Page 235 - The Toxicology of Fishes
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Biotransformation in Fishes                                                 215


                                                     S
                                               CH O
                                            CH 3  2
                                                     P   O           NO 2
                                            CH CH O
                                              3
                                                 2
                                                      Parathion


                                                         S
                                                        P  O                                   O
                                                                                         CH O
                                                                                       CH 3  2
                                   Desulfuration                   Dearylation                  P  OH
                                                                                       CH CH O
                                                                                            2
                                                                                         3
                                 O
                       CH CH O                                                          Diethyl phosphate
                            2
                         3
                                 P  O           NO 2         HO           NO 2               OR
                          CH O
                       CH 3  2                                                                  S
                                                                                            2
                                                                                       CH 3 CH O
                                                                                                P  OH
                                 Paraoxon                      p–Nitrophenol
                                                                                       CH CH O
                                                                                            2
                                                                                         3
                                                                                            Diethyl
                                                                                       phosphorothionate
                       FIGURE 4.26 Metabolic pathway of parathion in channel catfish. (From Straus, D.L. et al., Aquat. Toxicol., 50, 141, 2000.
                       With permission.)
                       is exclusively responsible for this reaction (Perkins et al., 1999); however, no single CYP isoform appears
                       to predominate in the sulfoxidation of aldicarb. Rather, it is likely that several isoforms participate in
                       the reaction (Perkins et al., 1999). The reduced S-oxygenation of aldicarb in channel catfish relative to
                       rainbow trout may explain its resistance against aldicarb toxicity compared to rainbow trout, which
                       readily convert aldicarb to aldicarb sulfoxide (Perkins and Schlenk, 2000).
                        In summary, fish are capable of activating organophosphate esters to more potent  cholinesterase
                       inhibitors. Species differences in the bioactivation and esterase-mediated cleavage of organophosphates
                       have been shown to greatly contribute to species differences in toxicity to these compounds. These data
                       argue for more studies to better characterize specific enzymes responsible for these transformations to
                       help identify sensitive populations of species that may be severely impacted by these compounds.



                       Conclusions
                       Biotransformation can be a very important process in the disposition and mechanistic determinations of
                       the mode of action of xenobiotics. Alterations in enzyme expression can dramatically affect the sensitivity
                       of an organism to the toxic insult of a xenobiotic or the disposition of endogenous substrates. Alteration
                       may occur as a result of genetics, diet, gender, environmental influences, or other xenobiotics. Under-
                       standing the latter is critical in risk evaluations of chemical mixtures. Very little is known regarding the
                       substrate specificities or the regulation of biotransformation enzymes in fish.  Through advances in
                       genomic technologies and the use of fish models in human health research (e.g., zebrafish, medaka),
                       numerous genotypic discoveries have recently occurred. It is likely that phenotypic functionality studies
                       with heterologously expressed enzymes resulting from genomic examinations will help in better under-
                       standing biotransformation pathways in fish. In addition, more studies are needed with whole-animal
                       systems to better characterize  in vivo  pathways of chemical biotransformation in species other than
                       classic fish models. Such studies are imperative for physiologically based toxicokinetic (PBTK) models,
                       which may help better estimate dose and aid regulators in reducing uncertainty between species, thus
                       leading to more accurate evaluations of chemical risk.
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