Page 1002 - The Toxicology of Fishes
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982                                                        The Toxicology of Fishes




                        Estradiol-17β (pg/mL)  A  11-Ketotestosterone (pg/mL)  B  Vitellogenin (µg/mL)  C








                            Female  Intersex  Male     Female  Intersex  Male    Female  Intersex  Male

                       FIGURE 25.9 Endocrine status of roach (Rutilus rutilus) sampled from wild populations in the United Kingdom. Fish
                       from effluent contaminated waters were collected from the River Nene (Northamptonshire) and Aire (Yorkshire). Roach
                       from sites uncontaminated with treated sewage effluent were sampled from the Royal Canal, Ireland, Grantham Canal,
                       Leicestershire, and a spring-fed Lake at Wartnarby, Leicestershire. Fish were collected in October. (A) Plasma estradiol-17β,
                       (B) 11-ketotestosterone, and (C) vitellogenin in male, female, and intersex fish. Asterisks represent significant differences
                       of intersex male or exposed females from pooled control males or females, respectively (∗∗∗p < 0.001). (Adapted from
                       Jobling, S. et al., Biol. Reprod., 66, 272–281, 2002.)

                       from any point of sewage input, it is likely that the fish collected were truly representative of populations
                       in typical English river ecosystems. The ecological implications of intersexuality will depend on whether
                       the reproductive competence of the fish that are intersex is compromised. Our studies have shown that wild
                       intersex roach (Rutlius rutilus) and male roach living in effluent contaminated rivers in England have altered
                       sex steroid hormone profiles (Figure 25.9), altered spawning times, and reduced sperm production (Jobling
                       et al., 2002a). When all data for male, intersex, and female fish were pooled across all the sampling sites,
                       the plasma concentrations of estradiol-17β and vitellogenin in the intersex fish were intermediate between
                       the concentrations found in male and female fish. Female fish had considerably lower 11-ketotestosterone
                       concentrations than in either male or intersex fish and there were no significant differences in the concen-
                       tration of 11-ketotestosterone between the male and intersex fish (Jobling et al., 2002a).
                        Examining the reproductive potential of intersex fish, we have also established that the ability of
                       intersex roach to produce gametes is highly variable and is dependent on the degree of disruption in the
                       reproductive ducts or altered germ cell development. Small numbers of wild roach have been found that
                       cannot produce any gametes at all due to the presence of severely disrupted gonadal ducts. In the majority
                       of intersex fish found, male gametes are produced that, although viable, are of poorer quality than those
                       from males obtained from aquatic environments that do not receive treated sewage effluent (Jobling et
                       al., 2002b). Fertilization and hatchability studies have shown that intersex roach, even with a low level
                       of gonadal disruption (mildly intersex), are compromised in their reproductive capacity and produce
                       fewer offspring than fish from uncontaminated sites under laboratory conditions (Jobling et al., 2002b).
                       In that study, there was an inverse correlation between reproductive performance (defined by the ability
                       to produce viable offspring) and severity of gonadal intersex (Figure 25.10). This, in turn suggests that
                       the intersex condition is likely to have population level consequences. This question is of fundamental
                       importance for the sustainability of wild populations of fish.



                       Identification of Estrogenic Substances in STW Effluent and
                       Evidence That They Cause Feminization of Fish in English Rivers

                       Sewage treatment works that receive domestic, industrial, and agricultural waste release a complex (and
                       ill-defined) mixture of natural and synthetic chemicals into the aquatic environment following their
                       partial or complete biodegradation during the treatment process. The scale of the problem of isolating
                       causal compounds responsible for biological effects in aquatic wildlife can be gauged from reported
                       estimates that over 60,000 manmade chemicals are in routine use worldwide (a total of over 100,000
                       manmade chemicals are discharged into the environment), and anywhere between 200 and 1000 new
                       synthetic chemicals enter the market each year (Shane, 1994); thus, identifying specific chemicals
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