Page 197 - The Toxicology of Fishes
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Biotransformation in Fishes                                                 177


                       1993; Schlenk and Li-Schlenk; Schlenk et al., 1995). At least two microsomal proteins in rainbow trout
                       liver were recognized by antibodies raised against porcine FMO1 (Schlenk and Buhler, 1993). Subsequent
                       studies with antibodies raised against human FMO1 only recognized one of the two bands (Schlenk et
                       al., 2004). Although a faint band was noted in Japanese medaka liver microsomes with anti-FMO3, a
                       stronger signal from anti-FMO1 was observed (El-Alfy and Schlenk, 2002); however, catalytic activities
                       (stereochemical analyses) in trout and shark do not correspond to FMO1 or FMO3 but seem to resemble
                       FMO4-like activities, which tends to support genetic observations in Fugu (Schlenk et al., 2004).

                       Regulation, Function, and Toxicological Relevance
                       Regulation of FMO expression appears to be extremely complex, with the enzyme often being expressed
                       in a random manner (Baker et al., 1963). As mentioned earlier, FMO has been observed in all marine
                       fish species, some euryhaline, and virtually no freshwater species. Strong correlations have been observed
                       between FMO1-like proteins, enzymatic activity, and mRNA recognized by FMO1 cDNA in juvenile
                       Atlantic flounder (Platichthys flesus) and turbot (Scophthalmus maximus) (Peters et al., 1995; Schlenk
                       et al., 1996a,b), but catalytic activity did not correspond with mRNA expression in sexually mature adult
                       flounder (Schlenk, unpublished data). In fact, although FMO1-like mRNA was observed in all sexually
                       mature animals, hepatic FMO activity was lacking in more than 40% of the animals, with males having
                       more frequent expression. Although evidence suggests that various hormones may modulate the expres-
                       sion of FMO (El-Alfy and Schlenk, 2002; El-Alfy et al., 2002; Schlenk et al., 1997), no consistent
                       induction of enzyme expression has been observed following xenobiotic treatment. In medaka, estradiol
                       downregulated the hepatic FMO3-like protein but induced the gill FMO1-like form (El-Alfy and Schlenk,
                       2002). Testosterone downregulated both forms of FMO and activity in medaka. Arterial infusion of
                       cortisol induced expression of FMO1 in rainbow trout gill and liver (El-Alfy et al., 2002). However,
                       infusion of growth hormone failed to alter FMO activity or expression (Schlenk, unpublished data).
                        As mentioned above, FMO activity and protein in several tissues, particularly the gill, appear to be
                       directly correlated with serum osmolality or the salinity regime in which the fish resides (Daikoku and
                       Sakaguchi, 1990; El-Alfy and Schlenk, 2002; Schlenk, 1998; Schlenk and El-Alfy, 1998; Schlenk et al.,
                       1996a,b). Several hypotheses have been put forth to explain this relationship. Four possibilities are: (1)
                       TMA N-oxide is produced as a cellular defense to prevent the enzyme inactivation by high cellular ion
                       (Na, K) or urea that occurs in fish residing in subartic or subantarctic environments (Raymond, 1998;
                       Raymond and DeVries, 1998); (2) TMA N-oxide is produced to counterbalance high tissue and serum
                       levels of urea that are present regardless of temperature (e.g., in sharks) (Van Waarde, 1988; Yancey et
                       al., 1982); (3) TMA N-oxide may be produced in muscle of deep-sea gadiform teleosts (which also
                       produce urea) as an adaptive defense against high pressure (Gillett et al., 1997); and (4) TMA N-oxide
                       may be formed by FMOs as a secondary organic osmolyte in response to shifts in salinity regimes
                       (Schlenk, 1993). Each scenario is interrelated, with the common similarity being hyperosmolality. In
                       some euryhaline fish, FMO activity and expression are directly related to the salinity regime in which
                       the animal resides (Charest et al., 1988; Daikoku and Sakaguchi, 1990; Daikoku et al., 1988; El-Alfy
                       and Schlenk, 2002; Lange and Fugelli, 1965; Schlenk and El-Alfy, 1998; Schlenk et al., 1996a,b). FMO
                       activity and protein expression is higher in gills and kidneys than liver in several species of euryhaline
                       fish such as the Atlantic flounder (Platichthys flesus), Japanese medaka (Oryzias latipes), and rainbow
                       trout (Larsen and Schlenk, 2001; Schlenk, 1998; Schlenk and El-Alfy, 1998; Schlenk et al., 1995). In
                       addition, FMO activity in trout and medaka is downregulated following steroid treatment, which also
                                                           +
                                                              +
                       downregulates osmoregulatory function (i.e., Na /K -ATPase) (McCormick, 1995; Schlenk et al., 1997).
                       FMO activity and expression in rapid osmoconformers such as striped bass and tilapia do not respond
                                                                                               +
                                                                                            +
                       to changes in salinity (Wang et al., 2001), which is also consistent with mechanisms of Na /K -ATPase
                       regulation in these species. Testing scenarios 1 and 3, recent studies in rainbow trout have indicated that
                       urea infusion or reductions in temperature induce FMO activity and increase muscular TMA N-oxide
                       concentrations (Larsen and Schlenk, 2001). Given induction following cortisol treatment, several factors
                       may be involved in FMO regulation in rainbow trout, including stress resulting from alterations in cellular
                       redox potential due to urea or hyperosmotic conditions (El-Alfy et al., 2002; Larsen and Schlenk, 2001).
                       Clearly, more studies are necessary to better understand the regulation of this enzyme system given its
                       role in xenobiotic biotransformation and toxicology.
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