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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 />

Method: Sewage sludge was incorporated into a sandy soil to give a range of very low<br />

to very high applications (0.4 to 90 mg/ha dry weight). <strong>LAS</strong> was added as<br />

water solutions to this mixture. The soil was transferred to pots and sown<br />

with barley, rape, or carrot and allowed to grow for 19, 85, and 30 days,<br />

respectively in a greenhouse. Plant-free controls were also established.<br />

Samples were collected of the soil and analyzed for total <strong>LAS</strong> and for<br />

individual homologues.<br />

GLP: Yes [ ] No [ ] ? [X]<br />

Test substance: <strong>LAS</strong> C10-13, Approximate composition at start of study: C10 3%, C11 22%, C12<br />

40%, C13 35%<br />

Results: <strong>LAS</strong> was not taken up by plants and its degradation in soil increased by the<br />

presence of crop plants with concentration decreasing in rape from 27<br />

mg/kg (dry soil) to 0.7 - 1.4 mg/kg (dry soil) at harvesting after 30 days.<br />

During degradation, the relative fraction of homologues C10, C11, and C12<br />

decreased, while C13 increased.<br />

Reference: Mortensen, G.K., Elsgaard, H., Ambus, P., Jensen, E.S., and Gron, C. 2001.<br />

Influence of plant growth on degradation of linear alkylbenzene sulfonate in<br />

sludge-amended soil. J. Environ. Qual. 30:1266-1270.<br />

Reliability: 2 Valid with restrictions<br />

(h)<br />

Type of Measurement: Background [ ]; At contaminated site [ ]; Other [X]<br />

Medium: Sludge modified soils<br />

Method: <strong>LAS</strong> biodegradation and its kinetic parameters were studied in a land filling<br />

operation using sludges (15%) blended with soil (85%) at a site in Spain.<br />

Once the soil was blended with the sludges, grab samples were taken in three<br />

different zones of the plot. All samples were blended every day in order to<br />

have a daily composite sample. Immediately after sampling, all samples<br />

were frozen and then sieved to a 2 mm particle size. The sampling was<br />

conducted on 10 different days over a period of 62 days. <strong>LAS</strong> determination<br />

in sludge-modified soils was carried out by HPLC-UV. Degradation was<br />

determined based on <strong>LAS</strong> concentrations measured on the 10 sampling days.<br />

Results: Average <strong>LAS</strong> concentrations on the 10 sampling days were 155, 55.6, 28.0,<br />

30.2, 35.2, 28.2, 31.6, 35.1, 19.3 and 16.7 for days 0, 6, 15, 20, 27, 34, 41, 48,<br />

55 and 62, respectively. The biodegradation level reached after 62 days was<br />

89.2%. Assuming first order kinetics, the half-life is 19.3 days.<br />

Remarks: <strong>LAS</strong> adsorbed or precipitated on anaerobic sludges is biodegraded during soil<br />

amendment operations by commonly occurring micro organisms. The table<br />

shows a shift in the percent homologue distribution on days 0 and 62,<br />

demonstrating that higher molecular weight homologues exhibit stronger soil<br />

adsorption.<br />

% phenyl homologue Day 0 Day 62<br />

C10 3.7 1.2<br />

C11 29.4 18.7<br />

C12 41.4 48.9<br />

C13 25.5 31.2<br />

Reference: de Ferrer, J., Moreno, A., Vaquero, M.T. and Comellas, L. 1997.<br />

Monitoring of <strong>LAS</strong> in direct discharge situations. Tenside Surf. Det. 34:278-<br />

283.<br />

Reliability: 2 Valid with restrictions<br />

3.2 MONITORING DATA (ENVIRONMENTAL)<br />

<strong>UNEP</strong> PUBLICATIONS 135

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