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


20.4.2024

Data bank of environmental properties of chemicals


Chemical
Chloroform
CAS-number :
67-66-3
 
Synonyms :
Kloroformi
trichloromethane
trikloorimetaani
 
Sumformula of the chemical :
CHCl3
EINECS-number :
2006638
 
Uses :
Manufacturing fluorocarbon refrigerants and propellants and
plastics; manufacturing anesthetics and pharmaceuticals,
primary source for chlorodifluoromethane; fumigant; sweetener;
fire extinguisher manufacturing; electronic circuitry
manufacturing; analytical chemistry; insecticide; solvent.
 
State and appearance :
Colourless liquid.
 
Odor :
Odour index at 20 °C: 70 
(Verschueren 1983).
 
Molecular weight :
119.37
 
Spesicif gravity (water=1) :
1.489  20 °C
 
Vapor density (air=1) :
4.12 
 
Conversion factor, 1 ppm in air=_mg/m3 :
4.96  mg/m3
 
Conversion factor, 1 mg/m3 in air=_ppm :
0.2  ppm
 
Vapor pressure, mmHg :
160  20 °C
245  30 °C
 
Water solubility, mg/l :
9300  25 °C
10000  15 °C
8100  20 °C, Anon 1986b
5000  MITI 1992
 
Melting point, °C :
-64 
-63.5  MITI 1992
 
Boiling point, °C :
62 
61  61 - 62 °C
62  Anon 1986b
61.2  MITI 1992
 
Log octanol/water coefficient, log Pow :
1.97  20 °C
1.97  Anon 1986b
1.97  Schwarzenbach et al. 1983
1.97  Hansch & Leo 1979
1.94  Hansch & Leo 1979
1.9  Banerjee et al. 1980
1.95  Mackay 1982
 
Henry's law constant, Pa x m3/mol :
322  exptl., Dilling 1977
372  exptl., Gossett 1987
410.7  calc. Yaws et al. 1991
 
Volatilization :
Measured half-life for evaporation from 1 ppm aqueous solution,
still air, and an average depth of 6.5 cm:
at 1 - 2 °C: 34.5 min.;
at 25 °C: 18.5 - 25.7 min (Dilling 1977).
 
Mobility :
97.64 % (air), 2.28 % (water), 0.07 % (sediment).
 
Photochemical degradation in air :
Photooxidation half-life in air:
26d - 260d,
based upon measured rate data for the vapor phase reaction with 
hydroxyl radicals in air (Howard 1991).
 
Photochemical degradation in water :
Photooxidation half-life in water:
78.5yr - 3140yr,
based upon measured rate data for hydroxyl radicals in aqueous 
solution (Howard 1991).
 
Hydrolysis in water :
First-order hydrolysis half-life:
3500 yr, scientific judgement based upon reported rate constant
at pH 7 and 25 C (Howard 1991).
 
Half-life in air, days :
26  26d - 260d,
260  based upon photooxidation half-life in air,
  Howard 1991
 
Half-life in soil, days :
28  4w - 6mo,
180  scientific judgement based upon estimated
  aqueous aerobic biodegradation half-life,
  Howard 1991
 
Half-life in water, days :
0.012  = 18.5 - 25.7 min.
0.018  measured, 1 ppm
  aqueous liquid, 25 °C
  --
28  4w - 6mo,
180  in surface water, scientific judgement based upon
  estimated aqueous aerobic biodegradation half-life,
28  8w - 5yr,
1825  in ground water, scientific judgement based upon
  estimated unacclimated aqueous aerobic
  biodegradation half-life and grab sample data
  of aerobic soil from a ground water aquifer,
  Howard 1991
 
Aerobic degradation in water :
Aerobic half-life:
4w - 6mo, 
scientific judgement based upon unacclimated aerobic
screening test data (Howard 1991).
 
Anaerobic degradation in water :
Anaerobic half-life:
1w - 4w,
scientific judgement based upon unacclimated anaeobic screening 
test data (Howard 1991).
 
