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 />
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