www.ymparisto.fi
 
 
Data bank of environmental chemicals     |     The Finnish Environment Institute (SYKE)
 


9.5.2024

Data bank of environmental properties of chemicals


Chemical
1,4-Dioxane
CAS-number :
123-91-1
 
Synonyms :
1,4-diethylene dioxide
1,4-dioksaani
1,4-dioxacyclohexane
diethylene dioxide
diethylene ether
dietyleenieetteri
dioxan
dioxyethylene ether
glycol ethylene ether
p-dioksaani
p-dioxan
p-dioxane
tetrahydro-1,4-dioxin.
tetrahydro-p-dioxin
 
Sumformula of the chemical :
C4H8O2
EINECS-number :
2046618
 
Uses :
Solvent for cellulosics and wide range of organic products; 
lacquers; paints; varnish.
 
Odor :
Quality: sweet, alcohol Hedonic tone: pleasant 
Threshold odour concentration absolute: 0.80 ppm 
                       50 % recognition: 1.8 ppm 
                      100 % recognition: 5.7 ppm 
Odour index 100 % recognition: 6 228 
(Hellman & Small 1974)
 
Molecular weight :
88.12
 
Vapor pressure, mmHg :
30  20 °C
30  4000 Pa/20°C, EU RA Report 2002
 
Melting point, °C :
10 
10  10.0-11.9, MITI 1992
11.9 
 
Boiling point, °C :
101 
 
Log octanol/water coefficient, log Pow :
-0.27  EU RA Report 2002
 
Henry's law constant, Pa x m3/mol :
0.6964  calc. Yaws et al. 1991
 
Volatilization :
Relative volatility (nBuAc=1) = 2.72
 
Photochemical degradation in air :
1,4-Dioxane have two possible photo-degradation routes:
direct photolysis and photo-oxidation through reaction with free OH-radicals or ozone. 
Studies of direct photolysis of liquid 1,4-dioxane at 185 nm give following products: 
formaldehyde, glycol monovinyl ethe and ethylene. Gas-phase photolysis at 147 nm gives principal 
products of formaldehyde and ethylene. 
Since the wavelength of light in the troposphere is greater than 290 nm, photolysis does 
not occur in the lower atmosphere (EU RA Report 2002)

Photo-oxidation of 1,4-dioxane in air and water:
A photo-oxidation reaction in air with OH-radicals - half-ife is 29 hours.
An experimental photo-oxidation in the presence of nitrogen monoxide - half-life is measured 
to be 3.4 hours. 
A half-life of 60 hours for 1,4-dioxane in water with ozone.
(EU RA Report 2002).
Photooxidation half-life in air:
 0.7hr - 7.0hr,
scientific judgement based upon estimated rate constant for
reaction with hydroxyl radical in air (Howard 1991).
 
Photochemical degradation in water :
Photooxidation half-life in water:
 67d - 9.1yr,
based upon measured rates for reaction with hydroxyl radicals
in water (Howard 1991).
 
Half-life in air, days :
0.34  0.34d - 3.4d,
3.4  based upon photooxidation half-life in air,
  Howard 1991
 
Half-life in soil, days :
28  4w - 6mo,
180  scientific judgement based upon estimated unacclimated
  aqueous aerobic biodegradation half-life,
  Howard 1991
 
Half-life in water, days :
28  4w - 6mo,
180  in surface water, based upon estimated unacclimated
  aqueous aerobic biodegradation half-life,
28  8w - 12mo,
360  in ground water, scientific judgement based upon
  estimated unacclimated aqueous aerobic
  biodegradation half-life,
  Howard 1991
 
Aerobic degradation in water :
Aerobic half-life:
4w - 6mo, scientific judgement based upon unacclimated aerobic
aqueous screening test data which confirmed resistance 
to biodegradation (Howard 1991).
 
Anaerobic degradation in water :
Anaerobic half-life:
16w - 24mo, scientific judgement based upon estimated aerobic
biodegradation half-life (Howard 1991).
 
Total degradation in water :
Biodegradation:
0% by BOD
period: 14d
substance: 100 mg/l
sludge: 30 mg/l
(MITI 1992)
 
Ready biodegradability :
Confirmed to be non-biodegradable (Anon. 1987).
 
