Page 230 - Partition & Adsorption of Organic Contaminants in Environmental Systems
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UPTAKE BY SMALL PLANT ROOTS FROM WATER      221

            TABLE 8.1. Root Concentration Factors (RCFs) of Pesticides and Related
            Compounds from Water into Barley Roots (Hordeum vulgare cv. Georgie) over
            a Period of 24 to 48 Hours (Briggs et al., 1982) and Calculated Quasiequilibrium
            Factors (a pt)
            Compound                                       logK ow  RCF     a pt
            O-Methylcarbamoyloximes
              Aldoxycarb                                    -0.57    0.66   0.74
              Oxamyl                                        -0.47    0.91   1.02
              Acetone O-methylcarbamoyloxime                -0.13    0.95   1.06
              Aldicarb                                       1.08    0.94   0.90
              Benzaldehyde O-methylcarbamoyloxime            1.49    1.48   1.19
              4-Chlorobenzaldehyde O-methylcarbamoyloxime    2.27    2.80   0.98
              3,4-Dichlorobenzaldehyde O-methylcarbamoyloxime  2.89  5.61   0.64
              3-Phenylbenzaldehyde O-methylcarbamoyloxime    3.12    8.72   0.61
              3-(3,4-Dichlorophenoxy)benzaldehyde            4.6    81.1    0.20
               O-methylcarbamoyloxime
            Substituted ureas
              3-Methylphenylurea                            -0.12    0.73   0.82
              Phenylurea                                     0.80    1.20   1.25
              4-Fluorophenylurea                             1.04    1.10   1.06
              3-(Methylthio)phenylurea                       1.57    0.94   0.72
              4-Chlorophenylurea                             1.80    2.00   1.28
              4-Bromophenylurea                              1.98    3.17   1.63
              3,4-Dichlorophenylurea                         2.64    5.86   1.09
              4-Phenoxyphenylurea                            2.80    7.08   0.97
              4-(4-Bromophenoxy)phenylurea                   3.7    34.9    0.68
            Source: Data from Chiou et al. (2001).




                                        w [
                               C pt = a  pt C f pw +  f K +  f K ]         (8.8)
                                               ch
                                                  ch
                                                      lip
                                                         lip
            or
                           a pt = ( C pt C ) (0 875 0 115.  + .  K + 0 01 K ow )  (8.9)
                                                          .
                                      w
                                                     ch
            Calculations of the a pt values for contaminants require values for the individ-
            ual carbohydrate–water partition coefficients (K ch’s); these are not available.
            However, the K ch values are expected to be small because of the high polar-
            ity of carbohydrates. For example, the cellulose–water partition coefficients
            for benzene (logK ow = 2.13) and carbon tetrachloride (logK ow = 2.83) are 0.56
            and 1.75 (Rutherford et al., 1992), respectively; the cellulose is taken to be
            similar in composition to the carbohydrates. As an approximation, we thus
            assume K ch to be 0.1 for compounds with logK ow < 0; 0.2 for logK ow = 0.1 to
            0.9; 0.5 for logK ow = 1.0 to 1.9; 1 for logK ow = 2.0 to 2.9; 2 for logK ow = 3.0 to
            3.9; and 3 for logK ow ≥ 4.0. With the assumed barley root composition, the
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