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CAS 67-66-3

Chloroform

carcinogenVOCHAPdrinking water contaminantOSHA carcinogen

Chloroform forms in your drinking water when chlorine used to disinfect the water reacts with natural organic matter — it is one of the most common disinfection byproducts in US tap water. It is also the Victorian-era anesthetic that, at high doses, damages the liver and kidneys and causes cancer.

Where It Comes From

Chloroform was discovered in 1831 independently by several chemists and became famous as one of the first general anesthetics, used widely in surgeries beginning in the 1840s [1]. Its use as an anesthetic declined when safer alternatives became available, and its toxicity to the liver and kidneys was recognized. Today, chloroform is not deliberately added to anything — it forms as an unintended byproduct. When water utilities chlorinate drinking water (which is essential for killing pathogens), the chlorine reacts with naturally occurring organic matter in the source water — humic acids from decaying leaves, soil compounds — to form trihalomethanes, a group that includes chloroform, bromodichloromethane, dibromochloromethane, and bromoform [2]. Chloroform is also produced industrially as a precursor to HCFC-22 refrigerant and is used as a laboratory solvent. Swimming pools are a source: the chlorine that keeps pools safe also reacts with swimmers' body oils, sweat, and urine to form chloroform and related compounds in pool air [3].

How You Are Exposed

Drinking chlorinated tap water is the primary exposure for most Americans — the EPA limits trihalomethanes (including chloroform) at 80 µg/L total in municipal water [1]. Showering and bathing in chlorinated water is a significant exposure route: chloroform is highly volatile and inhaled in hot shower steam, and it also absorbs directly through skin. Studies show that showering in chlorinated water may deliver more chloroform to your bloodstream than drinking equivalent volumes of the same water [2]. Indoor swimming pools are high-exposure environments, particularly for competitive swimmers and pool workers who spend many hours breathing chloroform-containing air. Chloroform is also present in industrial emissions and can contaminate groundwater near chemical manufacturing sites [3].

Why It Matters

Chloroform is classified as a probable human carcinogen (Group 2A by IARC), primarily for colorectal cancer, bladder cancer, and rectal cancer based on epidemiological studies of people drinking chlorinated water [1]. The liver and kidneys are the primary organs of acute toxicity — chloroform damages cells in both organs, and the effects at environmental concentrations are thought to be a threshold phenomenon rather than a linear no-threshold cancer model. Central nervous system depression occurs at high concentrations, explaining why it worked as a historical anesthetic [2]. The bladder cancer association is the most consistent across epidemiological studies: people who have consumed chlorinated drinking water for decades have modestly elevated bladder cancer rates, with longer-duration use and higher trihalomethane levels conferring greater risk [3].

Who Is at Risk

People who have spent a lifetime drinking chlorinated municipal water and those with higher-than-average water consumption face the most significant bladder cancer association [1]. Competitive swimmers — especially those who swim in indoor pools for many hours per week — have elevated genotoxicity markers compared to non-swimmers, reflecting elevated chloroform and related disinfection byproduct exposures [2]. Pregnant women may face additional concern: some studies link high trihalomethane exposures during pregnancy to small-for-gestational-age births and miscarriage, though evidence is mixed. Industrial workers involved in chloroform manufacturing and laboratory workers who use it as a solvent face occupational exposures [3].

How to Lower Your Exposure

Use a granular activated carbon filter (GAC) or point-of-use activated carbon block filter on your drinking water — these effectively remove trihalomethanes including chloroform [1]. Because showering exposure can exceed drinking exposure, consider an inline carbon shower filter to reduce chloroform in shower steam. Let hot water sit in a running shower for a minute before entering, and leave bathroom ventilation fan running during and after showering [2]. For swimming, outdoor pools have lower indoor air chloroform concentrations than indoor pools; competitive swimmers may benefit from monitoring their training environment's air quality. If you draw from a surface water source with high organic matter (common in the South and Mid-Atlantic), consider a whole-house filter to reduce all trihalomethane exposures from tap water [3]. Request your utility's annual water quality report, which must disclose total trihalomethane levels.

References

  1. [1]IARC. Chloroform. IARC Monographs Vol 73. 1999. https://monographs.iarc.who.int/
  2. [2]EPA. Disinfection Byproducts. https://www.epa.gov/sdwa/disinfection-byproducts
  3. [3]Villanueva CM, et al. Meta-analysis of studies on individual consumption of chlorinated drinking water. J Epidemiol Community Health. 2003;57(3):166-73.
  4. [4]Florentin A, et al. Health effects of disinfection by-products in swimmers. Ann Occup Environ Med. 2011;22(1):86-100.

Recovery & Clinical Information

Body Half-Life

Chloroform has a blood half-life of approximately 8-10 hours; it is metabolized by CYP2E1 to trichloromethanol (which decomposes to phosgene) and to dichloromethanol [1]. Urinary trichloroethanol and trichloroacetic acid are metabolites detectable for 1-2 days after exposure [2].

Testing & Biomarkers

Blood chloroform and exhaled air chloroform for acute recent exposures [1]. Urinary trichloroacetic acid and total trichloroethanol for occupational monitoring (though less specific since these are shared with TCE and PCE metabolism) [2]. For routine drinking water chloroform exposure, urine trihalomethane metabolites can be measured but are not clinically standard. Liver enzymes (ALT, AST) and urinalysis monitor for hepatic and renal effects of chronic exposure [1].

Interventions

Switch to filtered water — an activated carbon filter or reverse osmosis system reduces chloroform and other trihalomethanes by 90%+ from tap water [1]. Run cold water 2-3 minutes before drinking to flush distribution system residues. Shower ventilation reduces inhalation of chloroform released from hot shower water [2]. There is no specific chelation. For occupational pharmaceutical and chemical workers: local exhaust ventilation, low-chloroform product substitution, and liver function monitoring [1].

Recovery Timeline

Blood and exhaled chloroform normalize within 24 hours of stopping acute exposure [1]. Urine metabolites normalize within 2-3 days. Liver enzyme elevations from chloroform hepatotoxicity typically resolve within weeks after source removal [2]. The cancer risk contribution from chloroform (TTHM exposure from drinking water) is a small but non-zero lifetime risk that is not reversible — filtering water going forward prevents further accumulation of risk [1].

Recovery References

  1. [1]EPA (2001). Chloroform IRIS Assessment. https://iris.epa.gov/ChemicalLanding/&substance_nmbr=0025
  2. [2]ATSDR (2005). Toxicological Profile for Chloroform. https://www.atsdr.cdc.gov/toxprofiles/tp6.pdf

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