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 />
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