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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 />

<strong>UNEP</strong> PUBLICATIONS 133

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