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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 />

defined in which CP is found by pairing off carbon atoms along the two<br />

branches up to the terminus of the shorter branch. Regression analysis<br />

correlating log (1/LC50) to goldfish with a combination of ALP [representing<br />

log P calculated without a branch factor] and log (CP + 1) [representing the<br />

water sharing function]:<br />

Log (1/LC50) = 0.78ALP – 1.13 log (CP + 1) + 2.06 (EQ 2)<br />

(for LC50 tests on guppies; n = 20, r = 0.997, s = 0.041)<br />

Further, dividing the first two terms on the right of EQ 2 by 0.78 gave,<br />

assuming the role of the second term to be solely that of the branching factor,<br />

the following equation:<br />

Log P = ALP – 1.44 log (CP + 1) (EQ 3)<br />

Thus, the PDBF was defined as -1.44 log (CP + 1). Further details on this<br />

method are described in Roberts (1989).<br />

Log P values calculated using EQ 3 were found to give good correlations<br />

with published river sediment sorption partition coefficients for <strong>LAS</strong><br />

compounds, supporting the applicability and validity of the PDBF. Log P<br />

values calculated using EQ 3 were also used successfully in regression of<br />

toxicity data for pure <strong>LAS</strong> homologues and isomers to Daphnia magna and<br />

Gammarus pulex. The basic equation is similar to EQ 1 and has the general<br />

form:<br />

Log (1/LC50) = alog P + b (EQ 4)<br />

with the values for a, b and regression data shown in the following table:<br />

Daphnia Daphnia Gammarus Gammarus<br />

(H) (S) (H) (S)<br />

Value of a 0.7 0.64 0.76 0.71<br />

Value of b<br />

Regression<br />

data<br />

2.23 2.44 2.46 2.27<br />

n 9 12 9 11<br />

r 0.987 0.955 0.966 0.950<br />

s 0.07 0.15 0.13 0.16<br />

F 263 103 98 83<br />

Notes: H = hard water (250 mg/L CaCO3); S = soft water (25 mg/L CaCO3). Strongly<br />

negative outliers omitted.<br />

The log P coefficients and intercepts for goldfish, Daphnia, and Gammarus<br />

are all intermediate between those of Könemann’s QSAR equation (EQ 1),<br />

suggesting that a narcosis (possibly polar) mechanism applies to <strong>LAS</strong> acute<br />

toxicity.<br />

Results: Agreement between observed and calculated toxicities for <strong>LAS</strong> is good. The<br />

fact that QSARs derived from compounds whose log P values are calculated<br />

with the PDBF give good predictions for unbranched compounds supports<br />

the validity of the PDBF for the type of branching encountered in <strong>LAS</strong>.<br />

Remarks: The analyses presented in this paper indicates that the problems of<br />

calculating log P for surfactants can be overcome. The case for the<br />

applicability of the PDBF appears compelling, although it is based on<br />

indirect evidence. In terms of acute aquatic toxicity, anionic surfactants like<br />

<strong>LAS</strong> do not seem greatly different from unreactive non-surfactant organic<br />

chemicals. Anionic surfactants of various types have log (1/LC50) values<br />

<strong>UNEP</strong> PUBLICATIONS 125

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