Page 321 - The Toxicology of Fishes
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Reactive Oxygen Species and Oxidative Stress                                301




                       Studies with Fishes
                       A large number of studies of oxidative stress in fish have been carried out in the last 25 years or so,
                       with different motivations (Di Giulio et al., 1989). These motivations might be summarized as: (1)
                       increasing the understanding of basic biochemical and molecular mechanisms related to oxidative stress
                       in fish, (2) developing biomarkers related to oxidative stress fish, and (3) investigating the relationships
                       between oxidative stress and the health of wild populations of fish. Some of the results of the studies
                       carried out are presented below with respect to these three concerns.


                       Basic Biochemical and Molecular Mechanisms of Oxidative Stress in Fish
                       The study of the toxicity of prooxidant xenobiotics in fish serves both to inform risk assessment with
                       regard to fish populations and to inform our understanding of the toxicity of such chemicals in other
                       organisms, including humans (Bailey et al., 1996; Di Giulio et al., 1989; Kelly et al., 1998; Winston,
                       1991). Mechanistic studies in fish can be further categorized as characterizing the ability of a xenobiotic
                       to generate ROS in fish cells or living fish, as well as characterizing the antioxidant defenses present in
                       different species of fish, either with or without prior xenobiotic exposure. It is often useful to employ
                       comparative studies involving different species (piscine and nonpiscine) to better understand the impact
                       of prooxidant chemicals in the environment.


                       In Vitro Biochemical Generation of ROS
                       In vitro studies have clearly demonstrated that ROS are generated in subcellular fractions (microsomal,
                       mitochondrial, and cytosolic) of fish tissues. Generation of ROS in fish, as in mammals, is sometimes
                       involved in normal physiological processes such as immune function (Anderson, 1994); moreover, release
                       of ROS by phagocytic cells can be stimulated after pollutant exposure in fish (Fatima et al., 2000). In
                       addition, laboratory and field exposures to prooxidant chemicals have resulted in increased ROS pro-
                       duction in subcellular fractions of various tissues, particularly liver, gill, and kidney (Lemaire et al.,
                       1994; Livingstone, 2001; Livingstone et al., 2000; Peters et al., 1996; Schmieder et al., 2003; Washburn
                       and Di Giulio, 1988). As discussed previously in this chapter, xenobiotics have been shown in vitro to
                       enhance ROS production and oxidative stress by diverse mechanisms, including redox cycling, depletion
                       of glutathione or other antioxidants, facilitation of Fenton chemistry, uncoupling of  mitochondrial
                       electron transport, and uncoupling of cytochrome P4501A monooxygenation reactions.

                       Enzymatic Antioxidant Defenses in Fish
                       Studies aimed at understanding the biochemistry and, to a much lesser degree, the molecular biology
                       of fish antioxidant systems have also been carried out. Many if not all of the basic antioxidant defenses
                       (enzymatic and nonenzymatic) characterized in mammals are also present in fish. Representative studies
                       describing antioxidant enzymatic activities, reactivity of mammalian antibodies to presumably homol-
                       ogous fish antioxidant enzymes, and sequences for antioxidant genes in fish are presented in Table 6.3.
                       In addition, similar evidence supports the existence of many of the phase II enzymes that can be viewed
                       as playing an antioxidant role or that are regulated by an ARE in mammals (discussed earlier in the
                       section on the ARE and in Chapter 4). Certain GST isoforms in mammals, for example, may play an
                       antioxidant role both by conjugating electrophilic compounds in general (Chapter 4) and by metabolizing
                       4-hydroxy-2-nonenal (HNE) (Eaton and Bammler, 1999). HNE is a lipid peroxidation product that is
                       both highly toxic and involved in ROS-related signaling (Poli and Schaur, 2000); recent evidence
                       indicates that fish species also express a GST isoform capable of metabolizing HNE (Leaver and George,
                       1998; Pham et al., 2002; 2004). Similarly, there is evidence that in fish, as in mammals, some GST
                       isoforms possess a glutathione peroxidase activity (Martínez-Lara et al., 2002).
                        Unfortunately, the exact isoforms of antioxidant enzymes present in different fish species have rarely
                       been carefully identified and characterized. In most cases, enzyme activities have been measured with
                       slight adaptations of assays developed with mammalian species and may reflect the activities of multiple
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