INDUSTRIAL CHEMICALS – KNOWN CARCINOGEN (IARC 1)
Trichloroethylene is a clear liquid at room temperature with a sweet, chloroform-like odour. Produced commercially since the 1920s, trichloroethylene has been used as a solvent and degreaser. Trichloroethylene is related to another chlorinated solvent, tetrachloroethylene (also called perchloroethylene or PERC). Trichloroethylene may also be referred to as trichloroethene or TCE. There are numerous other synonyms and product names; see the Hazardous Substances Data Bank (HSDB) for more information.
Trichloroethylene has been classified by the International Agency for Research on Cancer (IARC) as Group 1, a known human carcinogen, with a well established link to kidney cancer. Epidemiologic studies also found limited evidence for associations between TCE exposure and non-Hodgkin lymphoma and liver cancer.
Additional adverse health effects associated with low to moderate inhalation exposure to trichloroethylene range from headaches and dizziness to nerve damage. Acute exposures may damage the kidneys and liver, and cause arrhythmias. Skin irritation following dermal exposure has also been reported.
Regulations and Guidelines
|Canadian Jurisdictions||OEL (ppm)|
|Canada Labour Code||10
|BC, MB, ON, NL, PE, NS||10
|AB, NU, SK, NB, NT||50
|Other Jurisdiction||OEL (ppm)|
|ACGIH 2018 TLV||10
ppm = parts per million
stel = short term exposure limit (15 min. maximum)
ACGIH = American Conference of Governmental Industrial Hygienists
TLV = threshold limit value
Canadian Environmental Guidelines
|Canadian Drinking Water Guidelines||0.005 mg/L||2017|
|Ontario Ambient Air Quality Criteria||Annual: 2.3 μg/m3
24 hour: 12 μg/m3
|BC’s Contaminated Sites Regulation, BC Reg 375/96||Sets soil standards for the protection of human health:
Agricultural and low density residential sites: 20 μg/g
Urban park and high density residential sites: 40 μg/g
Commercial sites: 150 μg/g
Industrial sites: 3,500 μg/gDrinking water: 5 µg/L
Sets vapour standards for the protection of human health:
μg/m3 = micrograms per cubic metre
μg/g = micrograms per gram
μg/L = micrograms per litre
|Health Canada||DSL – low priority substance (already risk managed)||2006|
|CEPA||Schedule 1, paragraphs ‘a’ and ‘c’ (human health)||1999|
|CEPA 1999: Solvent
|Users of >1,000 kg/yr of TCE for cold or vapour degreasing must comply with these regulations||2003|
|National Classification System for Contaminated Sites||Rank = “High hazard”||2008|
|Environment Canada’s National Pollutant Release Inventory||NPRI Part (Threshold Category): 1A, Reportable to NPRI if manufactured, processed, or otherwise used at quantities greater than: 10 tonnes||2016|
DSL = domestic substance list
CEPA = Canadian Environmental Protection Act
Trichloroethylene was not included in other Canadian chemical listings reviewed.
Trichloroethylene is used primarily to degrease metals in automotive and metal industries. Another important use is as a feedstock material to produce other chemicals, such as fluorinated hydrocarbons and polymers. Trichloroethylene is also used to: produce adhesives and copolymers; clean electronic components; perform petroleum industry processes involving refining catalysts, paint removers, coatings, and vinyl resins; and act as a reagent/solvent in laboratory applications.
As a solvent, trichloroethylene has been used in the past to extract natural fats and oils, spices, hops, and caffeine from food products. It was also used as a dry cleaning solvent, but since the 1950s when tetrachloroethylene gained popularity, this use declined. Use as a spot treatment in the textile industry, however, continued into the 1990s at least.
Environmental Exposures Overview
The primary route of exposure to trichloroethylene for the general public is inhaling indoor air.[32,34] Minor sources of exposure include food, drinking water, and outdoor air. Trichloroethylene in indoor air likely comes from volatilized water sources (e.g. from showering), as well as from household products containing the solvent. Elevated concentrations in indoor air may also occur in homes that are built above groundwater contaminated with trichloroethylene. Trichloroethylene can be formed in groundwater when tetrachloroethylene breaks down.
Recent surveys of trichloroethylene levels in Canadian food products are not available. However, given that trichloroethylene has been banned from food preparation since 1977, these levels are expected to be negligible.
Most trichloroethylene that is used is expected to eventually enter the atmosphere. Point sources that may create higher, localized environmental levels of trichloroethylene include metal degreasing operations, sewage treatment plants, textile mills, landfills, incinerators, and septic tanks.
Searches of Environment Canada’s National Pollutant Release Inventory (NPRI) and the US Household Products Database yielded the following results on current potential for exposure to trichloroethylene in Canada:
NPRI and US Household Products Database
|Substance name: ‘Trichloroethylene’|
|Released into Environment||46 t||Manufacturing of plastic, aerospace, metal, and chemical products, non-residential building construction, waste treatment and disposal, pulp and paper mills (12 facilities)|
|Sent to off-site recycling||7.4 t|
|US Household Products 2016|
|Search Term||Quantity||Product Type|
|‘Trichloroethylene’||13||Cleaners/degreasers, vehicle undercoating, adhesives, sealants, and toner enhancer|
t = tonne
Occupational Exposures Overview
Inhalation and dermal contact are the most important routes of occupational exposure to trichloroethylene.
CAREX Canada estimates that approximately 9,800 Canadians are exposed to trichloroethylene in their workplaces. The largest industrial groups exposed are metal manufacturing, followed by personal and household goods repair and maintenance. The largest occupational groups exposed are metal product machine operators, plating, metal spraying and related operators, and labourers in metal fabrication. All of these occupations involve metal degreasing; workers who degrease metals tend to be the most heavily exposed occupational group.
Other important occupations outside the metal industry that may be exposed to trichloroethylene include tailors and dressmakers, upholsterers, and sewing machine operators.
For more information, see the occupational exposure estimate for trichloroethylene.
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