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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 />

eliminated via the urine, with sulfophenyl butanoic and sulfophenyl pentatonic acid as metabolites.<br />

Approximately 35% of the absorbed dose was excreted in the bile. Although the metabolites in the<br />

bile were not identified, it was shown that no unchanged <strong>LAS</strong> was eliminated via this pathway. In<br />

oral studies with pigs, Havermann and Menke (1959) found that at 200 hours after oral<br />

administration, the radiolabeled <strong>LAS</strong> was relatively high in bristles and bones, while low in liver,<br />

kidney and spleen. After 10 weeks only traces of radioactivity were still in the body. At 40 hours<br />

after administration, 40% of the dose was excreted into the urine and 60% of the dose via the feces.<br />

In another study (Sunakawa et al. 1979), rats were dosed orally with 14C-<strong>LAS</strong> and radioactivity<br />

was detected 0.25 hours after administraton, reaching a maximum at 2 hours. The biological halflife<br />

was calculated to be 10.9 hours. The distribution was high in the digestive tract and in the<br />

bladder at 4 hours after administration, with high concentrations also found in the liver, kidney,<br />

testis, spleen and lung. At 168 hours after administration, the rates of excreted radioactivity were<br />

47% in the urine and 50% in the feces.<br />

Toxicokinetics has also been studied in adult rhesus monkeys (Cresswell et al. 1978). Two male<br />

and two female monkeys were given single or repeated oral (30, 150 or 300 mg/kg) or subcutaneous<br />

(0.1, 0.5 or 1 mg/kg) doses of 14C-<strong>LAS</strong>. For example, after single 30 mg/kg oral doses, the<br />

radioactivity was rapidly excreted, mostly during the first 24 hours. Means of 71.2% and 23.1% of<br />

the dose were excreted in the urine and feces, respectively, during 5 days. During seven<br />

consecutive daily (30 mg/kg/day) or subcutaneous (1 mg/kg/day) doses, there was no accumulation<br />

of radioactivity in plasma. Mean peak concentrations and biological half-lives were similar after<br />

the first and seventh doses. No unchanged <strong>LAS</strong> was detected in the urine after oral or subcutaneous<br />

doses. Five metabolites were excreted but they were not identified.<br />

Studies in Humans<br />

Studies were conducted with isolated human skin preparations using two solutions of C12 <strong>LAS</strong><br />

(Howes 1975). The results demonstrated that penetration through the skin and subsequent<br />

absorption does not occur to any significant extent (less than 1%) at 24 to 48 hours.<br />

3.1.2 Acute Toxicity<br />

Acute mammalian toxicity data are available for all three potential routes of exposure (inhalation,<br />

dermal, oral), as summarized below and in Table 5.<br />

Studies in Animals<br />

Oral<br />

Eight acute oral toxicity studies are available for <strong>LAS</strong> using rats, and one acute oral study is<br />

available using mice (Murmann 1984a,b,c; Ito et al. 1978; Kynoch 1986a; Monsanto 1971,<br />

1972a,b). All of the studies were conducted on the low average chain length <strong>LAS</strong> (C11.2-C11.7).<br />

The resultant LD50 values ranged from 1,080 up to 1,980 mg/kg bw for rats and greater than 2000<br />

mg/kg bw for mice, with no significant difference between sexes. Mortality and symptoms of<br />

toxicity occurred at the high doses tested in each study, and usually within the first few hours or<br />

days, after which surviving animals generally recovered. Symptoms noted in most of the studies<br />

included piloerection, hunched posture, abnormal gait (waddling), lethargy, reduced appetite,<br />

decreased respiratory rate, ptosis, pallor of the extremities, and diarrhea. All oral studies are<br />

reliability 1 or 2, except for those by Ito et al. (1978), which were rated unassignable (4) since the<br />

original reports were not available for review. However, these studies were considered reliable<br />

because they have been reviewed by the International Program on Chemical Safety.<br />

<strong>UNEP</strong> PUBLICATIONS 22

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