Total degradation in water :
Biodegradation:
0% by BOD
period: 14d
substance 100 mg/l
sludge 30 mg/l
(MITI 1992)
 
Other information of degradation :
*-------------------------------------------------------------*
ENVIRONMENT  INIT.CONC  REDOX-      TEMP   DEGRADATION    REF.
             mg/l       COND        °C     %/day   t1/2
*-------------------------------------------------------------*
biofilm      0.028      methanogen  22               8 (1)  a
water        0.003      methanogen  35   93/112     11      b
water        0.029      methanogen  35   99/112     16      b
water        0.117      methanogen  35   71/112     63      b
water        0.013      aerobic     20    0/175   >175      b
water        0.029      aerobic     20    0/175   >175      b
water        0.080      aerobic     20    0/175   >175      b
biofilm      0.03       aerobic     22    0/730     -       c
biofilm      0.04       methanogen  22   95/60      15      d
water        0.06       denitrif.   25    0/56     >56      e
biofilm      0.16       methanogen  23     -        33 (1)  f
water (deion.) 1.0      aerobic     25     -       450      g
soil         0.21       aerobic + natural gas -      0.05   h
digestive sludge 238.4  methanogen         5/90   1216      i
dig. sludge      119.2  sulfate reducing  30/90    175      i
water (adapted)  0.354  aerobic           97/11   <2 - 3    i
water (abiotic)    -    aerobic     25      -     3500 yr   j
water            5 - 10 aerobic     25    47/7       -      k
water (adapted)  5 - 10    -        25   100/7      <1      k
soil column      0.90   aerobic     20     5/2      27      l
soil column      0.25   aerobic     20     8/2      17      l
soil          0.6 - 0.8 aerobic     17    <3/7    >160      m
*-------------------------------------------------------------*
(1) biomass concentration set to 0.100 mg/l.
a) Bouwer & McCarty 1985    h) Anon. 1987b
b) Bouwer et al. 1981       i) Kästner 1986 (1000000000 org./ml)
c) Bouwer & McCarty 1982    j) Schwarzenbach 1985
d) Bouwer & McCarty 1983a   k) Tabak et al. 1981
e) Bouwer & McCarty 1983b   l) Wilson et al. 1981
f) Bouwer & Wright 1987     m) Wilson et al. 1983b
g) Dilling et al. 1975      (Anon. 1987b).
 
Bioconcentration factor, fishes :
14d, Lepomis macrochirus, Anon 1986b
1.4  1.4 - 4.7, 6w, Cyprinus carpio, conc 1 mg/l
4.7 
4.1  4.1 - 13, 6w, Cyprinus carpio,conc 0.1 mg/l
13  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 :
908  orl-rat, Lewis & Sweet 1984
36  orl-mus, - " -
800  orl-rat, Anon 1986b
 
LDLo values to mammals in oral exposure, mg/kg :
140  orl-hmn, Lewis & Sweet 1984
2400  orl-mus, Anon 1986b
1000  orl-dog, Anon 1986b
 
TCLo values to mammals in inhalation exposure, mg/kg :
1000  1 y, ihl-hmn, Lewis & Sweet 1984
 
Health effects :
Man: severe toxic effects: 2000 ppm = 9960 mg/m3, 60 min;
symptoms of illness: 500 ppm = 2490 mg/m3;
unsatisfactory: > 50 ppm = 249 mg/m3 
(Verschueren 1983).
 
Carcinogenicity :
NCI carcinogenesis bioassay completed: results positive; mus,
rat (Lewis & Sweet 1984).
 
Maximum longterm immission concentration in air for plants,mg/m3 :
10  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): 125 mg/l
(Bringmann & Kühn 1980a).

EC50 = 435 mg/l, 5 min, Photobakterium phosphoreum,
EC50 = 1013 mg/l, 5 min, Photobakterium phosphoreum
(Anon 1986b).
 
Effects on wastewater treatment :
96%, based upon % degraded under aerobic continuous flow 
conditions (Howard 1991).
 
