogenic to humans) based on sufficient evidence in experimental animals and inadequate evidence in humans. The U.S. Environmental Protection Agency (EPA) concludes that carbon tetrachloride is likely to be carcinogenic to humans, while the National Toxicology Program (NTP) lists carbon tetrachloride as reasonably anticipated to be a human carcinogen. California has listed carbon tetrachloride under Proposition 65 as a chemical known to cause cancer. In addition to its carcinogenic potential, carbon tetrachloride is recognized as one of the classic hepatotoxic chemicals used extensively in toxicological research because of its well-characterized mechanism of free radical-mediated liver injury.
- Scientific understanding of carbon tetrachloride toxicity has expanded considerably through occupational, epidemiological, and experimental research. Acute exposure commonly produces headache, dizziness, nausea, vomiting, central nervous system depression, and respiratory irritation, while higher exposures may result in liver failure, kidney injury, cardiac arrhythmias, coma, and death. Carbon tetrachloride is metabolized primarily by hepatic cytochrome P450 enzymes to form highly reactive trichloromethyl (
- CCl₃) and trichloromethyl peroxy (
- OOCCl₃) radicals, which initiate lipid peroxidation and widespread cellular injury. Repeated exposure has been associated with chronic liver disease, renal impairment, neurological effects, and increased cancer risk. Because the chemical is readily absorbed by inhalation, ingestion, and dermal contact, occupational exposure historically occurred across multiple pathways, although inhalation represented the principal route in industrial settings.
Carbon tetrachloride remains an important contaminant in environmental forensic investigations because of its extensive historical use in chemical manufacturing, metal degreasing, grain fumigation, dry cleaning, military operations, and industrial solvent applications. Environmental investigations commonly evaluate carbon tetrachloride in groundwater, soil, soil gas, indoor air, ambient air, surface water, sediment, and hazardous waste while considering historical solvent handling practices, chemical manufacturing operations, groundwater hydrogeology, vapor intrusion pathways, and natural attenuation processes. Because carbon tetrachloride frequently co-occurs with other chlorinated solvents—including chloroform, methylene chloride, trichloroethylene (TCE), tetrachloroethylene (PCE), and 1,1,1-trichloroethane (TCA)—forensic investigations routinely evaluate complete chlorinated solvent signatures to identify contaminant sources, distinguish multiple release events, reconstruct historical industrial activities, evaluate environmental fate and transport, and assess potential human and ecological exposures. Groundwater plume reconstruction, compound-specific isotope analysis, vapor intrusion assessments, and historical solvent use evaluations are frequently employed to support environmental remediation and litigation involving carbon tetrachloride contamination.
References
Agency for Toxic Substances and Disease Registry. (2005). Toxicological profile for carbon tetrachloride. U.S. Department of Health and Human Services. https://www.atsdr.cdc.gov/toxprofiles/tp30.pdf
California Office of Environmental Health Hazard Assessment. (2025). Proposition 65 chemicals list. https://oehha.ca.gov/proposition-65/proposition-65-list
International Agency for Research on Cancer. (1999). Re-evaluation of some organic chemicals, hydrazine and hydrogen peroxide (IARC Monographs on the Evaluation of Carcinogenic Risks to Humans, Vol. 71). World Health Organization. https://monographs.iarc.who.int/
National Toxicology Program. (2021). Report on carcinogens (15th ed.). U.S. Department of Health and Human Services. https://ntp.niehs.nih.gov/whatwestudy/assessments/cancer/roc
Occupational Safety and Health Administration. (n.d.). Carbon tetrachloride.
https://www.osha.gov/chemicaldata/103
U.S. Environmental Protection Agency. (2024). Integrated Risk Information System (IRIS): Carbon Tetrachloride.https://iris.epa.gov
U.S. Environmental Protection Agency. (2024). Technical Fact Sheet – Carbon
Tetrachloride.https://www.epa.gov/remedytech
United Nations Environment Programme. (1987). Montreal Protocol on Substances that Deplete the Ozone Layer.https://ozone.unep.org/treaties/montreal-protocol
World Health Organization. (2022). Guidelines for drinking-water quality (4th ed., incorporating the 1st and 2nd addenda). World Health Organization.
This regulatory history was developed under the direction of Dr. Paul Rosenfeld, an environmental scientist with extensive experience in environmental chemistry, contaminant fate and transport, exposure science, toxicology, and human health risk assessment. Through RoseyFields LLC, Dr. Rosenfeld evaluates the scientific and regulatory literature to characterize the properties, environmental behavior, historical uses, regulatory framework, and potential human and ecological impacts of environmental contaminants. His technical oversight helped ensure that the scientific interpretations, regulatory context, and technical information presented in this report are consistent with accepted scientific principles, current regulatory guidance, and established environmental health practices.
