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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 />

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unpublished results (Test substance number Fi 5959).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

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