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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 />

containers (as described for springtails). Ten female and five male H.<br />

aculeifer (16-19 days old) were added to each test container together with<br />

100 F. fimetaria (16-19 days old) serving as prey for the mites. Incubation<br />

and extraction of mite offspring followed the same procedure as described for<br />

springtails.<br />

A natural sandy, agricultural soil was used for all tests, rather than synthetic<br />

test soil. Nominal concentrations of <strong>LAS</strong> for some tests were verified by<br />

chemical analysis using HPLC.<br />

GLP: Yes [ ] No [ ] ? [X]<br />

Test substance: C10-13 <strong>LAS</strong> was obtained as an aqueous sodium salt solution with an active<br />

matter concentration of 16.1% (w/w), average molecular weight = 342 g/mol,<br />

distribution of the linear alkyl chains: C10 14%, C11 34%, C12 31%, and C13<br />

21%; average alkyl chain length = C11.6<br />

Remarks: Toxic effects on reproduction and growth were revealed when the<br />

concentration in soil exceeded 40 to 60 mg/kg dry weight. Reproduction was<br />

approximately fourfold more sensitive in earthworms and enchytraeids than<br />

in springtails and mites. It is argued that this difference in sensitivity is<br />

related to the dependency of soil pore water, which is high in the annelids but<br />

comparatively low in the arthropods. It should be noted that these studies<br />

report worst case exposures due to the use of a sandy test soil and the fact<br />

that <strong>LAS</strong> was added as an aqueous solution to the soil. In addition, too few<br />

replicates were used for the ECx approach (e.g., 1000 mg/kg<br />

NOEC = 250 mg/kg soil dw<br />

Method: OECD Guideline 207, 1984. Ten adult worms (mean wt. 0.66 g/animal)<br />

were placed into each of four glass jars per concentration with soil comprised<br />

of 70% 5010 grade silica sand, 20% kaolinite clay, and 10% finely ground<br />

sphagnum peat. Nominal test concentrations in the soil were 1000, 500, 250,<br />

125, 63 and 0 mg/kg dry weight. Temperature was maintained at 20 + /-2 o C<br />

with 24-hour continuous lighting at 600 lux. Earthworms were assessed for<br />

mortality, general health, body weight, and behavior after 7 and 14 days.<br />

GLP: Yes [ ] No [ ] ? [X]<br />

Test substance: <strong>LAS</strong> (commercial blend) with average alkyl chain length C11.6 (typical of<br />

<strong>LAS</strong> chain lengths found in the environment).<br />

Remarks: No significant mortality was observed at the highest nominal concentration of<br />

1000 mg/kg. A 33% and 23% reduction in body weight was observed at 100<br />

and 500 mg/kg vs. a 14% reduction for the controls. Based on statistical<br />

analysis of the weight data, the no effect concentration was the nominal 250<br />

mg/kg dose, which was confirmed by HPLC to be 235 mg/kg.<br />

Reference: Mieure, J.P., Waters, J., Holt, M. and Matthijs, E. 1990. Terrestrial safety<br />

assessment of <strong>LAS</strong>. Chemosphere 21:251-262.<br />

Reliability: 2 Valid with restrictions<br />

<strong>UNEP</strong> PUBLICATIONS 226

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