LINEAR ALKYLBENZENE SULFONATE (LAS) - UNEP Chemicals
LINEAR ALKYLBENZENE SULFONATE (LAS) - UNEP Chemicals
LINEAR ALKYLBENZENE SULFONATE (LAS) - UNEP Chemicals
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OECD SIDS <strong>LINEAR</strong> <strong>ALKYLBENZENE</strong> <strong>SULFONATE</strong> (<strong>LAS</strong>)<br />
GLP: Yes [ ] No [X] ? [ ]<br />
Test Substance: C10 to C13 homologues of <strong>LAS</strong> with varying phenyl positions<br />
Remarks: The results show that longer chain homologues are removed faster than the<br />
shorter chain homologues, indicating that primary biodegradation increases<br />
as the chain length increases. In addition, the greater the distance between<br />
the sulfonic group and the more distant terminal methyl group on the alkyl<br />
chain the faster the degradation (i.e., phenyl position 2 degrades faster than<br />
phenyl position 5 for the same homologue). For example, percent removal<br />
was 52, 68, 88 and 92% for the C10 <strong>LAS</strong> with phenyl positions 5, 4, 3, and 2,<br />
respectively.<br />
Reference: 1) Bock, K.J. and Wickbold, R. 1966. Auswirkungen der Umstellung auf<br />
leicht abbaubare Waschrohstoffe in einer großtechnischen Kläranlage und im<br />
Vorfluter. Vom Wasser 33:242-253.<br />
2) Wickbold, R. 1964. Zwischenprodukte beim Abbau eines geradkettigen<br />
Alkylbenzolsulfonates. Vortrage IV, Inern. Kongr. F. grenzflachenaktive<br />
Stoffe, Brussel. (not available for review)<br />
Reliability: 2 Valid with restrictions<br />
(b)<br />
Type: aerobic [X]; anaerobic [ ]<br />
Inoculum: adapted [X]; non-adapted [X]; activated sludge [X]<br />
Concentration of the chemical: 10 mg/L related to COD [ ]; DOC [X] test substance<br />
Medium: water [ ]; water-sediment [X]; soil [ ]; sewage treatment [ ]<br />
Degradation: 69.6% after 28 days (acclimated inoculum)<br />
66.7% after 28 days (non-acclimated inoculum)<br />
Results: readily biodeg. [ ]; inherently biodeg. [ ]; under test condition no<br />
biodegradation observed [ ], other [X]<br />
Kinetics:<br />
% Biodegradation % Biodegradation<br />
Days<br />
(Acclimated) (non-Acclimated)<br />
5 14.3 9.2<br />
8 32.4 24.5<br />
12 49.5 43.6<br />
19 63.9 60.8<br />
28 69.6 66.7<br />
Method: OECD 301 B, modified Sturm test, also reported as method C 5 in the Italian<br />
D.M. 109. The reference standard sodium benzoate was used at the same<br />
concentration of the tested surfactants (about 10 mg/L). The testing period<br />
was 28 days and during this time the testing solutions were kept in dark glass<br />
vessels. A supernatant solution from a sludge, which was aerated and left to<br />
settle, was used as an inoculum for each biodegradation test at an amount<br />
equal to 1% of the solution. Both the STP sludges and the laboratory<br />
assimilated sludges were analysed for the dry matter contents. Tests were<br />
conducted using acclimated or non-acclimated inocula to determine whether<br />
this affected ultimate biodegradation. Acclimation was achieved by running<br />
the laboratory activated sludge plant for seven days before testing with a<br />
synthetic influent containing <strong>LAS</strong> at a concentration of abourt 10 mg/L.<br />
Tests were conducted on <strong>LAS</strong> and three other surfactants.<br />
GLP: Yes [X] No [ ] ? [ ]<br />
Test substance: C10-13 <strong>LAS</strong>; average alkyl chain length = C11.6<br />
Remarks: <strong>LAS</strong> was biodegradable using both acclimated and non-acclimated inocula.<br />
Acclimated inocula did not significantly improve the total biodegradation,<br />
but did accelerate the attainment of the degradation plateau. The 10-day<br />
time-window criterion was missed slightly, so this study does not meet the<br />
<strong>UNEP</strong> PUBLICATIONS 156