EFFECTS INDUCED BY FEEDING ORCANOCHLORINE-CONTAMINATED CARP FROM SAGINAW BAY, LAKE-HURON, TO LAYING WHITE LEGHORN HENS .2. EMBRYOTOXIC AND TERATOGENIC EFFECTS
Cl. Summer et al., EFFECTS INDUCED BY FEEDING ORCANOCHLORINE-CONTAMINATED CARP FROM SAGINAW BAY, LAKE-HURON, TO LAYING WHITE LEGHORN HENS .2. EMBRYOTOXIC AND TERATOGENIC EFFECTS, Journal of toxicology and environmental health, 49(4), 1996, pp. 409-438
Carp from Saginaw Bay, Lake Huron, MI, was fed to While Leghorn chicke
ns for a period of 8 wk. The diets contained 0.3 (control; 0% carp), 0
.8 (3.4% carp), and 6.6 (35% carp) mg polychlorinated biphenyls (PCBs)
/kg diet by wet weight (ww). These concentrations corresponded to 3.3,
26, and 59 pg 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) equivalents/
g diet ww, respectively. Though the diets were not acutely toxic to th
e adult laying hens, dose- and time-dependent responses were observed
in the embryos and chicks. Toxicity was manifested as a dose-dependent
increase in embryo mortality and decreased hatching races. Furthermor
e, embryos and chicks displayed Various deformities, including iii hea
d and neck edema and hemorrhage, (2) abdominal edema and hemorrhage, (
3) foot and leg deformities, (4) skull and brain deformities, (5) yolk
-sac deformities, and (6) miscellaneous deformities. The types of defo
rmities observed were similar to those reported for embryos and chicks
of colonial waterbirds in Saginaw Bay, as well as in controlled studi
es where technical mixtures or individual congeners of polychlorinated
diaromatic hydrocarbons (PCDAHs) were fed to chickens. increasing con
centrations of carp also significantly affected the various organ weig
hts in 18-d embryos and hatched chicks. At 18 d of incubation, weights
of the embryos' fivers were directly proportional to the concentratio
n of PCBs in the diets. The weights oi the spleens and bursae were inv
ersely proportional to the dietary PCB concentration. After 3 addition
al days of incubation, significant effects in body, brain, fiver, hear
t, and bursa weights were observed in hatched chicks. The concentratio
ns of total PCBs, as well as 2,3,7,8-TCDD equivalents (TEQs) in the di
ets, were in the range of those that have been shown to cause similar
adverse effects in other species. This study has shown that fish, the
primary food source of colonial waterbirds in Saginaw Bay, are capable
of causing adverse reproductive effects in a model avian species, the
chicken. However, due to differences in the relative potency to cause
effects on different endpoints in different species, the results of t
his study should not be used to predict the threshold for effects in o
ther species.