EC50 values to algae, mg/l :
500  24hr, assimilationtest, Anon 1986b
 
LOEC values to algae, mg/l :
185  srv, Microcystis aeruginosa, Bringmann &
  Kühn 1976
  --
1100  act, Scenedesmus quadricauda
  Bringman & Kühn 1980a
 
LC50 values to crustaceans, mg/l :
29  48hr, Daphnia magna, LeBlanc 1980
28.9  48hr, Daphnia magna, Anon 1986b
 
EC50 values to crustaceans, mg/l :
2140  24hr, Daphnia magna, Anon 1986b
 
LC50 values to fishes, mg/l :
2.03  23d, Salmo gairdneri, embryos
2.03  96 hr, Salmo gairdneri, Birge et al.
  1979
  --
2.09  96hr, Salmo gairdneri
  Black et al. 1982
  --
162  48hr, 162/191 mg/l
191  Leuciscus idus melanotus
66.8  96hr, Salmo gairdneri
43.8  96hr, Salmo gairdneri
18  96hr, Salmo gairdneri
18  96hr, Lepomis macrochirus
115  96hr, Lepomis macrochirus
100  96hr, Lepomis macrochirus
51  96hr, Micropterus salmoides
  Anon 1986b
117  48hr, Oryzias latipes, MITI 1992
  --
70.7  96 hr, Pimephales promelas, Geiger et al. 1990
 
EC50 values to fishes, mg/l :
70.7  96 hr, mbt, Pimephales promelas, Geiger et al. 1990
 
Effects on physiology of water organisms :
Salmo gairdneri, 0.020 mg/l, 4 d, change in enzyme activity
(Castren & Oikari 1987).
 
Other information of water organisms :
Toxicity threshold (cell multiplication inhibition test):
algae (Microcystis aeruginosa): 185 mg/l
(Bringmann & Kühn 1976)

green algae (Scenedesmus quadricauda): 1100 mg/l
protozoa (Entosiphon sulcatum): > 6560 mg/l
(Bringmann & Kühn 1980a)

protozoa (Uronema parduczi): > 6560 mg/l
(Bringmann & Kühn 1980b).

LC50 = 40 mg/l, 3d, (Buto fowleri); LC50 = 35,14 mg/l, 4d,
(Embryos); LC50 = 0.76 mg/l, 3d, (Hyla crucifer);
LC50 = 0.27 mg/l 4d, (Hyla crucifer); LC50 = 28,17 mg/l, 4d,
(Rana palustris); LC50 = 20,55 mg/l, 4d, (Rana palustris);
LC50 = 4.56 mg/l, 5d, (Rana pipiens); LC50 = 4.16 mg/l, 4d,
(Rana pipiens) (Anon 1986b).
 
Other effects on aquatic ecosystems :
Reduction of amenities:
Odour Thresholds: 20 mg/l; 0.1 mg/kg 
(Verschueren 1983).

