Page 860 - The Toxicology of Fishes
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840                                                        The Toxicology of Fishes


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                                         Extract Dose–Response in Lake Trout
                                         LD50 = 108 pg TEQ per g egg
                                     80


                                   Fry Mortality (%)  60




                                     40



                                     20



                                      0.1          1           10          100         1000
                                                      Dose (pg TEQ per g egg ww)

                       FIGURE 21.5 Embryo/fry mortality caused by graded doses of an extract of lake trout collected in Lake Michigan in
                       1988 injected into freshly fertilized, hatchery-derived lake trout eggs. Doses of the extract (TEQs) were based on the
                       measured concentrations of HAHs and an additive model of toxicity. (Data are from Tillitt, D.E. and Wright, P.J., Organo-
                       halogen Comp., 34, 221–225, 1997.)


                       rainbow trout-specific REPs)—were 1.8- and 1.3-fold greater, respectively,  than those for TCDD (200
                       pg TCDD per g rainbow trout egg and 74 pg TCDD per g lake trout egg). Although these results suggest
                       a less than additive interaction for the TCDD-like PCB, PCDD, and PCDF congeners in the mixture,
                       the TEQ LD  and TCDD LD  values for each species were only 30 to 80% different (Walker et al.,
                                50
                                              50
                       1996). Considering all of the potential variation in the model variables, this is a small amount of difference
                       among the predicted and actual toxicity; consequently, additivity appears to be the appropriate model
                       for HAHs in early life stages of salmonines. Furthermore, when the lake-trout-specific REP for PCB
                       126, 0.003 (Zabel 1995c), is used instead of the slightly more potent rainbow trout-specific REP for
                       PCB 126, 0.005, to calculate the TEQ concentration of the mixture, then the TEQ LD  and TCDD LD 50
                                                                                        50
                       values for early-life-stage mortality in lake trout are no longer significantly different (Cook et al., 1997).



                       Symptoms of TCDD-Induced Early-Life-Stage Toxicity in Salmonines
                       Time Course

                       Lake trout embryos exposed to TCDD as fertilized eggs show stage-specific periods of sensitivity at
                       hatch and later during the sac fry stage (Spitsbergen et al., 1991). The stage when toxicity occurs is
                       determined by the egg TCDD concentration. At TCDD concentrations in eggs that are at or exceed the
                       LD , toxicity is generally manifested at the time of hatching and is characterized by a high incidence
                         100
                       of mortality. The affected lake trout embryos are typically incompletely hatched and have significant
                       yolk sac edema. On the other hand, at lake trout egg concentrations of TCDD below the LD  embryos
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                       hatch successfully and signs of toxicity are delayed until later during the sac fry stage. Mortality generally
                       occurs from middle to end of the sac fry stage. Once the yolk sac has been absorbed and the lake trout
                       fry begin feeding, TCDD begins to be more rapidly eliminated. Mortality during the fry stage is typically
                       very low. Thus, the critical period for early-life-stage mortality in lake trout is from about one week
                       prior to hatching until the end of the sac fry stage. There is typically no mortality in TCDD-exposed
                       lake trout eggs before about one week prior to hatch. This does not include induction of CYP1A, which
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