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 />
Reference: Lewis, M.A., Pittinger, C.A., Davidson, D.H., and Ritchie, C.J. 1993. In situ<br />
response of natural epiphyton to an anionic surfactant and an environmental<br />
safety assessment for phytotoxic effects. Environ. Toxicol. Chem. 12:1803-<br />
1812.<br />
Reliability: 2 Valid with restrictions<br />
(k)<br />
Type: Laboratory bottles/lake exposures<br />
Methods: Species or ecosystem studied: Bottles (300 ml) filled with lake water were<br />
used as the test systems. Nine concentrations were tested in triplicate.<br />
Once a month the bottles were suspended in a lake at 1 m depth for three<br />
hours. The experiment was repeated for six months.<br />
Effects monitored: photosynthetic response of phytoplankton was<br />
determined.<br />
Chemical analysis: Concentrations were measured.<br />
Results: Mean EC50 values were 3.4 and 1.9 mg/L for C12 and C13, respectively. The<br />
ranges of EC50 values for the different tests were 0.5-8.0 and 0.2-8.1 mg/L<br />
for C12 and C13, respectively.<br />
Substance: Dodecyl <strong>LAS</strong>; average chain length C11.8 (CAS #25155-30-3); and Tridecyl<br />
<strong>LAS</strong>, average chain length C13.3 (CAS #26248-24-8).<br />
Remarks: A concentration-effect relationship was found. Suspended solids were not<br />
measured. The wide range of EC50 values is in part due to seasonal<br />
differences in temperature and community dynamics.<br />
Reference: 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. Water. Res. 20:1575-1582.<br />
Reliability: 2 Valid with restrictions<br />
4.8 BIOTRANSFORMATION AND KINETICS<br />
(a)<br />
Type: Animal [ ]; Aquatic [X]; Plant [ ]; Terrestrial [ ]; Other [ ]<br />
Methods: In a flow-through system a 21 day uptake and 14 day elimination experiment<br />
was conducted with Lepomis macrochirus. The LSC-measured exposure<br />
concentration was 0.5 mg/L (1.45 uM). Flow-through; water renewal rate:<br />
20 renewals per day; hardness as CaCO3 35 mg/L; pH 7.1; water/fish ratio:<br />
0.04 L/g.<br />
Results: k1/k2 concentration factors were for muscle 36, liver 171, blood 237, carcass<br />
64, gall bladder 5224, gill and viscera 282 (on wet weight basis).<br />
k2 values are almost the same (0.24-0.28 d-L) in all tissues but the liver. The<br />
value for the liver is double (0.48 d-L) of the other tissues. This indicates<br />
biotransformation in the liver. The value of kl in the gall bladder (1461<br />
L/kg/d) is at least 16 times higher than those in the other tissues (9-82<br />
L/kg/d).<br />
t95 in the different tissues range between 150 and 300.<br />
No information on metabolism was given.<br />
Test Substance: Na-alkylbenzenesulfonate average chain length: C11.7 (C11 45%, C12 36.5%,<br />
C13 18.5%) radiolabeled material ( 14 C uniformly labelled benzene ring) is<br />
spiked with unlabelled <strong>LAS</strong> (identical homologue composition), spiking ratio<br />
4:1 (unlabeled: 14 C labeled).<br />
Remarks: Whole body concentration factors are reliable. Steady state attained within<br />
24 h.<br />
Reference: Kimerle, R.A., Macek, K.J., Sleight, B.H., and Burrows, M.E. 1981.<br />
Bioconcentration of linear alkylbenzene sulfonates (<strong>LAS</strong>) in bluegill<br />
(Lepomis macrochirus). Water. Res. 15:251-256.<br />
<strong>UNEP</strong> PUBLICATIONS 246