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 />
Remarks: Half-lives compare well with those for ultimate degradation in lab soil tests<br />
(with ........14-C-evolution), indicating that the degradation of <strong>LAS</strong> does not<br />
lead to the ... formation of significant levels of break-down intermediates in<br />
soil.<br />
The homologue distribution of <strong>LAS</strong> in soil suggests that removal represents<br />
biodegradation rather than leaching.<br />
Reference: 1) Holt, M.S., Matthijs, E. and Waters, J. 1989. The concentrations and fate<br />
of linear alkylbenzene sulphonate in sludge amended soils. Wat. Res.<br />
23:749-759.<br />
2) Waters, J., Holt, M.S., Matthijs, E. 1989. Fate of <strong>LAS</strong> in sludge amended<br />
soils. Tenside Surfactants Detergents 26(2):129-135.<br />
Reliability: 2 Valid with restrictions<br />
(d)<br />
Type: Laboratory<br />
Radiolabel: Yes [ ] No [X] ? [ ]<br />
Concentration: 8 to 488 mg/kg<br />
Soil Composition: Coarse sand 67%, fine sand 16%, silt 8.6%, clay 6.2% and humus 2.7%<br />
Organic Carbon: 1.5%<br />
Method: <strong>LAS</strong> mixed with sewage sludge was applied to sandy agricultural soil and<br />
incubated for up to 8 weeks. Various microbial soil parameters were<br />
measured (see Section 4.4). <strong>LAS</strong> was quantified after methanol extraction<br />
using HPLC.<br />
GLP: Yes [ ] No [ ] ? [X]<br />
Test Substance: C10-13 <strong>LAS</strong> obtained as an aqueous sodium salt solution with a <strong>LAS</strong> content<br />
of 16.1% (w/w), NA-<strong>LAS</strong> average molecular weight = 342 g/mol,<br />
distribution: C10 14%, C11 34%, C12 31%, and C13 21%.<br />
Results: For nominal concentrations of 8 to 62 mg/kg, the depletion of <strong>LAS</strong> after 2<br />
weeks was more than 73%. At 488 mg/kg, only 15% depletion occurred. It<br />
is possible that this high <strong>LAS</strong> level may have inhibited microbial activity or<br />
caused a prolonged log phase to occur.<br />
Reference: Elsgaard, L. Petersen, S.O. and Debosz, K. 2001b. Effects and risk<br />
assessment of linear alkylbenzene sulfonates in agricultural soil. 2. Effects<br />
on soil microbiology as influenced by sewage sludge and incubation time.<br />
Environmental Toxicology and Chemistry. 20:1664-1672.<br />
Reliability: 2 Valid with restrictions<br />
(e)<br />
Type : Field trial [X]; Laboratory [X]; Other [ ]<br />
Radiolabel: Yes [ ] No [X] ? [ ]<br />
Soil Content: Clay 1.8 - 4%, Silt 7.6 - 18.5 %, Sand 77.1 - 95.5%<br />
Organic Carbon: Ranged from 0.9 - 1.79%<br />
Soil pH: 5.2 – 6.8<br />
Dissipation time: DT50: 3 days (lysimeters)<br />
DT50: 7 days (field trials)<br />
Method: Sewage sludge containing <strong>LAS</strong> was added to four cultivated sandy soils with<br />
low amounts of organic matter in field trials and lysimeter studies. The field<br />
trial lasted one year. For the lysimeter studies, undisturbed soil columns<br />
were taken from the corresponding field sites.<br />
GLP: Yes [ ] No [ ] ? [X]<br />
Test substance: Marlon A350 (CAS #68411-30-3) C10-13 <strong>LAS</strong>, average alkyl chain length =<br />
11.6; activity: 50%<br />
Remarks: <strong>LAS</strong> are mobile in all four soils tested. They were detected down to a depth<br />
of 30-40 cm after being applied at the surface. After one week, a<br />
concentration of 500 mg/kg was measured in the 0-5 cm layer, which<br />
corresponds to 23% of the the total <strong>LAS</strong>. In the 5-10 cm layer, the<br />
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