Mg. Barron et al., COMPARATIVE REPRODUCTIVE AND DEVELOPMENTAL TOXICOLOGY OF PCBS IN BIRDS, Comparative biochemistry and physiology. Part C, Pharmacology toxicology & endocrinology, 112(1), 1995, pp. 1-14
The acute toxicity of PCBs to adult birds increases with increasing ch
lorination of the PCB mixture, and brain residues greater than 300 mg/
kg are associated with mortality, Sublethal effects in adults include
reduced parental attentiveness and abnormal reproductive behavior, PCB
s cause a suite of developmental effects, including endocrine disrupti
on, immunotoxicity and teratogenesis, rather than a specific etiology
such as egg shell thinning, possible polychlorinated dibenzofuran (PCD
F) contamination in PCB mixtures may have been responsible for some of
the reported toxic effects attributed to PCBs, such as edema, PCB con
centrations causing embryo mortality range from 3.1 mu g/kg for 3,3',4
,4',5-pentachlorobiphenyl in chicken eggs to 30 mg/kg for total PCBs i
n double crested cormorant eggs, Dietary no adverse effect concentrati
ons range from 0.5 ppm in the American kestrel to 50 ppm in the Japane
se quail, Genetic differences related to expression of the aryl hydroc
arbon (Ah) receptor, rather than toxicokinetics, may be the dominant f
actor determining reproductive toxicity of PCBs in birds, The assessme
nt of potential injury to bird populations from PCBs is confounded by
the presence of multiple contaminants in field-collected biota and env
ironmental media.