28.01.2014 Views

N-(1,3-Dimethylbutyl)-N

N-(1,3-Dimethylbutyl)-N

N-(1,3-Dimethylbutyl)-N

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

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

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!