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 />
length) were added to each aquarium. Fish were screened from access to the<br />
macroinvertebrates by a 60 mesh stainless steel screen and were fed a daily<br />
supplement of frozen brine shrimp. Test duration was 28 days. Effects<br />
monitored included population and community effects. Nominal<br />
concentrations were confirmed with MBAS analysis. After 28 days the<br />
vegetative shoots of Elodea were removed, the total length measured, and the<br />
shoots were placed into aluminium dishes for determination of ash-free dry<br />
weights.<br />
GLP: Yes [ ] No [ ] ? [X]<br />
Test substance: <strong>LAS</strong>; C 14 -<strong>LAS</strong> chain length C12 (91% purity) plus unlabeled <strong>LAS</strong> with<br />
average chain length C11.6 (C10 9.7%, C11 27.9%, C12 54.4%, C13 8.0%; 95%<br />
purity) (tested together)<br />
Remarks: Dissolved oxygen concentrations ranged between 7.0 and 9.0 mg/L.<br />
Temperature was maintained at 2°C and the mean pH was 8.1 ± 0.2. The<br />
growth and productivity of Elodea was not significantly inhibited at the<br />
highest concentration tested (4 mg/L) in Phase I. Growth throughout the 28day<br />
exposure approximately doubled the initial biomass of the vegetative<br />
shoots from a mean of about 37 mg ash-free dry weight to a mean of about<br />
72 mg for the treatment concentrations. Similarly, Phase II experiments<br />
resulted in an approximate doubling of the initial Elodea biomass in the<br />
controls and the 3.75% effluent concentration, though the heavy growth of<br />
attached bacteria and fungi (periphyton) that developed in the higher<br />
concentrations effectively covered the growing surface of the Elodea shoots<br />
resulting in progressively lower productivity in 7.5, 15 and 30% dilutions.<br />
Reference: Maki, A.W. 1981. A Laboratory model ecosystem approach to<br />
environmental fate and effects studies. Unpublished Internal Report,<br />
Environmental Safety Department Procter and Gamble Company,<br />
Cincinnati, Ohio.<br />
Reliability: 2 Valid with restrictions<br />
(p) (Lemna)<br />
Species: Lemna minor (aquatic plant)<br />
Endpoint: Biomass [ ]; Growth rate [ ]; Other [X] frond count<br />
Exposure period: 7 days<br />
Results: EC50 = 2.7 mg/L<br />
NOEC = 0.9 mg/L (calculated as EC50/3); normalized to C11.6 = 1.1 mg/L<br />
Analytical monitoring: Yes [X] No [ ] ? [ ]<br />
Method: A 7-day flow-through growth inhibition test was developed using duckweed<br />
(Lemna minor). Control water (carbon and reverse osmosis filtered well<br />
water) and five concentrations of test material were delivered from diluter<br />
mixing chambers to Pyrex glass exposure chambers at a rate of 1.5 L every<br />
16 minutes (approximately 14 replacement volumes per day). At time 0,<br />
each chamber received seven 2-frond, root excised duckweed colonies (four<br />
replicates per treatment level). Plants were given continuous illumination at<br />
3875 lux (360 foot candles) and temperature was maintained between 21 and<br />
23 o C. Total hardness was 120-130 mg/L CaCO3 and pH was 7.2-7.6. The<br />
number of fronds was recorded once every 24 hours for 7 days. <strong>LAS</strong><br />
concentrations were measured using the MBAS method.<br />
GLP: Yes [ ] No [ ] ? [X]<br />
Test substance: C10-14 <strong>LAS</strong>, average alkyl chain length 11.8, MW = 345, 27.3% active<br />
Remarks: Results based on frond count were found to provide the most useful<br />
information per unit of laboratory time. Other endpoints resulted in 7-day<br />
EC50 values of 3.6 mg/L (dry weight), 4.9 mg/L (root length), and 4.8 mg/L<br />
(growth rate/doubling time). Concurrent tests with bluegill sunfish (96-hr<br />
LC50 = 1.7 mg/L) and D. magna (48-hr LC50 = 4.4 mg/L) indicate that<br />
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