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


19.4.2024

Data bank of environmental properties of chemicals


Chemical
Captan
CAS-number :
133-06-2
 
Synonyms :
1H-Isoindole-1,3(2H)-dione, 3a,4,7,7a-tetrahydro-2- [(trichloromethyl)thio]-
3a,4,7,7a-tetrahydro-N-(trikloorimetaanisulfenyyli)ftaalimidi
cis-N-((trichloromethyl)thio)-4-cyclohexene-1,2-dicarboximide.
kaptaani
N-((trichloromethyl)thio)-4-cyclohexene-1,2-dicarboximide
N-trichloromethylthiotetrahydrophthalimide
 
Sumformula of the chemical :
C9H8Cl3NO2S
EINECS-number :
2050870
 
Uses :
Protectant-eradicant fungicide.
 
State and appearance :
White solid.
 
Molecular weight :
300.59
 
Water solubility, mg/l :
0.5  < 0.5, 20°C
 
Melting point, °C :
175 
 
Log octanol/water coefficient, log Pow :
2.35 
 
Photochemical degradation in air :
Photooxidation half-life air:
32hr - 3.2hr, scientific judgement based upon an estimated rate 
constant for the vapor phase reaction with hydroxyl radicals in 
air (Howard 1991).
 
Hydrolysis in water :
First-order hydrolysis half-life:
1.8hr, scientific judgement based upon first order rate 
constant (6.5X10-3 s-1) at pH 7.1 and 28 °C (Howard 1991).
 
Hydrolysis in acid :
Acid rate constant (M(H+)-hr)-1:
1.87X10-5 s-1, (t1/2 = 10.3hr) based upon first order rate 
constant at pH 5.2 and 28 °C (Howard 1991).
 
Hydrolysis in base :
Base rate constant (M(OH-)-hr)-1:
1.1X10-3 s-1, (t1/2 = 10.5min) based upon first order rate 
constant at pH 8.3 and 28 °C (Howard 1991).
 
Half-life in air, days :
1.33  32hr . 3.2,
0.13  scientific judgement based upon estimated photooxidation half-life in air.
  Howard 1991
 
Half-life in soil, days :
Li et al. 1990
  --
60  60d - 2d,
scientific judgement based upon unacclimated and acclimated soil grab sample data.
  Howard 1991
 
Half-life in water, days :
0.43  10.3hr - 10.5min,
0.0073  in surface water: scientific judgement based upon aqueous hydrolysis half-lives for pH 5.2 (high t1/2) and 8.3 (low t1/2) at 28 °C.
0.43  10.3hr - 10.5min,
0.0073  in ground water: scientific judgement based upon aqueous hydrolysis half-lives for pH 5.2 (high t1/2) and 8.3 (low t1/2) at 28 °C.
  Howard 1991
 
Aerobic degradation in water :
Aerobic half-life:
60d - 2d, scientific judgement based upon unacclimated and 
acclimated soil grab sample data (Howard 1991).
 
Anaerobic degradation in water :
Anaerobic half-life:
240d - 8d, scientific judgement based upon unacclimated aerobic 
biodegradation half-life (Howard 1991).
 
LD50 values to mammals in oral exposure, mg/kg :
9000  orl-rat, Anon. 1976
740  orl-rbt, Lewis & Sweet 1984
 
Other information of mammals :
In diet: no effect level from 2 years dietary tests on rats;
1000 mg/kg (Martin 1968).
 
Carcinogenicity :
Carcinogenic (McCann et al. 1975).

NCI carcinogenesis bioassay completed: results positive, mus;
results negative, rat (Lewis & Sweet 1984).
 
Mutagenicity :
Mutagenicity in the Salmonella test positive (without liver
homogenate):
25 revertant colonies/nmol;
820 revertant colonies at 0.010 mg/plate
(McCann et al. 1975).
 
LD50 values to birds in oral exposure, mg/kg :
100  100 - 104, orl-Agelaius phoeniceus
104 
100  >100, orl-Passer domesticus
100  >100, orl-Quiscalus quiscula
100  >100, orl-Corvus brachyrhynchos
  Schafer et al. 1983
 
Effects on plants :
Development of mycorrhizal fungi in roots of sour orange
(Citrus aurantium) seedlings was reduced by spraying of soil
with 9.0 kg captan (50 %) /ha  (Nemec 1980).
 
LC50 values to crustaceans, mg/l :
1.5  srv,act, Daphnia pulex, Hashimoto &
  Nishiuchi 1981
 
LC50 values to fishes, mg/l :
0.04  srv,act, 48 hr, Carassius auratus,
0.25  srv,act, 48 hr, Cyprinus carpio,
  Hashimoto & Nishiuchi 1981
  --
0.3  srv,act, 96 hr, Rasbora heteromorpha,
  Tooby et al. 1975
 
LOEC values to fishes, mg/l :
0.04  srv,chr, Pimephales promelas,
  Hermanutz et al. 1973
 
NOEC values to fishes, mg/l :
0.017  rpd,grw, Pimephales promelas,
  Hermanutz et al. 1973

References
63Anon. 1976. Pesticide Dictionary 1976. Farm Chemicals, Meister Publishing Company, 37841 Euclid Avenue, Willoughby, Ohio 44094.
550Hashimoto, Y. & Nishiuchi Y. 1981. Establishment of bioassay methods for the evaluation of acute toxicity of pesticides to aquatic organisms. J. Pestic. Sci. (Jap.) 6: 257.
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.
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.
2450Li, W.,Merrill, D. E. & Haith, A. 1990. Loading functions for pesticide runoff. Research Journal WPCF, 62(1): pp. 16 - 26.
897Martin, H. 1968. Pesticide manual, British crop protection council, Clacks Farm, Boreley, Ombersley, Droitwich, Worcester, U.K.
912McCann, J. et al. 1975. Detection of carcinogens as mutagens in the Salmonella/microsome test: Assay of 300 chemicals, Proc. Nat. Acad. Sci. USA, 72(12): 5135-5139 Medical Sciences, Dec.
1726Nemec, S. 1980. Effects of 11 fungicides on endomycorrhizal development in sour orange. Can. J. Bot. 58(5): 522 - 526.
1743Schafer , E.W.Jr., Bowles, W.A.Jr., Hurlbut, J. 1983. The acute oral toxicity, repellency and hazard potential of 993 chemicals to one or more species of wild and domestic birds. Arch. Environ. Contam. Toxicol. 12: 355 - 382.
1427Tooby, T.E., Hursey, P.A. & Alabaster, J.S. 1975: The acute toxicity of 102 pesticides and miscellaneous substances to fish. Chemistry and Industry 21: 523-525.
1468Verschueren, K. 1983. Handbook of environmental data of organic chemicals. Van Nostrand Reinhold Co. Inc., New York. 1310 s.

 
 
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