Page 674 - The Toxicology of Fishes
P. 674

654                                                        The Toxicology of Fishes



                                             Atmospheric
                                             Deposition:  Volatilization:  Absorption:
                                                                       0.828
                                               0.680      3.998
                           Direct Discharge:
                               100





                                                                                Advective Outflow: 74.163

                                                Mass in Water: 20.32 kg
                          Advective Inflow: 54.751
                                                Concentration in Water: 1354 µg/m 3
                                                                            Water Reaction: 72.558



                                                            Deposition: 8.089
                           W–S Diffusion: 4.469
                                                Resuspension: 0.834             S–W Diffusion: 6.186




                                                   Burial: 0.845
                                                             Active Sediment    Sediment Reaction: 4.693
                                                           Mass in Sediment: 42.52 kg
                                                           Concentration in Sediment: 3932 ng/g

                                      Total mass of pyrene: 62.84 kg

                       FIGURE 14.3 Process rates of the chemical fate of pyrene in the hypothetical lake environment (expressed as kg/year).

                       on both the properties of the chemical and those of the environment in which it is distributed. Chemical
                       properties can vary over a range of 10 , so the fate of a very volatile chemical such as chloroform is
                                                    12
                       entirely different from that of the involatile benzo(a)pyrene. Only with the aid of a model can these
                       differences be assessed, evaluated, and predicted in advance.



                       Bioaccumulation
                       Chapters 2 and 3 gave comprehensive reviews of bioavailability and bioaccumulation, so no attempt is
                       made here to repeat this material; however, it is useful to demonstrate how the abiotic fate data presented
                       above can be used to calculate concentrations in fish. This can be accomplished by one of several models
                       in which the box receiving inputs and generating outputs is a fish (Figure 14.4). In more sophisticated
                       pharmacokinetic models, the fish can be treated as a series of connected boxes, each box corresponding
                       to an organ or a group of tissues. To extend the illustration, we apply the FISH mass balance model
                       (www.trentu.ca/cemc) to both chemicals, using the water column concentrations previously determined.
                       The fish considered is a 10 g trout as specified in Table 14.5. The output data and fluxes are given in
                       Table 14.6 and Table 14.7.
                        For anthracene, the whole body wet weight concentration is 1.14 g/m  or µg/g. Uptake is 21.8% from
                                                                             3
                       food and 78.2% from respired water for a total input rate of 1.04 µg/day. The bioconcentration factor
                       expressed as the ratio of concentration in fish to that dissolved in water is 1713. The losses are 0.176
   669   670   671   672   673   674   675   676   677   678   679