Page 122 - The Toxicology of Fishes
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102                                                        The Toxicology of Fishes


                       Body Weight—A modification of the static exposure model is required when experiments are conducted
                       using individual fish of different sizes. Larger fish will deplete the exposure solution faster, but the
                       amount of toxicant absorbed per gram of body weight will be less than in smaller fish because the
                       absorbed toxicant distributes into a larger body size. In this case, Equations 3.32 and 3.51 must be
                       rewritten to explicitly consider fish body weight (W):
                                                               (
                                                     dX dt = ρ W C w − C p u, )                  (3.53)
                                                        /
                                                              (
                                                           ρ
                                                   −dC dt  = W C w  − C p u,  ) V w              (3.54)
                                                      w
                       Integrating, one obtains equations analogous to those given previously:

                                                 X =  VV C w  1 −  e − ( (  WV w)+(1 V))ρ t    (3.55)
                                                       w
                                                           ,0
                                                     WV w + V            
                                                          V    (   − ( (  V))ρ t 
                                             C w =  C w   −    1 − e  WV w)+(1  )              (3.56)
                                                    ,0 1
                                                        WV w + V              
                       To fit Equation 3.55 and Equation 3.56 to experimental data, both time and fish weight are entered as
                       independent variables, along with measured values of C  and X.
                                                                  w
                       Oral Administration
                       A single oral dose may be administered to a fish that has been prepared with an indwelling vascular
                       catheter. If the absorption kinetics are first order and monoexponential, then the rate of appearance of
                       chemical in the fish is:
                                                      dX/dt = k X  – CLC p                       (3.57)
                                                             ab
                                                                g
                       where k  is the absorption rate constant, and X  is the amount of toxicant remaining in the GIT. From
                                                           g
                             ab
                       this equation it is possible to derive the following relationship:
                                                                −
                                           C p = k F dose e (  −( CL V t )  − e ) (  CL V ) )    (3.58)
                                                  ⋅
                                                                 k t
                                                                              /
                                                                    V k ab − (
                                                                 ab
                                                ab
                       where F is the fraction of the dose that reaches the systemic circulation of the fish (oral bioavailability;
                       see earlier section on hepatic clearance). The value of F may be estimated by comparison of the area
                       under the C ,t profile with the area determined after an intravascularly administered dose, where F is unity.
                               p
                        When the dietary exposure is continuous, the rate of change of the amount of chemical in the fish is:
                                                      dX/dt = FR  – CLC                          (3.59)
                                                               in     p
                       where R  is the rate of chemical ingestion. In this case, the mass of chemical exponentially approaches
                             in
                       a constant or steady-state value:
                                                    X ss = ( FR V CL) − (1  e )                  (3.60)
                                                                     −
                                                                      kt
                                                                       el
                                                           in
                       Two-Compartment Model
                       A one-compartment model assumes that a chemical distributes instantaneously throughout all tissues of
                       the exposed animal. This assumption often fails because chemical distribution to each tissue is linked
                       to blood perfusion rate, and tissue-specific perfusion rates vary considerably. When the kinetics of internal
                       distribution affect the shape of the plasma concentration–time profile, a higher order compartment model
                       is required. Perhaps the most common example of this phenomenon occurs when log-transformed plasma
                       concentration data from an intravascular dosing study decrease in a biphasic manner (Figure 3.21). The
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