RESUMO
Freshwater turtles (Chrysemys picta) were collected from two sites on Cape Cod, MA. One site (Moody Pond), adjacent to the Massachusetts Military Reservation (MMR), was considered potentially impacted by toxic agents deriving from contaminant point sources on the MMR. The second (reference) site (Washburn Pond), to the east of the MMR, was considered not impacted by these pollutants and was chosen as a control site. Plasma estradiol 17 beta and vitellogenin were significantly lower in female turtles from Moody Pond. Ovarian follicular analysis indicated a significant decrease in the >16.00-mm follicular cohort in Moody Pond female turtles compared with Washburn Pond animals. Although testicular weight was lower at the Moody Pond site, histology, plasma testosterone, and sperm number were similar to these parameters in Washburn Pond animals. The data suggest that in Moody Pond, the reproductive capacity of turtles may be negatively affected by contaminants from the MMR.
Assuntos
Estradiol/sangue , Fertilidade/efeitos dos fármacos , Tartarugas/fisiologia , Vitelogeninas/sangue , Poluentes Químicos da Água/intoxicação , Animais , Monitoramento Ambiental , Feminino , Resíduos Industriais , Massachusetts , Folículo Ovariano/crescimento & desenvolvimentoRESUMO
The freshwater painted turtle, Chrysemys picta, was used to investigate (a) the distribution of an injected dose of 109Cd in tissues over a period of 192 h (8 days) and (b) the effect of non-isotopic cadmium injection on tissue metal-binding protein levels. Cadmium is cleared from the blood with 9% remaining in the circulation at 192 h. 109Cd is found in all tissues, but is accumulated preferentially in liver, kidney, pancreas, and gastrointestinal tract. The liver is the primary site of Cd accumulation, accounting for 46.4% of the injected dose by 192 h and the highest Cd concentration (cpm/mg tissue). Steroidogenic tissues and the oviduct accumulate significant amounts of 109Cd and the isotope is present in yolk. An increase in tissue metal-binding protein level after non-isotopic CdCl2 injection is consistent with 109Cd distribution, in that metal-binding protein concentration after CdCl2 injection is highest in liver, followed by pancreas and kidney with low, but with significant levels of cadmium-binding protein in gonads and steroid target organs. We conclude that the liver is the major site of storage after a single injection of isotopic cadmium and induction of a metal-binding protein may be an adaptive response to exposure to cadmium.