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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 />

LOEC = 1.0 mg/L<br />

Analytic Monitoring: Yes [ ]; No [ ]; ? [X]<br />

Method: ASTM. 1984. Standard Practice for Conducting Toxicity Tests with<br />

Microalgae, Draft #7, Philadelphia, PA. Algae were exposed to the test<br />

material for four days, after which cell counts were made. The EC50 value<br />

was calculated using the method of Larson and Schaefer. Assumed 1 x 10 4<br />

cells/mL because ASTM protocol, but not reported.<br />

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

Test Substance: C11.8 <strong>LAS</strong>; MW = 345; technical grade <strong>LAS</strong> from P&G<br />

Remarks: The first significant effect concentrations were<br />

between 0.5 and 1.0 mg/L. Mean test temperature was 23.6 (21.2-25.6 °C).<br />

Total mean water hardness was 137 mg/L as CaCO3. The pH range was 6.8<br />

to 7.2. Mean dissolved oxygen was 9.1 mg/L. Results of the laboratory<br />

studies were compared with enclosure studies conducted with natural<br />

phytoplankton assemblages. Concentrations in the enclosures that first<br />

altered community structure were found to be between 27 and 108 mg/L.<br />

The EC50 value reported represents the lowest acute value for algal species<br />

for which a report or publication was available. This is a key study for<br />

aquatic toxicity to algae (see SIAR Tables 10 and 12).<br />

Reference: 1) Lewis, M.A. 1986. Comparison of effects of surfactants on freshwater<br />

phytoplankton communities in experimental enclosures and on algal<br />

population growth in the laboratory. Environ. Toxicol. Chem. 5:319-332.<br />

2) Lewis, M.A. and Hamm, B.G. 1986. Environmental modification of the<br />

photosynthetic response of lake plankton to surfactants and significance to a<br />

laboratory-field comparison. Wat. Res. 20:1575-1582.<br />

Reliability: 2 Valid with restrictions<br />

(b)<br />

Species: Selenastrum capricornutum and Scenedesmus subspicatus<br />

Endpoint: Biomass [ ]; Growth rate [X ]; Other [ ]<br />

Results: ErC50 values ranged from 29 to 35.5 for S. capricornutum (two records)<br />

ErC50 values ranged from 82 to 163 mg/L for S. subspicatus (three records)<br />

Test Substance: C10-13 <strong>LAS</strong> (CAS #68411-30-3)<br />

Remarks: A total of 13 algae studies originally were reviewed by HERA in 2004. Eight<br />

of these studies were rejected because<br />

the test material was not commercial <strong>LAS</strong>, the study deviated<br />

significantly from standard protocols, or non-standard endpoints were<br />

measured. The remaining five studies were evaluated for reliability and<br />

the results reflect the range of acute ErC50 values obtained for the two<br />

most commonly tested algal species. These studies are tabulated and<br />

discussed further in the SIAR and SIAP in a weight-of-evidence<br />

approach. A robust summary for the study with the lowest acute ErC50<br />

value was prepared (see Lewis 1986 above).<br />

Reference: HERA-<strong>LAS</strong> team, May 2004; see SIAR Annex 2.<br />

Reliability: 4 Not assignable. This study is given a reliability score of 4 because it is<br />

a summary evaluation of a series of studies conducted by other<br />

researchers.<br />

(c)<br />

Species: Chlamydomonas reinhardi, Chlorella kessleri, Microcystis sp., Plectonema<br />

boryanum, Scendesmus subspicatus, Selenastrum sp. (algae)<br />

Results: NOEC (C. reinhardi) = 12 mg/L (1 record)<br />

NOEC (C. kessleri) = 3.5 mg/L (1 record)<br />

NOEC (Microcystis sp.) = 0.80 mg/L (4 records)<br />

NOEC (P. boryanum) = 15 mg/L (1 record)<br />

NOEC (S. subspicatus) = 7.7 mg/L (4 records)<br />

<strong>UNEP</strong> PUBLICATIONS 188

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