| Chemical |
2,6-toluenediisocyanate |
| CAS-number : |
91-08-7 |
| |
| Synonyms : |
| 2,6-diisocyanato-1-methylbenzene |
| 2,6-diisocyanatotoluene |
| 2,6-TDI |
| 2,6-tolueenidi-isosyanaatti |
| 2-methyl-meta-phenyleneisocyanate |
| isocyanic acid,2-methyl-meta-phenylene ester |
| tolueenidi-isosyanaatti. |
| toluene diisocyanate |
| toluene-2,6-diisocyanate |
| |
| Sumformula of the chemical : |
| C9H6N2O2 |
| EINECS-number : |
| 2020390 |
| |
| State and appearance : |
TDI (mixture) is a clear-to-yellow flammable, volatile liquid
with a sweet, pungent odor.
|
| |
| Odor : |
USSR: human odour perception; non perception: 0.15 mg/m3;
perception: 0.020 mg/m3;
human reflex response; no response: 0.050 mg/m3;
adverse response: 0.1 mg/m3;
animal chronic exposure: no effect: 0.02 mg/m3;
adverse effect: 0.2 mg/m3
(Verschueren 1983).
|
| |
| Molecular weight : |
174.17 |
| |
| Conversion factor, 1 ppm in air=_mg/m3 : |
| 7.24 |
mg/m3 |
| |
| Conversion factor, 1 mg/m3 in air=_ppm : |
| 0.14 |
ppm |
| |
| Boiling point, °C : |
| 129 |
129 - 133 °C, at 18 °C, HSDB 1999 |
| 133 |
|
| |
| Volatilization : |
The vapor pressure of commercial toluene diisocyanate (80% 2,4-
and 20% 2,6-isomer) is 0.02 mmHg at 20 °C, suggesting that
spilled TDI will not readly volatilize from soil and surfaces.
TDI reacts with water; therefore volatilization from water is
not expected to be important (HSDB 1999).
|
| |
| Photochemical degradation in air : |
Photooxidation half-life in air:
3.21hr - 0.321hr, scientific judgement based upon estimated
rate constant for reaction with hydroxyl radical in air
(Howard 1991).
The half-life for toluene diisocyanate in the atmosphere is 3.3
hours by reaction with photochemically producted hydroxyl
radicals (HSDB 1999).
|
| |
| Hydrolysis in water : |
First-order hydrolysis half-life:
12hr, scientific judgement based upon observed disappearance of
toluene diisocyanate in a model river (Howard 1991).
|
| |
| Half-life in air, days : |
| 0.13 |
3.21hr - 0.32hr, |
| 0.013 |
scientific judgement based upon estimated photooxidation halflife in air. |
| |
Howard 1991 |
| |
| Half-life in soil, days : |
| 1 |
24hr - 12hr, |
| 0.5 |
scientific judgement based upon estimated hydrolysis half-life in water. |
| |
Howard 1991 |
| |
| Half-life in water, days : |
| 1 |
24hr - 12hr, |
| 0.5 |
in surface water: scientific judgement based upon estimated hydrolysis half-life in water, |
| 1 |
24hr - 12hr, |
| 0.5 |
in ground water: scientific judgement based upon estimated hydrolysis half-life in water. |
| |
Howard 1991 |
| |
| Aerobic degradation in water : |
Aerobic half-life:
4w - 7d, scientific judgement (Howard 1991).
|
| |
| Anaerobic degradation in water : |
Anaerobic half-life:
16w - 28d, scientific judgement based upon estimated
unacclimated aerobic aqueous biodegradation half-life
(Howard 1991).
|
| |
| Other information of degradation : |
When low concentrations of TDI (2,4- and 2,6-isomers) are
released into model river or seaway systems, it is hydrolyzed
with in a day (HSDB 1999).
Toluene diisocyanates are expected to be hydrolyzed much more
rapidly than they are attacked by microorganisms (HSDB 1999).
|
| |
| LC50 values to mammals in inhalation exposure, mg/m3 : |
| 91 |
4 hr, ihl-mus, Lewis & Sweet 1984 |
| |
| TCLo values to mammals in inhalation exposure, ppm : |
| 0.08 |
ihl-hmn, Lewis & Sweet 1984 |
| |
-- |
| 0.05 |
ihl-hmn, sense organs and special |
| |
senses |
| |
lungs, thorax or respiration |
| |
| Mutagenicity : |
Mutation data:
microsomal assay;
Salmonella typhimurium, 0.010 mg/plate (Sweet 1987).
|
| |
| LD50 values to birds in oral exposure, mg/kg : |
| 100 |
orl-bdw, Sweet 1987 |
| |
-- |
| 100 |
orl-Agelaius phoeniceus |
| 100 |
=,>100, orl-Sturnus vulgaris |
| |
Schafer et al. 1983 |
| |
| Maximum longterm immission concentration in air for plants,mg/m3 : |
| 0.007 |
VDI 2306 |
| |
| Maximum longterm immission concentration in air for plants,ppm : |
| 0.001 |
VDI 2306 |
| |
| LC50 values to fishes, mg/l : |
| 164 |
96 hr, Pimephales promelas, Curtis et |
| |
al. 1979 |
| |
| Other information of water organisms : |
Grass shrimp (Palaemonetes pugio): no significant mortality
below 508 mg/l (Verschueren 1987).
|
References |
| 300 | Curtis, M.W., Copeland, T.L. & Ward, C.H. 1979.
Acute
toxicity of 12 industrial chemicals to freshwater and
saltwater organisms.
Water Res. 13: 137 - 141. |
| 3120 | Howard, 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.
|
| 3114 | HSDB Database 1992 -.
Hazardous Substances Data Bank.
US.
National Library of Medicine.
TOMES Plus CD-ROM.
|
| 1589 | Lewis, R.J. & Sweet, D.V. 1984.
Registry of toxic effects of
chemical substances.
National Institute for Occupational Safety
and Health.
No. 83-107-4. |
| 1743 | Schafer , 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. |
| 2101 | Sweet, D. 1987.
Registry of toxic effects of chemical
substances 1985 - 1986 edition.
U.S.
Department of health and
human services. |
| 1599 | VDI 2306.
VDI-Kommission Reinhaltung der Luft.
Maximale
Immissions-Konzentrationen (MIK).
Organische Verbildungen. |
| 1468 | Verschueren, K. 1983.
Handbook of environmental data of
organic chemicals.
Van Nostrand Reinhold Co.
Inc., New York.
1310 s. |