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 />
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