Page 132 - Partition & Adsorption of Organic Contaminants in Environmental Systems
P. 132

SORPTION FROM WATER SOLUTION     123

            tion applies only to polar solutes and is considered to be most significant at
            low C e/S w, due to “site” availability. At high C e/S w, with the specific sites nearly
            saturated, the polar solutes then exhibit a linear partition into the entire SOM.
            Although the presumed polar solute–SOM specific interaction as a potential
            source of sorption nonlinearity seems sensible, it is debatable that it could be
            portrayed as a partition (solubility) process, since it operates only over a short
            range of solute concentrations. Much more work is needed to substantiate the
            assumed specific interaction between solute and SOM and related active SOM
            sites and active solute groups.
              By considering the dual mechanistic functions of the soil, the unsuppressed
            adsorption of polar solutes on certain minerals could also lead to significant
            nonlinear sorption by soils at low C e/S w (Chiou, 1995). On some special soil
            minerals (e.g., certain montmorillonite clays as discussed in Chapter 6), water
            may not sufficiently suppress the adsorption of polar organic solutes as it does
            the low-polarity solutes. In contrast, the residual mineral adsorption of low-
            polarity solutes should be relatively weak and linear over a large concentra-
            tion range, as noted for phenanthrene (Huang et al., 1996). The consequence
            of this unsuppressed adsorption with soil minerals or of the specific interac-
            tion with SOM to the overall solute sorption to a mineral soil having a sig-
            nificant SOM content is illustrated schematically in Figure 7.1b. Since the
            presumed unsuppressed mineral adsorption or the solute–SOM specific inter-
            action for polar solutes is significant largely at low C e/S w, the effect may over-
            whelm the linear partition with SOM at low  C e/S w, while the partition
            contribution usually prevails at moderate to high  C e/S w. As a result, the
            isotherm would be nonlinear at low C e/S w but virtually linear at moderate to
            high C e/S w. The solute concentration at which the linear partition and the non-
            linear contribution cross is expected to be a function of the SOM content, the
            magnitude of K om or K oc, and the mineral type and content, which determine
            the relative magnitudes of partition and adsorption.
              Because soils and sediments from different geographic locations differ con-
            siderably in their compositions, there is no simple a priori way to predict the
            magnitude of sorption nonlinearity and the specific cause for its occurrence.
            The possibilities of all mechanisms contributing to the concentration depend-
            ence of the polar-solute sorption coefficient have to be settled by experiments
            together with relevant soil and solute physical and chemical properties. The
            potential nonlinear sorption of polar solutes to soils and sediments at low con-
            centrations is important because the concentrations of many polar solutes in
            natural water (usually at low mg/L to low mg/L) fall into a low C e /S w range,
            owing to their high water solubilities. However, one should keep in mind that
            the magnitude of nonlinear sorption that one observes in single-solute systems
            is usually attenuated in multisolute systems because of the solute competition,
            as shown later. Thus the data derived from single-solute studies may not prop-
            erly reflect the actual solute behavior in natural systems. The nonlinear effect
            for low-polarity solutes should be far less serious in consideration of their
            wider isotherm linearity and their generally lower water solubilities (which
   127   128   129   130   131   132   133   134   135   136   137