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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 />

Reference: Mackay, D., Di Guardo, A., Paterson, S., Kicsi, G., Cowan, C. and Kane, D.<br />

1996. Assessment of chemical fate in the environment using evaluative,<br />

regional and local scale models: Illustrative application to chlorobenzene and<br />

linear alkylbenzene sulfonates. Environ. Toxicol. Chem. 15:1638-1648.<br />

Reliability: 2 Valid with restrictions<br />

(b)<br />

Media: Air-biota [ ]; Air-biota-sediment-soil-water [X]; Soil-biota [ ];<br />

Water-air [ ]; Water-biota [ ]; Water-soil [ ]<br />

Method: Fugacity level I [ ]; Fugacity level II [ ]; Fugacity level III [X]; Fugacity<br />

level IV [ ]; Other (calculation) [ ]; Other (measurement)[ ] Multi-media<br />

model HAZCHEM derived from MacKay type level III model, including a<br />

water purification module (comparable to SIMPLETREAT model used by<br />

the Netherlands Authorities). Regional model for Europe. Includes<br />

probabilistic evaluation of natural variability and inaccuracy in determination<br />

of input parameters using Monte Carlo simulation. Input parameters held<br />

constant in the simulations for the <strong>LAS</strong> used in the model were based on the<br />

best available data at the time of modeling and are:<br />

Molecular weight 347<br />

Melting point (°C) 10<br />

Vapor pressure (Pa) 1 x 10 -10<br />

Solubility (mg/L) 350<br />

Log Kow 2.5<br />

Half-life life in air (h) 8<br />

Half-life in water (h) 35<br />

Half-life in soil (h) 339<br />

Half-life in sediment (h) 17<br />

Soil-water partitition coefficient (L/kg) 1000<br />

Sediment-water partitition coefficient (L/kg) 1000<br />

Suspended solids-water partitition coefficient (L/kg) 1000<br />

Parameters that were varied using lognormal distributions for the Monte<br />

Carlo simulations included water surface and arable land fractions, depths of<br />

various compartments, fraction organic carbon in various compartments,<br />

advective residence times, temperature, and others.<br />

Results: Predicted concentrations in the various compartments as defined by the model<br />

as shown in the table below. Degradation in the soil was not taken into<br />

account and the model was not calibrated. Measured concentrations in arable<br />

soil were generally below 1 ppm. Results are the 5 th and 95 th percentile values<br />

from the Monte Carlo analysis and the normal average.<br />

Average 5 percentile 95 percentile<br />

air (ug/m 3 ) 3.23 E-12 -- --<br />

biota (ppm) 5.99 E-2 7.11 E-3 1.95 E-1<br />

sediment (ppm) 4.90 E-3 3.23 E-3 1.38 E-2<br />

arable soil (ppm) 44.2 7.02 1.11 E+2<br />

suspended. matter (ppm) 3.79 0.449 12.3<br />

dissolved in water (mg/L) 3.79 E-3 4.49 E-4 1.23 E-2<br />

suspended in water (mg/L) 7.81 E-5 1.54 E-5 2.16 E-4<br />

Remarks: Input data were the best estimates from ECETOC Task Force members,<br />

including detergent industries. Note the predicted average value for arable<br />

soil was reported in ECETOC 1993 as 4.42E-4, which is not possible given<br />

<strong>UNEP</strong> PUBLICATIONS 154

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