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Data bank of environmental chemicals     |     The Finnish Environment Institute (SYKE)
 


25.4.2024

Data bank of environmental properties of chemicals


Chemical
1,1,2-Trichloroethane
CAS-number :
79-00-5
 
Synonyms :
1,1,2-trikloorietaani
vinyltrichloride
vinyylitrikloridi
 
Sumformula of the chemical :
C2H3Cl3
EINECS-number :
2011669
 
Uses :
Manufacturing of 1,1-dichloroethylene; solvent for chlorinated
rubber and various organic materials (fats, oils, resins).

Intermediate.
 
State and appearance :
Colourless liquid
 
Molecular weight :
133.4
 
Vapor pressure, mmHg :
19  20°C
 
Water solubility, mg/l :
4500  0°C
10  < 10 mg/l, MITI 1992
 
Melting point, °C :
-35  -35/-36.7
-36.7 
-35.5  MITI 1992
 
Boiling point, °C :
113.7 
113.7 
 
Log octanol/water coefficient, log Pow :
2.13  Anon 1988
 
Log soil sorption coefficient, log Kom :
1.87  observed, Sabljic 1987
1.7  calculated, Sabljic 1987
 
Henry's law constant, Pa x m3/mol :
74  Anon 1988
97.34  calc. Yaws et al. 1991
 
Volatilization :
Relative volatility (nBuAc=1) = 7.5
 
Mobility :
Equilibrium distribution:
        mass %
air     96.16
water    3.76
solid    0.08
(Anon 1988).
 
Photochemical degradation in air :
Photooxidation half-life in air:
196hr - 1956hr,
based upon measured rate constants for reaction with hydroxyl 
radicals in air (Howard 1991).
 
Hydrolysis in water :
First-order hydrolysis half-life:
37yr at pH 7; scientific judgement based upon base catalyzed 
hydrolysis rate constant at 25 °C (Howard 1991).
 
Hydrolysis in base :
Base rate constant 5.9 x 10-3 M-1s-1,
(t1/2 3263hr at pH9); scientific judgement based upon base
catalyzed hydrolysis rate constant at 25 °C (Howard 1991).
 
Half-life in air, days :
8.2  8.2d - 81.5d,
81.5  scientific judgement based upon estimated
  photooxidation half life in air,
  Howard 1991
 
Half-life in soil, days :
136  3263hr - 8760hr,
365  scientific judgement based upon estimated
  hydrolysis half-life at pH 9 and 25 C (low t1/2)
  and data from the estimated unacclimated aerobic
  aqueous biodegradation half-life (high t1/2)
  and a soil column test in which no biodegradation
  was observed,
  Howard 1991
 
Half-life in water, days :
136  3263hr - 8760hr,
365  in surface water, scientific judgement based upon
  estimated hydrolysis half-life at pH 9 and 25 C
  (low t1/2) and estimated unacclimated aerobic
  aqueous biodegradation half-life (high t1/2),
136  3263hr - 17520hr,
730  in ground water, scientific judgement based upon
  estimated hydrolysis half-life at pH 9 and 25 C
  (low t1/2) and data from the estimated unacclimated
  aerobic aqueoous biodegradation half-life
  (high t1/2) and a ground water die-away study in
  which no biodegradation was observed,
  Howard 1991
 
Aerobic degradation in water :
Aerobic half-life:
6mo - 1yr,
scientific judgement based upon the extremely slow or no 
biodegradation which was observed in screening tests and a 
river die-away test (Howard 1991).
 
Anaerobic degradation in water :
Anaerobic half-life:
1yr - 4yr,
scientific judgement based upon estimated aerobic aqueous 
biodegradation half-life (Howard 1991).
 
Total degradation in water :
Biodegradation:
5% by GC analysis
period: 28d
substance: 100 mg/l
sludge: 30 mg/l
(MITI 1992)
 
Bioconcentration factor, fishes :
0.7  0.7 - 2.6, 6w, Cyprinus carpio, conc 0.3 mg/l
2.6 
2.7  2.7 - 6.7, 6w, Cyprinus carpio, conc 0.03 mg/l
6.7  MITI 1992
 
Other information of bioaccumulation :
Confirmed to be non-accumulative or low accumulative 
(Anon. 1987).
 
LD50 values to mammals in oral exposure, mg/kg :
580  orl-rat, Lewis & Sweet 1984
  --
100  100 - 200, orl-rat, Verschueren 1983
200 
  --
1140  orl-rat
 
LD50 values to mammals in non-oral exposure , mg/kg :
3730  skn-rbt, Lewis & Sweet 1984
 
LDLo values to mammals in oral exposure, mg/kg :
500  orl-dog, Lewis & Sweet 1984
 
LCLo values to mammals in inhalation exposure, ppm :
500  8 hr, ihl-rat, Lewis & Sweet 1984
 
Carcinogenicity :
NCI carcinogenesis bioassay completed: results positive, mus;
results negative, rat (Lewis & Sweet 1984).
 
