o-TOLUIDINE CAS N°: 95-53-4 - UNEP Chemicals
o-TOLUIDINE CAS N°: 95-53-4 - UNEP Chemicals
o-TOLUIDINE CAS N°: 95-53-4 - UNEP Chemicals
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OECD SIDS o-<strong>TOLUIDINE</strong><br />
Table 8 Geoaccumulative properties of o-toluidine (IUCLID 3.3.1)<br />
Parameter Method Result Reference<br />
Soil organic carbonwater<br />
distribution<br />
coefficient<br />
Soil organic carbonwater<br />
distribution<br />
coefficient<br />
Sediment organic<br />
carbon-water<br />
distribution coefficient<br />
2.2.8 Environmental Monitoring<br />
Occurrence<br />
Calculated with PCKOCWIN, v. 1.66 Koc = 74 Bayer<br />
AG, 2003<br />
log Koc = 0.62 log Kow + 0.85 = 1.72 Koc = 52 Application of<br />
the Koc-formula<br />
for anilines<br />
Determination of Kd between water of<br />
the river Elbe and the sediment from<br />
an aquifer located in Germany.<br />
Koc = 0.87 Boernick,<br />
Grischek and<br />
Worch, 2001<br />
Several natural occurrences of o-toluidine are reported (IARC, 2000). Toluidine (isomers not<br />
specified, but o-toluidine likely to be present) occurs in vegetables like kale (Brassica oleracea),<br />
celery (Apium graveolens), and carrots (Daucus carota). In beans (Phaseolus vulgaris), o-toluidine<br />
was detected but could not be quantitatively determined with a determination limit of 0.1 mg/kg<br />
fruit (Neurath et al., 1977). o-Toluidine occurs also in tocacco leaves (Irvine and Saxby, 1969) and<br />
in the aroma of black tea (Vitzthum, Werkhoff and Hubert, 1975).<br />
In the environment o-toluidine is also formed by reduction of o-nitrotoluene, e.g. at former<br />
munitions sites. However, o-toluidine was degraded much faster than its precursor, o-nitrotoluene<br />
(Van Aken and Agathos, 2002).<br />
Toluidine (isomers not specified, but o-toluidine likely to be present) was detected as a component<br />
of coal oil at a concentration of 135 mg/kg (Tomkins and Ho, 1982). o-Toludine is present in 77 %<br />
of in total 65 Swiss and US gasoline samples (average 6.1 mg/l) and in their aqueous extracts<br />
(average 0.47 mg/l) (Schmidt et al., 2002).<br />
Water<br />
Neurath et al. (1977) found o-toluidine in 3 of 9 samples of environmental waters in Northern<br />
Germany. The highest value occurred in the river Alster (ca. 1 µg/l).<br />
In 1979, Wegman and De Korte (1981) found several aromatic amines in surface waters of the<br />
Netherlands. In 46 water samples (containing sediments) of the river Rhine from Lobith, the mean<br />
o-toluidine concentration was 0.03 µg/l (3 samples above the determination limit of 0.02 µg/l,<br />
maximum 1.8 µg/l). In its tributaries Boven Merwede and Issel the mean o-toluidine concentration<br />
was 0.07 µg/l (1 sample of 12 above detection limit: 0.8 µg/l) and 0.2 µg/l (1 sample of 13 above<br />
detection limit: 2.4 µg/l), respectively. 3 ground water samples from the vicinity of an US underground<br />
coal gasification site, contained up to 9.2 µg/l toluidine (sum of o- and p-isomers)<br />
(Stuermer, Ng and Morris, 1982).<br />
o-Toluidine was detected in the effluents from refineries and production facilities, in river water,<br />
process water, and ground water (CHIP, 1984).<br />
o-Toluidine was monitored in several rivers in North Rhine-Westfalia in Germany (LWA<br />
NRW, 1992). In 1991, o-toluidine was only detected in the Emscher (highest value: 1.8 µg/l,<br />
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