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696                                                        The Toxicology of Fishes


                                                         Heme
                                                                  NADPH + O 2

                                              Heme oxygenase
                                                 (HSP30)
                                                                        3+
                                                                  CO + Fe + NADP +
                                                        Biliverdin
                                                                  NADPH

                                            Biliverdin reductase

                                                                  NADP +

                                                        Bilirubin
                       FIGURE 16.5 Degradation pathway of heme.


                       metabolism through a mechanism involving interaction of CYP1A with the halogenated aromatic com-
                       pound potentially initiating  oxidative stress (Hahn and Chandran, 1996). Based on the relationships
                       between HSP30 (oxygenase), CYP1A (protein), bilirubin, and biliverdin (endogenous Ah agonists) (see
                       Figure 16.5), assessment of porphyrin profiles may provide significant mechanistic insight when they
                       are measured with these other proteins and metabolites. It is obvious that the use of these metabolites
                       as biomarkers has been largely overlooked in fish and deserves further characterization.

                       Retinoids
                       Vitamin A-derived compounds, also known as retinoids, are an additional group of endogenous metab-
                       olites that have shown promise as biomarkers of effect and potential exposure to planar halogenated
                       aromatic compounds when used in combination with other markers (Alsop et al., 2005; Arcand Hoy et.
                       al. 1999; Peakall, 1992; Spear et al., 1992). In brook trout (Salvelinus fontinalis), a single injection of
                       5 µg/g of a coplaner PCB (3,3′,4,4′-TCBP) reduced retinoids in several tissues (Ndayibagira et al., 1995).
                       In the same study, lake sturgeon (Acipenser fulvescens) collected from a contaminated waterway near
                       Montreal, Canada, had significantly lower retinoid levels in the intestine. In addition, field studies with
                       white sucker demonstrated a direct relationship between maternal retinoid loss, CYP1A activity in the
                       liver, and prevalence of embryonic malformations in animals collected from the same contaminated
                       location, with significant gender-related differences in hepatic retinoid expression (Branchaud et al.,
                       1995). Following a chronic exposure of 3 years to PAH-contaminated sediment in a mesocosm, retinol
                       concentrations in plasma and liver were significantly reduced in Atlantic flounder (Besselink et al., 1998).
                       In fact, a negative, nonlinear correlation was found between retinol concentrations and CYP1A expres-
                       sion, indicating that retinoids may be a significant indicator of exposure and effect of planar aromatic
                       compounds or other Ah receptor ligands (Alsop et al., 2005). Due to the meager research efforts directed
                       toward retinoid metabolism and disposition in fish, the relationships between altered hepatic retinoid
                       levels and fish health are uncertain; however, given the prominent role of retinoids in cellular metabolism
                       and development, relationships appear likely and deserve further study.


                       Genotoxic Endpoints
                       Alterations to an organisms’ genetic material (DNA) represent an impact of the highest  order.  The
                       consequences of DNA alterations potentially affect all levels of biological organization, from the molec-
                       ular to community level. Of central importance to an organism are its survival and reproductive success.
                       Neither is attainable without maintaining the integrity of its genetic material, DNA. At the molecular
                       level, the corruption of the information coded in DNA may not pass beyond the boundary of an affected
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