LOEC values to algae, mg/l :
430  rpd, schr, Scenedesmus quadricauda
  Bringmann & Kühn 1980a
 
LC50 values to crustaceans, mg/l :
18  48hr, Daphnia magna, LeBlanc 1980
  --
186  48hr, unfed, Daphnia magna
174  48hr, fed, Daphnia magna
  USEPA 1984
 
EC50 values to crustaceans, mg/l :
80.6  48hr, unfed, Daphnia magna
77.8  48hr, fed, Daphnia magna
  USEPA 1984
 
NOEC values to crustaceans, mg/l :
13.2  13.2 - 26.0, 28d, Daphnia
26  USEPA 1984
 
LC50 values to fishes, mg/l :
40  96 hr, Lepomis macrochirus, Buccafusco
  et al. 1981
  --
94  7d, Poelicia reticulata,Könemann 1979
  --
82  96hr, Pimephales promelas
  Veith et al. 1983
  --
81.6  96hr, flow-through, Pimephales promelas
  USEPA 1984
  --
133  48hr, Oryzias latipes, MITI 1992
  --
81.6  96 hr, Pimephales promelas, Geiger et al. 1986
 
NOEC values to fishes, mg/l :
6.0 - 14.8, 32d, Pimephales promelas
14.8  USEPA 1984

References
2357Anon 1988. Concentrations of industrial organic chemicals measured in the environment: The influence of physico - chemical properties, tonnage and use pattern. Technical report no 29. European chemical industry ecology & toxicology centre, ECETOC. pp. 105.
1848Anon. 1987a. The list of the existing chemical substances tested on biodegradability by microorganisms or bioaccumulation in fish body by Chemicals Inspection & Testing Institute. Ministry of International Trade and Industry, MITI. Japan.
188Bringmann, G. & Kühn, R. 1980a. Comparison of the toxicity thresholds of water pollutants to bacteria, algae and protozoa in the cell multiplication inhibition test. Water Res. 14: 231 - 241.
207Buccafusco, R.J., Ells, S.J. & LeBlanc, G.A. 1981. Acute toxicity of priority pollutants to bluegill (Lepomis macrochirus). Bull. Environ. Contam. Toxicol. 26: 446 - 452.
3296Geiger, D. L. et al. 1985. Acute toxicities of organic chemicals to fathead minnows (Pimephales promelas) Vol. 2. Center for Lake Superior Environmental Studies, University of Wisconsin-Superior, Superior, Winconsin, U.S.A. 326.
3120Howard, P.H., Boethling, R.S., Jarvis, W.F., Meylan, W.M. & Michalenko, E.M., Handbook of Environmental Degradation Rates, 1991. Lewis Publicers, Inc., Chelsea, Michigan, U.S.A., pp. 725.
761Könemann, W.H. 1979. Quantitative structure-activity relationships for kinetics and toxicity of aquatic pollutants and their mixtures in fish. Univ. Utrecht, Netherlands.
798LeBlanc, G.A. 1980. Acute toxicity of priority pollutants to water flea (Daphnia magna). Bull. Environm. Contam. Toxicol. 24: 684 - 691.
1589Lewis, R.J. & Sweet, D.V. 1984. Registry of toxic effects of chemical substances. National Institute for Occupational Safety and Health. No. 83-107-4.
3105MITI 1992. Biodegradation and bioaccumulation data of existing chemicals based on the CSCL Japan. Compild under the Safety Division Basic Industries Bureau Ministry of International Trade & Industry, Japan. Edited by Chemicals Inspection & Testing Institute, Japan.
2324Sabljic, A. 1987. On the prediction of soil sorption coefficients of organic pollutants from molecular structure: application of molecular topology model. Environ. Sci. Technol. 21: 358 - 366.
2757USEPA 1984. Aquatic toxicity tests to characterize the hazard of volatile organic chemicals in water. A toxicity data summary. Part 1. Report No. EPA-600/3-83-009. NITS No. PB84-141506. (Ed): Ahmad, N. et al. U.S. Environmental protection agency, Duluth, MN 55804.
1456Veith, G.D. et al. 1983. Estimating the acute toxicity of narcotic industrial chemicals to fathead minnows. In: Aquatic toxicology and hazard assessment: sixth symposium. ASTM STP 803. Bishop, W.E. et al. (eds.). Am. Soc. Test. Mater, Philadelphia, Pa, 90.
1468Verschueren, K. 1983. Handbook of environmental data of organic chemicals. Van Nostrand Reinhold Co. Inc., New York. 1310 s.
3030Yaws, C., Yang, H-C. & Pan, X. 1991. Henry's law constants for 362 organic compounds in water. Chemical Engineering. November. p 179 - 185.

 
 
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