Page 849 - The Toxicology of Fishes
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Reproductive Impairment of Great Lakes Lake Trout by Dioxin-Like Chemicals  829




                                    HSP90
                                         zfAHR2                                      Cytoplasm
                        TCDD        HSP90
                                        AIP
                                                                          Nucleus
                                                            HSP90
                                                                  AIP
                                                            HSP90
                                                                                 zfAHRR1
                                      TCDD
                                 HSP90
                                 HSP90  zfAHR2  HSP90  TCDD          TCDD            zfAHRR2
                                     AIP        HSP90 zfAHR2           zfAHR2 zfARNT1
                                                    AIP
                                                                      AHRE  TCDD-responsive genes
                                                         zfARNT1                  Induced
                                                                                              zfCYP1A
                                                                                  mRNAs
                                 zfAHR1
                                                                                             Unknown
                                         zfARNT2
                                                                                              proteins
                                                                                             Downstream
                                                                                            cellular effects


                                                                                             Endpoints
                                                                                              of toxicity
                       FIGURE 21.4 Aryl hydrocarbon receptor (AhR) signaling pathway in zebrafish. The AhR and ARNT isoforms marked
                       with an “X” are not in the functional pathway of AhR-related toxicity in zebrafish, as is the case with zfCYP1A.


                       Endpoints of TCDD Developmental Toxicity in Fish
                       Like other fish species, zebrafish embryos exposed to TCDD at the blastula stage develop normally
                       through gastrulation and primary organogenesis. TCDD toxicity is not manifested until later stages of
                       development when morphogenesis of primary organ systems and embryo growth occur. For zebrafish,
                       the early-life-stage period when endpoints of developmental toxicity are first manifested occurs 48 to
                       120 hours post-fertilization (hpf). If developing zebrafish are exposed to TCDD, prior to or during this
                       time, TCDD toxicity is manifested 48 to 120 hpf by cardiovascular dysfunction culminating in heart
                       malformation, peripheral ischemia and eventually heart failure, impaired osmoregulation culminating in
                       edema, impaired erythropoiesis leading to anemia, hemorrhage, reduced jaw growth and jaw malforma-
                       tion, altered brain morphology, body growth retardation, uninflated swim bladder, and, beginning around
                       144 hpf, mortality associated with blue sac syndrome (Antkiewicz et al., 2005; Belair et al., 2001; Bello
                       et al., 2004; Carney et al., 2006b; Dong et al., 2002; Henry et al., 1997; Hill et al., 2003, 2004a,b;
                       Teraoka et al., 2002).  The gross morphological manifestations of  TCDD developmental toxicity in
                       zebrafish are edema, cardiovascular toxicity, anemia, impaired chondrogenesis, and neurotoxicity.

                       Edema
                       The hallmark response to TCDD in the zebrafish embryo is the accumulation of edema fluid in the
                       pericardium beginning at 72 hpf and in the yolk sac beginning at 96 hpf (Belair et al., 2001; Dong et
                       al., 2002; Henry et al., 1997; Hill et al., 2004a). The edema may be caused by TCDD-induced disruption
                       of osmoregulatory or circulatory function. In the zebrafish embryo, osmoregulation is carried out by the
                       pronephric kidney and skin (Drummond et al., 1998; Hagedorn et al., 1998; Rombough, 2002). Also,
                       due to the close association between osmoregulatory function of the skin and kidney and circulatory
                       function of the heart and vasculature, edema may be secondary to cardiovascular dysfunction. The gills
                       are less likely to be involved because their osmoregulatory function does not occur until later, after the
                       critical period for TCDD developmental toxicity has passed. Although glomerular filtration is largely
                       unaffected by TCDD prior to edema (Hill et al., 2004a), peripheral blood flow is reduced (Carney et al.,
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