Bioconcentration factor, fishes :
0.2  0.2 - 0.6, 6w, Cyprinus carpio, conc 10 mg/l,
0.6 
0.3  0.3 - 0.7, 6w, Cyprinus carpio, conc 1 mg/l,
0.7  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 :
4200  orl-rat,Lewis & Sweet 1984
2000  orl-cat,orl-rbt
  --
3150  orl-gpg, Sweet 1987
5700  orl-mus
 
LD50 values to mammals in non-oral exposure , mg/kg :
7600  skn-rbt,Lewis & Sweet 1984
  --
790  ipr-mus, Sweet 1987
5600  ipr-rat
 
LC50 values to mammals in inhalation exposure, mg/m3 :
65000  2hr, ihl-mus, Sweet 1987
46000  2hr, ihl-rat
 
LDLo values to mammals in non-oral exposure , mg/kg :
1500  ivn-cat, Sweet 1987
1500  ivn-rbt
 
LCLo values to mammals in inhalation exposure, mg/kg :
44000  ihl-cat, 7hr, Sweet 1987
 
LCLo values to mammals in inhalation exposure, ppm :
470  3d, ihl-hmn,Lewis & Sweet 1984
 
TDLo values to mammals in oral exposure, mg/kg :
10000  orl-rat, 6-15d preg.
  effects on embryo or fetus
  specific developmental abnormalities
  Sweet 1987
  --
239000  orl-mus, tumorigenic
185000  orl-rat, tumorigenic
  Sweet 1987
 
TDLo values to mammals in non-oral exposure , mg/kg :
12000  ipr-mus, tumorigenic, Sweet 1987
14000  skn-mus, tumorigenic
 
TCLo values to mammals in inhalation exposure, ppm :
111  ihl-rat, tumorigenic, Sweet 1987
  --
470  ihl-hmn, Sweet 1987
5500  ihl-hmn, 1 min
 
Other information of mammals :
Skin and eye irritation data:
eye, human, 300 ppm, 15 min;
skin, rabbit, 515 mg open, mild;
eye, rabbit, 21 mg;
eye, guinea pig, 0.010 mg, moderate 
(Sweet 1987).
 
Carcinogenicity :
NCI carcinogenesis bioassay (oral); clear evidence: mouse, rat 
(Sweet 1987).
 
Mutagenicity :
Mutation data:
DNA damage:
rat, liver, 0.3 mmol/l;
unscheduled DNA synthesis:
rat,oral; 20 mg/kg;
test systers (other):
rat,intravenous, 50 mg/kg
(Sweet 1987).
 
LOEC values to algae, mg/l :
575  rpd,schr, Microcystis aeruginosa,
  Bringmann & Kühn 1976
 
LC50 values to fishes, mg/l :
6700  srv,act, 96 hr, Menidia audens,
  Dawson et al. 1977
  --
10500  48hr, Oryzias latipes, MITI 1992
  --
9850  96 hr, Pimephales promelas
10800  96 hr, Pimephales promelas, Geiger et al. 1990
 
EC50 values to fishes, mg/l :
9340  96 hr, mbt, Pimephales promelas
9550  96 hr, mbt, Pimephales promelas, Geiger et al. 1990

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.
187Bringmann, G. & Kühn, R. 1976. Vergleichende Befunde der Schadwirkung wassergefährdender Stoffe gegen Bakterien (Pseudomonas putida) und Blaualgen (Microcystis aeruginosa). Gwf-Wasser-Abwasser 117(9).
327Dawson, G.W., Jennings, A.L., Drozdowski, D. & Rider, E. 1977a. The acute toxicity of 47 industrial chemicals to fresh and saltwater fishes. J. Hazardous Materials 1 (1975/77): 303 - 318.
3358EU RA Report 2002. Existing Substances: 1,4-dioxane. European Union Risk Assessment Report (Vol 21). Institute for Health and Consumer Protection. European Chemicals Bureau. European Communities.
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.
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.
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.
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.
2101Sweet, D. 1987. Registry of toxic effects of chemical substances 1985 - 1986 edition. U.S. Department of health and human services.
3030Yaws, C., Yang, H-C. & Pan, X. 1991. Henry's law constants for 362 organic compounds in water. Chemical Engineering. November. p 179 - 185.

 
 
© Copyright Environmental Administration