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a Department of Environmental Engineering & Science and Department of Geological Sciences, School of the Environment, Clemson University, Clemson, SC 29634-0919
b Institute of Environmental Toxicology, Clemson University, Pendleton, SC 29670
* Corresponding author (mschlau{at}clemson.edu).
Received for publication July 25, 2003.
Mineral surfaces can alter the ability of humic substances (HS) to bind hydrophobic organic contaminants. In this study, complete adsorption (i.e., to avoid HS adsorptive fractionation effects) of a small subset of well-characterized terrestrial and aquatic HS on kaolinite and hematite significantly changed their subsequent organic carbonnormalized partition coefficients
for pyrene relative to their original respective dissolved organic carbonnormalized partition coefficients
. Parallel experiments with ultrafiltration (UF) fractions obtained from purified Aldrich humic acid (PAHA) (Aldrich Chemical, Milwaukee, WI) gave similar results. The heterogeneity among the PAHA UF fractions was examined via their mineral surface adsorption characteristics and their subsequent ability to bind pyrene. As expected, variations in maximum adsorption densities (qmax), Langmuir adsorption constants (Kq), and pyrene Kadsoc values were observed among the PAHA UF fractions. However, general trends of qmax, Kq, and pyrene log Kadsoc values for the PAHA UF fractions versus the logarithm of their weight-average molecular weights (MWw) did not typically match the corresponding trends obtained with the four aquatic and terrestrial HS. In general, an ideal mixture competitive adsorption model gave reasonable predictions for PAHA sorption to kaolinite and hematite based on their corresponding UF isotherm parameters. Ideal mixture predictions of pyrene partitioning to adsorbed PAHA from the corresponding UF fraction results were better for kaolinite versus hematite, indicating that the underlying mineral surface can alter the effects of HS heterogeneity on hydrophobic organic contaminant sorption.
Abbreviations: DOC, dissolved organic carbon HOC, hydrophobic organic contaminant HS, humic substances MWw, weight-average molecular weight PAHA, purified Aldrich humic acid SHA, soil humic acid SRFA, Suwannee River fulvic acid SRHA, Suwannee River humic acid SUVA, specific ultraviolet absorbance UF, ultrafiltration
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