Page 62 - Partition & Adsorption of Organic Contaminants in Environmental Systems
P. 62

Partition and Adsorption of Organic Contaminants in Environmental Systems. Cary T. Chiou
                                                     Copyright ¶ 2002 John Wiley & Sons, Inc.
                                                                    ISBN: 0-471-23325-0





            5 Contaminant Partition and

                   Bioconcentration






            5.1 INTRODUCTION

            The partition of organic compounds in a partially miscible solvent–water
            system has been an important subject in chemistry as the basis for solvent
            extraction of solutes from water. The application of partition coefficients to
            biochemical systems began about a century ago with Meyer (1899) and
            Overton (1901), who showed that the relative narcotic activities of drugs were
            well correlated with their oil–water partition coefficients. The usefulness of the
            partition coefficient as a system parameter for assessing the biochemical activ-
            ity of an organic compound or a drug has been greatly extended by the work
            of Fujita et al. (1964), Hansch and Fujita (1964), Hansch (1969), Leo and
            Hansch (1971), and Leo et al. (1971). Leo and Hansch (1971) reviewed the
            partition characteristics of organic compounds in a variety of solvent–water
            systems and for practical reasons considered the octanol–water system to
            be the most appropriate reference for assessing the relative lipophilicity
            of organic solutes with biological components. Hansch (1969) showed, for
            example, that the partition coefficients of organic solutes between protein
            and water could be correlated successfully with their octanol–water partition
            coefficients, thus providing an assessment of the binding of small organic
            molecules with biological macromolecules.
              The utility of partition coefficients to estimate the distribution of organic
            contaminants in environmental systems has meanwhile become increasingly
            evident since the 1970s. This development stemmed primarily from the obser-
            vations that the potential of an organic contaminant to concentrate from water
            into aquatic organisms (e.g., fish) may be correlated successfully with its
            octanol–water partition coefficient (Neely et al., 1974; Lu and Metcalf, 1975;
            Chiou et al., 1977; Könemann and van Leeuwen, 1980; Oliver and Nimii, 1983,
            Banerjee et al., 1984; Chiou, 1985). Similar empirical correlations with
            octanol–water partition coefficients were also found for soil/sediment–water
            distribution coefficients of selected groups of organic contaminants (Chiou et
            al., 1979; Karickhoff et al., 1979; Kenaga and Goring, 1980; Means et al., 1980;
            Briggs, 1981; Schwarzenbach and Westall, 1981). Although the contaminant
            distribution between water and natural organic substrates may often be more
            complicated than a simple partition, these results manifest that an important
            driving force for contaminant distribution in natural aquatic systems is con-
                                                                             53
   57   58   59   60   61   62   63   64   65   66   67