Abstract:The effects of exposure to the chlorinated cyclodiene termiticide aldrin was evaluated in pest control workers potentially exposed to this material. Sister chromatid exchange (SCE) frequencies were not elevated in workers handling aldrin. This is consistent with the fact that chlorinated cyclodienes are not genotoxic. Plasma dieldrin concentrations (up to 250 ng/ml) confirmed exposure in workers actively performing termiticide treatments and in maintenance and store workers, when compared with unexposed contro… Show more
“…Aldrin is readily absorbed into the circulating blood from the gastrointestinal tract, through the skin or by inhalation, and is rapidly converted to dieldrin through a mixed function monooxygenase-dependent pathway (aldrin epoxidase) (Hayes 1982). Chronic exposure of animals and human beings to aldrin or dieldrin has resulted in dose-related hepatomegaly and histological changes (Jager 1970;Edwards and Priestly 1994;Huyer 1998). Aldrin demonstrates estrogenic activity by a series of assays such as increase in the weights of uteri in immature and ovariectomized mature rats and binding capacity to recombinant human steroid receptors (Chatterjee et al 1992;Scippo et al 2004).…”
The organochlorine insecticide aldrin is commonly used in intensive agriculture, and demonstrates estrogenic activity. Rotifers such as Brachionus calyciflorus are favored test animals in aquatic toxicology because of their more sensitivity to most toxicants. In the tested concentration range of 0.04-1.28 mg/L, aldrin shortened significantly the durations of embryonic development. Lower concentrations of aldrin had an intriguing effect on the reproduction of the rotifers and are beneficial to their survival. Different endpoints of both development and reproduction had different sensitivity to aldrin. The reproductive endpoint of the rotifers is more sensitive to aldrin than the developmental endpoint.
“…Aldrin is readily absorbed into the circulating blood from the gastrointestinal tract, through the skin or by inhalation, and is rapidly converted to dieldrin through a mixed function monooxygenase-dependent pathway (aldrin epoxidase) (Hayes 1982). Chronic exposure of animals and human beings to aldrin or dieldrin has resulted in dose-related hepatomegaly and histological changes (Jager 1970;Edwards and Priestly 1994;Huyer 1998). Aldrin demonstrates estrogenic activity by a series of assays such as increase in the weights of uteri in immature and ovariectomized mature rats and binding capacity to recombinant human steroid receptors (Chatterjee et al 1992;Scippo et al 2004).…”
The organochlorine insecticide aldrin is commonly used in intensive agriculture, and demonstrates estrogenic activity. Rotifers such as Brachionus calyciflorus are favored test animals in aquatic toxicology because of their more sensitivity to most toxicants. In the tested concentration range of 0.04-1.28 mg/L, aldrin shortened significantly the durations of embryonic development. Lower concentrations of aldrin had an intriguing effect on the reproduction of the rotifers and are beneficial to their survival. Different endpoints of both development and reproduction had different sensitivity to aldrin. The reproductive endpoint of the rotifers is more sensitive to aldrin than the developmental endpoint.
“…Urinary D-glucaric acid (DGA), an index of hepatic enzyme activity, was elevated in pesticide-exposed groups but urinary DGA was poorly correlated with plasma dieldrin level. This indicates that concurrent exposures of these groups to other pesticides may have influenced mixed-function oxidase metabolic activity (53).…”
For centuries, several hundred pesticides have been used to control insects. These pesticides differ greatly in their mode of action, uptake by the body, metabolism, elimination from the body, and toxicity to humans. 801-806 (1997)
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