Technical Factsheet on: TRICHLOROETHYLENE
List of Contaminants
As part of the Drinking Water and Health pages, this fact sheet is part of a larger publication:
National Primary Drinking Water Regulations
Drinking Water Standards
MCLG: zero
MCL: 0.005 mg/L
HAL(child): none
Health Effects Summary
Acute: EPA has found trichloroethylene to potentially cause vomiting and abdominal pain from
acute exposures at levels above the MCL.
No Health Advisories have been established for short-term exposures.
Chronic: Trichloroethylene has the potential to cause liver damage from a lifetime exposure at
levels above the MCL.
Cancer: There is some evidence that trichloroethylene may have the potential to cause cancer
from a lifetime exposure at levels above the MCL.
Usage Patterns
Production of trichloroethylene has increased from just over 260,000 lbs in 1981 to 320 million
lbs. in 1991. Vapor degreasing of fabricated metal parts and some textiles accounts for 80% of its
use.
Five percent is used as an intermediate in the production of organic chemicals and
pharmaceuticals. Miscellaneous uses (5%) include solvents for dry cleaning, extraction and as a
refrigerant/heat exchange liquid. An estimated 10% is exported.
Release Patterns
Major environmental releases of trichloroethylene are due to air emissions from metal degreasing
plants. Wastewater from metal finishing, paint and ink formulation, electrical/electronic
components, and rubber processing industries also may contain trichloroethylene.
From 1987 to 1993, according to the Toxics Release Inventory, trichloroethylene releases to
water totalled over 100,000 lbs. Releases to land totalled over 191,000 lbs. These releases were
primarily from steel pipe and tube manufacturing industries. The largest releases occurred in
Pennsylvania and Illinois. The largest direct releases to water occurred in West Virginia.
Environmental Fate
Relatively high vapor pressure and low adsorption coefficient to a number of soil types indicates
ready transport through soil and low potential for adsorption to sediments. The mobility in soil is
confirmed in soil column studies and river bank infiltration studies. Four to six percent of
environmental concentrations of trichloroethylene adsorbed to two silty clay loams (Koc = 87
and 150). No adsorption to Ca-saturated montmorillonite and 17% adsorption to Al-saturated
montmorillonite was observed.
The high Henry's Law Constant indicates rapid evaporation from water. Half-lives of evaporation
have been reported to be on the order of several minutes to hours, depending upon the
turbulence. Field studies also support rapid evaporation from water. Trichloroethylene is not
hydrolyzed by water under normal conditions. It does not adsorb light of less than 290 nm and
therefore should not directly photodegrade. However, slow (half-life -l0.7 months)
photooxidation in water has been noted.
Trichloroethylene is relatively reactive under smog conditions with 60% degradation in 140 min
and 50% degradation in 1 to 3.5 hours reported. Atmospheric residence times based upon
reaction with hydroxyl radical is 5 days (6-8) with production of phosgene, dichloroacetyl
chloride, and formyl chloride.
Marine monitoring data only suggest moderate bioconcentration (2-25 times). Bioconcentration
factors of 17 to 39 have been reported in bluegill sunfish and rainbow trout.
Chemical/Physical Properties
CAS Number: 79-01-6
Color/ Form/Odor: Clear, colorless or blue mobile liquid with sweet
chloroform-like odor
M.P.: -73 C B.P.: 87 C
Vapor Pressure: 57.8 mm Hg at 20 C
Density/Spec. Grav.: 1.465 at 20 C
Octanol/Water Partition (Kow): Log Kow = 2.29
Solubilities: 1.0 g/L of water at 25 C
Soil sorption coefficient: Log Koc = 2 for many soil types; high to very high
mobility in soil
Bioconcentration Factor: 17 to 39 in fish; moderate.
Odor/Taste Thresholds: N/A
Henry's Law Coefficient: 0.01 atm-cu m/mole
Trade Names/Synonyms: 1,1,2-Trichloroethylene; Acetylene trichloroethylene;
Algylen; Anameth; Benzinol; Chlorilen; CirCosolv; Germalgene; Lethurin;
Perm-a-chlor; Petzinol; Philex; TRI-Plus M; Vitran
Other Regulatory Information
Monitoring:
-- For Ground/Surface Water Sources:
Initial Frequency- 4 consecutive quarterly samples during initial compliance period (1993-1995)
Repeat Frequency- If no detects in initial samples GW systems must take annual samples during 1996-1998 compliance period and triennial samples thereafter; SW systems must take annual samples.
-- Triggers - Return to quarterly monitoring if detect at > 0.0005 mg/L, until primacy State determines otherwise
Analysis
Reference Source | Method Numbers |
EPA 600/4-88-039 | 502.2; 524.2; 551 |
Treatment/Best Available Technologies: Granular Activated Charcoal and Packed Tower
Aeration
Toxic Release Inventory - Releases to Water and Land, 1987 to 1993 (in pounds):
| Water | Land |
TOTALS (in pounds) | 100,293 | 191,088 |
Top Six States* |
---|
PA | 0 | 33,450
|
IL | 0 | 30,711
|
GA | 3,742 | 17,532
|
TX | 0 | 21,000
|
MA | 0 | 19,920
|
WV | 12,822 | 0
|
Major Industries |
---|
Steel pipe, tubes | 31 | 39,288
|
Misc. Indust. Organics | 27,708 | 0
|
Car parts, access. | 4,405 | 19,920
|
Plating, polishing | 3,342 | 20,100
|
Wool fabric mills | 3,942 | 18,081
|
* State totals only include facilities with releases greater than 10,000 lbs.
For Additional Information
EPA can provide further regulatory or other general information:
EPA Safe Drinking Water Hotline - 800/426-4791
Other sources of toxicological and environmental fate data include:
Toxic Substance Control Act Information Line - 202/554-1404
Toxics Release Inventory, National Library of Medicine - 301/496-6531
Agency for Toxic Substances and Disease Registry - 404/639-6000
List of Contaminants
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