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 />
Daphnia magna<br />
Average chain length 24 hour 48 hour<br />
C4 (SØ Butyrate) 4 ~12,000 ~6,000<br />
C5 (SØ Valerate) 5 ~12,000 ~5,000<br />
C11 (SØU) 11 355 ± 150* 208 ± 85*<br />
*Subsequent repurification of this sample yielded a product with the same isomeric composition but<br />
with LC50 values over 1000 mg/L for daphnids (Swisher et al., 1976).<br />
Analytical monitoring: Yes [X] No [ ] ? [ ] MBAS<br />
Method: EPA-660/3-75-009 1975. Method for acute toxicity tests with fish,<br />
macroinvertebrates and amphibians.<br />
Acute toxicity tests were conducted on high molecular weight <strong>LAS</strong>,<br />
individual pure homologues, non-linear <strong>LAS</strong> components (dialkyl tetralin or<br />
indane sulfonates (DTIS), and model biodegradation intermediates<br />
(sulfophenyl undecane, SØU) in order to determine whether biodegradation<br />
decreases toxicity. In 250 mL beakers with 200 mL of well water of<br />
approximately 250 mg/L hardness, ten Daphnia, less than 18 hours old, were<br />
placed in each of the three beakers. No food was added for the duration of<br />
the test.<br />
GLP: Yes [X] No [ ] ? [ ]<br />
Test substance: 1) High molecular weight <strong>LAS</strong>: Average chain length = 13.3; C11 1%, C12<br />
8%, C13 52%, C14 39%<br />
2) Individual <strong>LAS</strong> homologues of C10, C11, C12, C13, and C14<br />
3) Nonlinear <strong>LAS</strong> components (DTIS)<br />
4) Model biodegradation intermediates<br />
Remarks: The length of the alkyl chain is the most important factor influencing acute<br />
toxicity, which increases as the alkyl chain increases. These longer alkyl<br />
chain homologues are the first constituents of the <strong>LAS</strong> mixture to degrade.<br />
The nonlinear components (DTIS) showed 1/2 to 1/10 the toxicity of <strong>LAS</strong><br />
with the same carbon chain length. Toxicity of biodegradation<br />
intermediates is significantly less than the parent <strong>LAS</strong>. Daphnia acute<br />
toxicity tests on partially degraded <strong>LAS</strong> demonstrated that toxicity is<br />
significantly lessened as <strong>LAS</strong> biodegraded. Because of the shorter than<br />
normal study duration and smaller than standard number of Daphnia per<br />
concentration, the reliability of the absolute values cannot be assessed.<br />
However, the study is considered reliable for the trends in the data because<br />
the homologues were tested under identical conditions.<br />
Reference: Kimerle, R.A. and Swisher, R.D. 1977. Reduction of aquatic toxicity of<br />
linear alkylbenzene sulfonate (<strong>LAS</strong>) by biodegradation. Water Research<br />
11:31-37.<br />
Reliability: 2 Valid with restrictions<br />
B. Other aquatic invertebrates<br />
(a)<br />
Species: Gammarus pulex (amphipod)<br />
Mysidopis bahia (mysid)<br />
Panaeus duorarum (pink shrimp)<br />
Results: EC50 (G. pulex) = 6.2 mg/L (25 records)<br />
EC50 (M. bahia) = 1.7 mg/L (6 records)<br />
EC50 (P. duorarum) = 49 mg/L (5 records)<br />
Test Substance: C10-14 <strong>LAS</strong> (all <strong>LAS</strong> in range, including data for individual homologues)<br />
Remarks: Geometric mean EC50 values for number of records listed for each species.<br />
The interspecies variation decreases considerably when the geometric mean<br />
value per species is calculated.<br />
<strong>UNEP</strong> PUBLICATIONS 185