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


24.4.2024

Data bank of environmental properties of chemicals


Chemical
1,2-dichloroethane
CAS-number :
107-06-2
 
Synonyms :
1,2-dikloorietaani
ethane dichloride
ethylene dichloride
etyleenidikloridi.
glycol dichloride
 
Sumformula of the chemical :
C2H4Cl2
EINECS-number :
2034581
 
Uses :
Manufacturing of vinylchloride; manufacturing of
tetraethyllead; intermediate; insecticidal fumigant; 
ingredient in cosmetics; petrol additive.
 
State and appearance :
Colourless liquid.
 
Odor :
Quality: sweet
Hedonic tone: unpleasant to neutral
Threshold odour concentration
absolute: 6.0 ppm
50 % recognition: 40.0 ppm
100 % recognition: 40.0 ppm
Odour index 100 % recognition: 2 037
(Hellman & Small 1974)
 
Molecular weight :
98.96
 
Vapor pressure, mmHg :
61  20°C
 
Water solubility, mg/l :
8690  20 °C
8100  20 °C
8800  25 °C, McConnell et al. 1975
 
Melting point, °C :
-35.4 
-35.36  Suntio et al. 1988
 
Boiling point, °C :
83.5 
 
Log octanol/water coefficient, log Pow :
1.45  1.45 - 1.79, Sabljic 1987
1.79 
2.82  Anon 1988
1.45  Banerjee et al. 1980
1.48  Hansch & Leo 1979
 
Henry's law constant, Pa x m3/mol :
1000  Anon 1988
1107.1  calc., Dilling 1977
1125  exptl., Gossett 1987
 
Volatilization :
Evaporation from water (1 ppm, 25 °C): 50 % after 29 min; 
90 % after 96 min (Verschueren 1983).

Relative volatility (nBuAc=1) = 6.5
 
Mobility :
84.04 % (air), 15.79 % (water), 0.17 % (sediment).

Equilibrium distribution:
        mass %
air     99.97
water    0.03
solid    0.00
(Anon 1988)
 
Photochemical degradation in air :
Photooxidation half-life in air:
122d - 12.2d, based upon measured rate data for the vapor phase 
reaction with hydroxyl radicals in air (Howard 1991).
 
Hydrolysis in water :
First-order hydrolysis half-life:
1.1yr, scientific judgement based upon rate constant at neutral 
pH (0.63yr-1) (Howard 1991).
 
Half-life in air, days :
122  122d - 12.2d,
12.2  based upon photooxidation half-life in air.
  Howard 1991
 
Half-life in soil, days :
180  6mo - 100d,
100  scientific judgement based upon estimated aqueous aerobic biodegradation half-life.
  Howard 1991
 
Half-life in water, days :
180  6mo - 100d,
100  in surface water: scientific judgement based upon unacclimated grab sample of aerobic soil from ground water aquifers and acclimated river die-away rate data.
360  12mo - 100d,
100  in ground water: scientific judgement based upon unacclimated grab sample of aerobic soil from groun water aquifers and estimated aqueous aerobic biodegradation half-life.
  Howard 1991
 
Aerobic degradation in water :
Aerobic half-life:
6mo - 100d, scientific judgement based upon unacclimated grab 
sample of aerobic soi from ground water aquifers and acclimated 
river die-away rate data (Howard 1991).
 
Anaerobic degradation in water :
Anaerobic half-life:
24mo - 400d, (Howard 1991).
 
Other information of bioaccumulation :
Confirmed to be non-accumulative or low accumulative (Anon. 
1987).
 
LD50 values to mammals in oral exposure, mg/kg :
670  orl-rat, Lewis & Sweet 1984
489  orl-mus, - " -
860  orl-rbt, - " -
 
LD50 values to mammals in non-oral exposure , mg/kg :
4886  skn-rbt, Lewis & Sweet 1984
 
LC50 values to mammals in inhalation exposure, ppm :
1000  432 min., ihl-rat, Verschueren 1983
 
LDLo values to mammals in oral exposure, mg/kg :
810  orl-man, Lewis & Sweet 1984
600  orl-mus, Lewis & Sweet 1984
2000  orl-dog, Lewis & Sweet 1984
 
LDLo values to mammals in non-oral exposure , mg/kg :
500  scu-rat, Lewis & Sweet 1984
380  scu-mus
1200  scu-rbt
600  ipr-gpg
175  ivn-dog
 
LCLo values to mammals in inhalation exposure, mg/kg :
5000  ihl-mus, Lewis & Sweet 1984
 
LCLo values to mammals in inhalation exposure, ppm :
3000  7hr, ihl-pig, Lewis & Sweet 1984
3000  7hr, ihl-rbt
1500  7hr, ihl-gpg
1000  4hr, ihl-rat
 
TDLo values to mammals in oral exposure, mg/kg :
38  orl-mus, Lewis & Sweet 1984
18  orl-rat
428  orl-hmn
 
TDLo values to mammals in non-oral exposure , mg/kg :
1120  skn-mus, Lewis & Sweet 1984
 
TCLo values to mammals in inhalation exposure, ppm :
4000  ihl-hmn, Lewis & Sweet 1984
 
Carcinogenicity :
NCI carcinogenesis bioassay completed: results positive; mus,
rat (Lewis & Sweet 1984).
 
