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 />
Results: The average Log Koc values over the four DHS materials (Aldrich-HA,<br />
Carlisle-WSOC, Carlisle-HA, and SRHA) for each <strong>LAS</strong> chain length tested<br />
are:<br />
Log Koc (C10 <strong>LAS</strong>): 4.02 L/kg<br />
Log Koc (C12 <strong>LAS</strong>): 4.83 L/kg<br />
Log Koc (C14 <strong>LAS</strong>): 5.49 L/kg<br />
The data for Ca-saturated Aldrich-HA was linear over the entire<br />
concentration range of DHS, whereas some curvatura was present in the data<br />
from the Ca-saturated SRHA, and considerable deviation from linearity was<br />
apparent in many of the Na-saturated DHS solutions.<br />
Test Substance: C10 <strong>LAS</strong> (98% purity), C12 <strong>LAS</strong> (93% purity), and C14 <strong>LAS</strong> (88% purity),<br />
each synthesized at Procter and Gamble. Uniformly 14 C-ring labeled C10-,<br />
C12- and C14-<strong>LAS</strong> were obtained from New England Nuclear and were 93.8,<br />
96.3 and 92.5% pure, with specific activities of 26.6, 68.2, and 34.3 µCi/mg,<br />
respectively.<br />
Remarks: Good agreement was obtained with both of the analytical methods, indicating<br />
that both techniques can be used to quantify the effects of DHS on speciation<br />
of <strong>LAS</strong> in natural waters with certain limitations. <strong>LAS</strong>-DHS partition<br />
coefficients increased with increasing length of the alkyl chain in the <strong>LAS</strong>.<br />
These data indicate the significance of nonpolar forces in <strong>LAS</strong>-organic<br />
matter interactions. Good agreement was found between the partition<br />
coefficients obtained from the two analytical techniques and those calculated<br />
from the response of uptake and depuration studies conducted with fathead<br />
minnows.<br />
Reference: Traina, S.J., McAvoy, D.C. and Versteeg, D.J. 1996. Association of <strong>LAS</strong><br />
with dissolved humic substances and its effect on bioavailability. Env. Sci.<br />
Technol. 30:1300-1309.<br />
Reliability: 2 Valid with restrictions<br />
(d)<br />
Type: Adsorption [X]; Desorption [ ]; Volatility [ ]; Other [ ]<br />
Media: water - activated sludge<br />
Method: estimation of Kd with Freundlich equation<br />
Results: The Kd of commercial <strong>LAS</strong> was between 660 and 5200 L/kg (6 citations),<br />
dependant on organic carbon content and other characteristics of the solid<br />
phase.<br />
Remarks: Concentration in liquid phase between 1 and 80 mg/L.<br />
Reference: Painter, H.A. and Zabel, T.F. 1988. Review of the environmental safety of<br />
<strong>LAS</strong>. Wrc Medmendham, UK. Report No. CO 1659-M/1/EV 8658.<br />
Reliability: 4 Not assignable<br />
(e)<br />
Type: Adsorption [X]; Desorption [ ]; Volatility [ ]; Other [ ]<br />
Media: water - activated sludge and water - river sediment<br />
Method: Comparison of Kd for <strong>LAS</strong> C10 to C14 - Year 1982<br />
Results: Adsorption coefficients (L/kg) in activated sludge and river sediment,<br />
respectively, for <strong>LAS</strong> homologues:<br />
C10: 220 and 41<br />
C11: 1000 and 100<br />
C12: 3070 and 330<br />
C13: 9330 and 990<br />
C14: 2950 (for river sediment – not determined for activated sludge)<br />
Remarks: Kd is highly dependent on the alkyl chain length of <strong>LAS</strong> with approximately<br />
a factor of 3 increase per carbon and on the position of the phenyl group on<br />
the alkyl chain. The organic carbon content is also an important factor,<br />
varying by a factor of 10 between activated sludge and river sediment.<br />
<strong>UNEP</strong> PUBLICATIONS 150