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 />
cycle. The NOEC normalized by van de Plassche et al. (1999) to C11.6 <strong>LAS</strong><br />
was 2.3 mg/L.<br />
GLP: Yes [ ]; No [X]; ? [ ]<br />
Test Substance: Marlon A 350 <strong>LAS</strong> (CAS #68411-30-3; Benzenesulfonic acid, C10-13- alkyl<br />
derives., sodium salts, 25.7% activity)<br />
Reference: Henkel KGaA, Biological Research and Product Safety/Ecology:<br />
unpublished results (Test substance number Fi 5959).<br />
Reliability: 2 Valid with restrictions. Duration of test considered too short for a chronic<br />
study, therefore not included in SIAR Table 12A.<br />
(b)<br />
Type of test: static [ ]; semi-static [ ]; flow-through [X]; other [ ]<br />
open-system [X]; closed-system [ ]<br />
Species: Pimephales promelas (Fish, fresh water)<br />
Exposure period: 30 day<br />
Effect criteria: Fry survival<br />
Results: NOEC = 1 mg/L<br />
LOEC = 2 mg/L<br />
Analytical monitoring: Yes [X] No [ ] ? [ ] HPLC<br />
Methods: Two replicates of 100 egg-fry stage fathead minnows were exposed for 30<br />
days to <strong>LAS</strong> under the following conditions: Hardness 41 mg/L as CaCO3;<br />
pH 7.2; temperature 24 o C. The exchange rate was 1 to 3 volume<br />
changes/day. Test chambers were 3500 mL volume. The studies were<br />
conducted at EG&G Bionomics (now Springborn Smithers Laboratory).<br />
GLP: Yes [ ] No [ ] ? [X]<br />
Test substance: Commercial C10-13 <strong>LAS</strong>, sodium salt (CAS #68411-30-3); C10 5%, C11 27%,<br />
C12 53%, C13 13%; 2-phenyl 23%.<br />
Remarks: Carboxylated intermediates formed in the biodegradation of <strong>LAS</strong> exhibit<br />
toxicity several orders of magnitude less than <strong>LAS</strong>; LC50 values were >144<br />
mg/L and >52 mg/L for sulfophenyl butarate and sulfophenyl undecanoate,<br />
respectively. NOEC based on fry survival. Egg hatchability and fry growth<br />
were less sensitive. This is a key study for chronic aquatic toxicity to fish<br />
(see SIAR Table 12).<br />
Reference: Swisher, R.D., Gledhill, W.E., Kimerle R.A. and Taulli, T.A. 1978.<br />
Carboxylated intermediates in the biodegradation of linear alkylbenzene<br />
sulfonates (<strong>LAS</strong>). VII International Congress on Surface Active Substance,<br />
Proceedings, Moscow, 1976 4:218-230.<br />
Reliability: 2 Valid with restrictions<br />
(c)<br />
Type of Test: Static [ ]; semi-static [X]; flow-through [ ]<br />
Open-system [X]; closed-system [ ]; not stated [ ]<br />
Species: Poecilia reticulata (Fish, Guppy, fresh water)<br />
Exposure Period: 28 days<br />
Effect Criteria: Mortality, behavior, and growth<br />
Results: NOEC = 3.2 mg/L<br />
LOEC = 10 mg/L<br />
Analytic Monitoring: Yes [ ]; No [X]; ? [ ]<br />
Method: Fish were 3-4 weeks old at test initiation. Fifty fish were used per group.<br />
Temperature was maintained at 23 ± 2°C. The test volume (10-L per<br />
chamber) was renewed three times per week. Circadian lighting (16:8<br />
light:dark) was used. Fish were fed a Tetramin/Tetraphyll mixture.<br />
Dissolved oxygen, water hardness and pH were measured during the study.<br />
GLP: Yes [ ]; No [ ]; ? [X]<br />
Test Substance: <strong>LAS</strong>, 42.4% activity (C8