References
2358Anon 1986b. Beitrag zur Beurteilung von 19 gefährlichen Stoffen in oberirdischen Gewässern. Texte 10. Umweltbundesamt. pp. 163.
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.
2333Anon. 1987b. Nedbrydelighed af miljøfremmede organiske stoffer. Utredningsrapport U1. Lossepladsprojektet.
2605Banerjee, S., Yalkowsky, S. H. and Valvani, S. C. 1980. Environ. Sci. Technol. 14: 1227 - 1229.
148Birge, W.J. et al. 1979b. Toxicity of organic chemicals to embryo-larval stages of fish. EPA-560/11-79-007, U.S. Environmental Protection Agency, Washington, D.C.
155Black, J.A. et al. 1982. The aquatic toxicity of organic compounds to embryo-larval stages of fish and amphibians. PB82-224601, NUS, U.S. Dept. Commerce, Springfield, Va.
2372Bouwer, E.J. & McCarty, P.L. 1982. Removal of trace chlorinated organic compounds by activated carbon and fixed film bacteria. Environ. Sci. & Technol. 16 (2): 836 -843.
2373Bouwer, E.J. & McCarty, P.L. 1983a. Transformation of 1- and 2-carbon halogenated aliphatic organic compunds under methanogenic conditions. Applied and Environmental Microbiology 45 (4): 1286 - 1294.
2370Bouwer, E.J. & McCarty, P.L. 1985. Utilization rates of trace halogenated organic coumpounds in acetate-grown biofilms. Biotechnology and Bioengineering 26: 1564 - 1571.
2375Bouwer, E.J. & Wright, J.P. 1987. Transformation of trace halogenated aliphatics in subsurface microcosms with anoxic biofilms. Submitted to Journal of Contaminant Hydrology.
2371Bouwer, E.J. et al. 1981. Anaerobic degradation of halogenated 1- and 2-carbon organic compounds. Environ. Sci. & Technol. 15 (5): 595 - 602.
2374Bouwer. E.J. & McCarty, P.L. 1983b. Transformation of halogenated organic compounds under denitrification conditions. Applied and Environmental Microbiology 45 (4): 1295 - 1299.
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.
189Bringmann, G. & Kühn, R. 1980b. Bestimmung der biologischen Schadwirkung wassergefahrdender Stoffe gegen Protozoen. II. Bakterienfressende Ciliaten, Z. Wasser/Abwasser Forsch. 1: 26 - 31.
1917Castren, M. & Oikari, A. 1987. Changes of the liver UDP-glucoronosyl-transferase activity in trout (Salmo gairdneri Rich.) acutely exposed to delected aquatic toxicants. Comp. Biochem. Physiol. 86C: 357.
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).
2094Dilling, W.L., Tefertiller, N.B. & Kallos, G.J. 1975. Evaporation rates and reactivities of methylene chloride, chloroform, 1,1,1-trichloroethane, trichloroethylene, tetrachloroethylene, and other chlorinated compounds in dilute aqueous solutions. Environm. Sci. and Techn. 9 (9): 833 - 837.
3297Geiger, D. L. et al. 1990. Acute toxicities of organic chemicals to fathead minnows (Pimephales promelas) Vol 5. Center for Lake Superior Environmental Studies, University of Winsconsin-Superior, Superior, Winconsin, U.S.A. 332.
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.
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.
2369Kästner, M. 1986. Biologische Elimination von leichtfluchtigen Halogenkohlenwasserstoffen (Theoretische Glundlagen und Laborversuche). Fachseminar - Bodensanierung und Grundwasserreinigung - Wiedernutzung von Altstandorten. 24-25/9 1986 in Braunsweig: 155 - 166.
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.
2777Mackay, D. 1982. Correlation of bioconcentration factors. Environ. Sci. Technol., 16(5): 274 - 278.
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.
1973Pilli.A., Carle, D.O., Kline. E., Pickering. Q. & Lazorchak. J. 1988. Effets of pollution on freshwater organisms. JWPCF 60(6): 994 - 1065.
2436Schwarzenbach, R. P., Giger, W., Hoehn, E. and Schneider, J. K. 1983. Behavior of organic compounds during infiltration of river water to groundwater. Field studies. Environ. Sci. Technol. 17 (8): 472 - 479.
2368Schwarzenbach, R.P. 1985. Behaviour and fate of halogenated hydrocarbons in groundwater. In: Ground water quality. ed.: C.H. Ward, W. Giger & P.L. McCarty, Wiley-Interscience Publications, Kap. 24: 446 - 471.
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.
2335Tabak, H.H., Quave, S.A., Mashni, C.I. & Barth, E.F. 1981. Biodegradability studies with organic priority pollutant compounds. Journal WPCF. 53: 1503 - 1518.
1468Verschueren, K. 1983. Handbook of environmental data of organic chemicals. Van Nostrand Reinhold Co. Inc., New York. 1310 s.
2377Wilson, J.T. et al. 1983a. Enumeration and characterization of bacteria indigenous to a shallow water-table aquifer. Ground Water 21 (2): 134 - 142.
2376Wilson, J.T., Enfield, C.G., Dunlap, W.H. et al. 1981. Transport and fate of selected organic pollutants in a sandy soil. J. Environ. Qual. 10 84): 501 - 506.
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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