Maximum longterm immission concentration in air for plants,mg/m3 :
VDI 2306
 
Maximum longterm immission concentration in air for plants,ppm :
VDI 2306
 
Effects on microorganisms :
Toxicity threshold (cell multiplication inhibition test):
bacteria (Pseudomonas putida): 135 mg/l
(Bringmann & Kühn 1980a)
 
EC50 values to microorganism, mg/l :
1100  15 min Microtox, Hermens et al. 1985
 
LOEC values to algae, mg/l :
105  rpd,schr, Microcystis aeruginosa,
  Bringmann & Kühn 1976
 
LC50 values to crustaceans, mg/l :
220  srv,act, 48 hr, Daphnia magna, LeBlanc
  1980
65  srv,act, 96 hr, Crangon crangon, Adema
  1976
  --
268  48hr, unfed, Daphnia magna
315  48hr, fed, Daphnia magna
  USEPA 1984
 
EC50 values to crustaceans, mg/l :
155  48hr, unfed, Daphnia magna
183  48hr, fed, Daphnia magna
  USEPA 1984
 
NOEC values to crustaceans, mg/l :
10.6  10.6 - 20.7, 28d, Daphnia
20.7  USEPA 1984
 
LC50 values to fishes, mg/l :
106  srv,act, 7 d, Poecilia reticulata,
  Könemann 1979
118  srv,act, 96 hr, Pimephales promelas,
  Veith et al. 1983
430  srv,act, 96 hr, Lepomis macrochirus,
  Buccafusco et al. 1981
185  srv,act, 96 hr, Gobius minutus, Adema
  1976
  --
116  96hr, flow-through, Pimephales promelas
  USEPA 1984
  --
136  96 hr, Pimephales promelas, Geiger et al. 1985
 
LOEC values to fishes, mg/l :
0.059  grw,schr, Pimephales promelas, Benoit et
  al. 1982
 
NOEC values to fishes, mg/l :
0.029  grw,schr, Pimephales promelas, Benoit et
  al. 1982
  --
29  29.0 - 59.0, 32d, Pimephales promelas
59  USEPA 1984
 
Other information of water organisms :
Toxicity threshold (cell multiplication inhibition test):
green algae (Scenedesmus quadricauda): 710 mg/l
protozoa (Entosiphon sulcatum): 1127 mg/l
(Bringmann & Kühn 1980a)

References
13Adema, D.M.M., 1976. Acute toxiciteitstoetsen met 1,2-dichloorethaan, fenol, acrylonitrile, en alkylbenzenesulfonaat in zeewater. Central laboratory TNO, 97 Schoemakerstraat-P.O. Box 217, Delft, The Netherlands.
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.
2605Banerjee, S., Yalkowsky, S. H. and Valvani, S. C. 1980. Environ. Sci. Technol. 14: 1227 - 1229.
135Benoit, D.A., Puglisi F.A. & Olson, D.L. 1982. Fathead minnow (Pimephales promelas) early life stage toxicity test method evaluation and exposure to four organic chemicals. Environ. Pollut. 28: 189 - 197.
187Bringmann, G. & Kühn, R. 1976. Vergleichende Befunde der Schadwirkung wassergefährdender Stoffe gegen Bakterien (Pseudomonas putida) und Blaualgen (Microcystis aeruginosa). Gwf-Wasser-Abwasser 117(9).
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.
2088Dilling, W.L. 1977. Interphase transfer processes: evaporation rates of chloromethanes, -ethanes, - ethylenes, -propanes and -propylenes from dilute aqueous solutions. Comparisons with theoretical predictions. Environm. Sci. & Techn. 11(4).
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.
2660Gossett, J. M. 1987. Environ. Sci. Technol. 21: 202 - 208.
2622Hansch, C. & Leo, A. 1979. Substituent Constant for Correlation Analysis in Chemistry and Biology. Wiley: New York.
1673Hellman, T.M. & Small, F.H. 1974. Characterization of the odour properties of 101 petrochemicals using sensory methods. J. Air Pollut. Control Assoc. 24: 979 - 982.
2414Hermens, J. et al. 1985c. Quantitative structure activity relationships and mixture of toxicity studies of organic chemicals in Photobacterium phosphoreum: Microtox test. Ecotox. Environ. Safety 9: 17.
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.
2633McConnell, G., Ferguson, D. M. and Pearson, C. R. 1975. Endeavour 34: 13.
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.
2602Suntio, L. R., Shiu, W. Y. and Mackay, D. 1988. A review of the nature and properties of chemicals present in pulp mill effluents. Chemosphere 17(7): 1249 - 1290.
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.
1599VDI 2306. VDI-Kommission Reinhaltung der Luft. Maximale Immissions-Konzentrationen (MIK). Organische Verbildungen.
1468Verschueren, K. 1983. Handbook of environmental data of organic chemicals. Van Nostrand Reinhold Co. Inc., New York. 1310 s.
2413Walker, J. D. 1987. Effects of chemicals on microorganisms. Journal WPCF 59 (6): 614 - 625.

 
 
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