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 />
sorption period. The sand was then mixed with sludge (0.3 g dry weight) and<br />
finally soil was mixed in with the sludge and sand. A sludge:soil ratio of<br />
1:100 (dry weight basis) was used to avoid depletion of oxygen.<br />
Folsomia candida<br />
The springtail reproduction test was initiated with 10- to 12-day old juveniles<br />
and lasted 4 weeks. The resulting nominal <strong>LAS</strong> concentrations were 125,<br />
250, 500, 1000, 2500, and 4000 mg/kg sludge-soil mixture. Ten juvenile F.<br />
candida were added to each of the 4 replicate vials per concentration<br />
containing 30 g (wet weight) of the sludge-soil mixture. The numbers of<br />
surviving adults and offspring were counted after 4 weeks.<br />
Enchytraeus albidus<br />
The enchytraeid worm reproduction test was initiated by introducing 10<br />
worms with visible clitellum to each of 4 replicate vials per concentration.<br />
Nominal <strong>LAS</strong> concentrations were 750, 1500, 2250, and 3000 mg/kg sludgesoil<br />
mixture (dry weight). Test duration was six weeks. After 3 weeks, the<br />
adult worms were removed and counted. At 6 weeks, the number of<br />
offspring hatched from cocoons were counted.<br />
Microbiological tests<br />
The toxicity of <strong>LAS</strong> to microbiological processes was evaluated using one<br />
aerobic system (simultaneous determination of aerobic respiration and<br />
nitrification) and two anaerobic systems (denitrification and<br />
methanogenesis). Nominal <strong>LAS</strong> concentrations were 0, 125, 250, 500, 1000,<br />
and 2500 mg/kg mixture (dry weight) for both the aerobic and methanogenic<br />
systems, and 0, 250, 500, 1500, 300, and 5000 mg/kg (dry weight) in the<br />
dentrifying system.<br />
GLP: Yes [ ] No [ ] ? [X]<br />
Test Substance: The test substance for soil invertebrates consisted of an aqueous sodium salt<br />
solution containing 14% (w/w) of 14 C-labeled C10-13 <strong>LAS</strong> (EniChem Augusta<br />
Industriale; purity 95%). The average alkyl chain length of C10-13 <strong>LAS</strong> was<br />
11.6 and the distribution was C10 14%, C11 34%, C12 32% and C13 20%. A<br />
pure C12 <strong>LAS</strong>, 4-(2-dodecyl)benzene sulfonate sodium salt, was used in the<br />
microbiological tests.<br />
Remarks: Reproduction of E. albidus was the most sensitive endpoint (EC10 = 447<br />
mg/kg dry weight). Danish laws stipulate a maximum cut-off value of 1300<br />
mg/kg for <strong>LAS</strong> in sludge for agricultural use.<br />
Reference: Gejlsbjerg, B., Klinge, C., Samsoe-Petersen, L., and Madsen, T. 2001.<br />
Toxicity of linear alkylbenzene sulfonates and nonylphenol in sludgeamended<br />
soil. Environmental Toxicology and Chemistry 20:2709-2716.<br />
Reliability: 2 Valid with restrictions. Well documented publication, comparable to ISO.<br />
4.6.2 TOXICITY TO TERRESTRIAL PLANTS<br />
(a)<br />
Species/Endpoints: See table<br />
Results: The following table shows the available NOEC, EC10 and EC50 values for<br />
twelve terrestrial plant species (in mg/kg dry weight).<br />
Species Endpoint EC10 EC50<br />
Brassica rapa Growth 134<br />
Brassica rapa Growth 90 200<br />
Malvia pusila Growth 204<br />
Solanum nigrum Growth 169<br />
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