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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
Catechol
CAS-number :
120-80-9
 
Synonyms :
1,2-Benzenediol
1,2-dihydroksibentseeni
1,2-Dihydroxybenzene
catechin.
Katekoli
o-Dihydroxybenzene
o-diphenol
o-hydroquinone
o-hydroxyphenol
o-phenylenediol
oxyphenic acid
pyrocatechol
pyrokatekoli
 
Sumformula of the chemical :
C6H6O2
EINECS-number :
2044275
 
Uses :
Preparation of dyes, pharmaceuticals, production of
anti-oxidants for rubber and lubricatory oils. 
It is also used
in photography, in rubber, in fur dyeing and in specialty inks as
an agent for oxygen removal.
 
State and appearance :
Colourless leaflets.
 
Molecular weight :
110.12
 
Spesicif gravity (water=1) :
1.371  15 °C
 
Vapor density (air=1) :
3.79 
 
Conversion factor, 1 ppm in air=_mg/m3 :
4.5  mg/m3
 
Conversion factor, 1 mg/m3 in air=_ppm :
0.22  ppm
 
Water solubility, mg/l :
451000  20°C
  Sol, MITI 1992
 
Melting point, °C :
105 
104  104 - 105, MITI 1992
 
Boiling point, °C :
240  240 - 245, MITI 1992
 
Degradation point, °C :
240 
 
Log octanol/water coefficient, log Pow :
0.88 
1.01 
 
Photochemical degradation in air :
Photooxidation half-life in air:
26hr - 2.6hr, based upon estimated reaction rate constant with 
.OH (Howard 1991)
 
Photochemical degradation in water :
Photooxidation half-life in water:
160d - 3.2d, scientific judgement based upon reported reaction 
rate constants for RO2. with the phenol class (Howard 1991).
 
Other chemical degradation processes :
Ozonation: catechol + O3 -> o-quinone (Eisenhauer 1968).

Autoxidation at 25 °C: t1/2: 447 hr at pH 7.0
                             412 hr at pH 9.0
                             (Moussavi 1979).
 
Half-life in air, days :
1.08  26hr - 2.6hr,
0.1  based upon estimated photooxidation half-lives in air.
  Howard 1991
 
Half-life in soil, days :
1w - 1d,
scientific judgement based upon estimated aqueous aerobic biodegradation half-lives.
  Howard 1991
 
Half-life in water, days :
1w - 1d,
in surface water: scientific judgement based upon the estimated aqueous aerobic biodegradation half-life.
14  2w - 2d,
in ground water: scientific judgement based upon estimated aqueous aerobic biodegradation half-lives.
  Howard 1991
 
Aerobic degradation in water :
Aerobic half-life:
7d - 1d, scientific judgement based upon aerobic biological 
screening test data (Howard 1991).
 
Anaerobic degradation in water :
Anaerobic half-life:
28d - 4d, scientific judgement based upon estimated aqueous 
aerobic biodegradation half-lives (Howard 1991).
 
Total degradation in soil :
Biodegradation: decomposition by a soil microflora: 1 day
(Verschueren 1983).
 
Total degradation in water :
Biodegradation:
83% by BOD
substance: 100 mg/l
sludge: 30 mg/l
(MITI 1992)
 
Ready biodegradability :
Confirmed to be biodegradable (Anon. 1987).
 
Other information of degradation :
Routes for degradation of catechol by microorganisms:

catechol                         catechol
   I                                I
'ortho'cleavage                  'meta'cleavage
   I O2                             I O2
   V                                V
cis,cis-muconate                  2-hydroxymuconic semialdehyde

   I                                I
   V                            H2O -> HCOOH
(+)-muconolactone                   I
   I                                V
   V                              2-oxo-pent-4-enoate
3-oxoadipate enol lactone           I  H2O
   I  H2O                           V
   V                              4-hydroxy-2-oxovalerate
3-oxoadipate                        I
   I                                V
   V                              acetaldehyde pyruvate
3-oxoadipyl CoA
   I
   V
Acetyl-CoA + succinate

(Verschueren 1983).
 
LD50 values to mammals in oral exposure, mg/kg :
358  orl-rat, Lewis & Sweet 1984
260  orl-mus, - " -
240  orl-mam, - " -
 
LD50 values to mammals in non-oral exposure , mg/kg :
800  skn-rbt, Lewis & Sweet 1984
 
LDLo values to mammals in oral exposure, mg/kg :
100  orl-cat, Lewis & Sweet 1984
 
LD50 values to birds in oral exposure, mg/kg :
100  >100, orl-Agelaius phoeniceus
  Schafer et al. 1983
 
Effects on microorganisms :
Bacteria: Escherichia coli: LD0: 90 mg/l (Meinck et al. 1970).
 
LC50 values to fishes, mg/l :
8.9  96 hr, Salmo gairdneri, DeGraeve et al.
  1980
3.5  96 hr, Pimephales promelas, - " -
  --
9.22  96 hr, Pimepahles promelas, Geiger et al. 1990
 
EC50 values to fishes, mg/l :
96 hr, mbt, Pimephales promelas, Geiger et al. 1990
 
Other information of water organisms :
Algae: Scenedesmus: LD0: 6 mg/l
Protozoa: Vorticella campanula: LD0: 1.6 mg/l
          Paramaecium caudatum: LD0: 35 mg/l
Arthropoda: Daphnia: LD0: 4 mg/l
Fish: Trutta iridea: perturbation level: 3 mg/l
      Cyprinus carpio: perturbation level: 2.8 mg/l
      (Meinck et al. 1970).

Goldfish: approximate fatal concentration: 14 mg/l, 48 hr
(McKee & Wolf 1963).
 
Other effects on aquatic ecosystems :
Reduction of amenities:
taste in fish (carp): 2.5 mg/l (Jones 1971)
tainting of fish flesh: 2 - 5 mg/l (Verschueren 1983)
odour threshold (detection): 8.0 mg/l (Verschueren 1983).

References
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.
331DeGraeve, G.M. et al. 1980. Toxicity of underground coal gasification condenser water and selected constituents to aquatic biota. Arch. Environ. Contam. Toxicol. 9: 543.
330DeGraeve, G.M., Geiger, D.L., Meyer, J.S. & Bergman, H.L. 1980. Acute and embryo-larval toxicity of phenolic compounds to aquatic biota. Arch. Environ. Contam. Toxicol. 9: 557 - 568.
1962Eisenhauer, H.R. 1968. The ozonation of phenolic wastes. JWPCF 40: 1887.
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.
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.
675Jones, H.R. 1971. Environmental control in the organic and petrochemical industries. Noyes Data Corporation 1971.
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.
921McKee, J.W. & Wolf, H.W. 1963. Water quality criteria. The Resources Agency of California, State Water Quality Control Board.
950Meinck, F., Stoof, H. & Kohlschutter, H. 1970. Les eaux residuaires industrielles.
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.
1963Moussavi, M. 1979. Effect of polar substituents on autoxidation of phenols. Water Res. 13: 1125 - 1128.
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.
1468Verschueren, K. 1983. Handbook of environmental data of organic chemicals. Van Nostrand Reinhold Co. Inc., New York. 1310 s.

 
 
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