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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 Unpublished Internal Report,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 />

<strong>UNEP</strong> PUBLICATIONS 195

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