N-(1,3-Dimethylbutyl)-N
N-(1,3-Dimethylbutyl)-N
N-(1,3-Dimethylbutyl)-N
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OECD SIDS<br />
N-(1,3-DIMETHYLBUTYL)-N´-PHENYL-1,4-PHENYLENEDIAMINE<br />
3. ENVIRONMENTAL FATE AND PATHWAYS ID: 793-24-8<br />
DATE: 11.05.2005<br />
Degradation : 97 (±) % after 22 hour(s)<br />
Result :<br />
Kinetic of testsubst. : 1 hour(s) 40 %<br />
2 hour(s) 57 %<br />
3 hour(s) 67 %<br />
5 hour(s) 74 %<br />
22 hour(s) 97 %<br />
Deg. product :<br />
Method : other: River die-away in Mississippi River water<br />
Year : 1981<br />
GLP : Yes<br />
Test substance : other TS: Santoflex 13<br />
Method : Aqueous Die-Away Screening Method<br />
The die-away screening method involved exposure of the test chemical to<br />
three types of aqueous environments:<br />
- purified (Milli-Q) water<br />
- membrane filtered Mississippi River water and<br />
- glass-wool filtered Mississippi River water.<br />
The die-away (= decrease in concentration) of the test chemical was<br />
monitored as a function of time by an appropriate analytical method (see<br />
TC).<br />
The Mississippi River water was collected on 1981-04-27 at the St. Louis<br />
waterfront (Eads Bridge). A portion of the water was sterilized by<br />
membrane filtration through 0.2 µm filters (Gelman Metricel GA-8, 47 mm).<br />
A second portion was filtered through glass wool to remove large inert<br />
particulates, but retaining the active biomass. Purified water for the test<br />
was obtained from a Milli-Q Water Purification System.<br />
500 mL of each water were added to 32-ounce Boston round bottles. 20 µL<br />
of a 0.6263 g/25 mL stock solution in dimethyl sulfoxide was injected with a<br />
25 µL syringe into each bottle resulting in a nominal S-13 concentration of<br />
1002 µg/L. After mixing, a 10 mL aliquot of each water was removed for<br />
zero time analyses. The bottles were then sealed with TFE-fluorocarbon<br />
lined caps and stored in the dark at ambient temperature (24 °C). At<br />
appropriate sampling points, a 10 mL aliquot of each water was removed<br />
from each bottle for analysis.<br />
Remark : Degrees of transformation not determined; adsorption onto<br />
suspended matter may have affected the observed results<br />
Result : Rate of disappearance of 6PPD in biologically active and sterile Mississippi<br />
River water and in deionized water are listed respectively as follows (%<br />
remainder of about 1 mg/l initial concentration):<br />
Hour Water<br />
active sterile deionized<br />
0 hour 100 % 100 % 100 %<br />
1 hour 60 % 85 % 100 %<br />
2 hour 43 % 70 % 88 %<br />
3 hour 33 % 56 % 86 %<br />
4 hour 38 % 49 % 80 %<br />
5 hour 26 % 41 % 65 %<br />
22 hour 3 % 4 % 12 %<br />
The estimated half-lives due to primary transformation are<br />
2.9 h in biologically active river water, 3.9 h in sterile<br />
river water, and 6.8 h in sterile deionized water.<br />
Test condition : Analytical Method: Santoflex 13 analyses involved extraction of 10 mL<br />
aqueous samples with 2 mL ethyl acetate followed by measurement of the<br />
S-13 in the extract by gas chromatography using a nitrogen/phosphorus<br />
selective detector. The method was validated in Mississippi River water in<br />
the concentration range 100 to 1000 µg/L (ppb)<br />
Reliability : (2) valid with restrictions<br />
Study in accordance with generally accepted scientific<br />
standards and described in sufficient detail<br />
UNEP PUBLICATIONS 71