PubMed · 13164698
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L S DAWSON. 1954. Dieldrin and aldrin.. https://pubmed.ncbi.nlm.nih.gov/13164698/
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This study was conducted to investigate the possible long-term health effects, in particular carcinogenic effects, of occupational exposure to the organochlorine insecticides dieldrin and aldrin. We updated an earlier cohort mortality study of 570 employees involved in the production of these insecticides. All of the employees had worked in the production plants between 1 January 1954 and 1 January 1970 and were followed for cause-specific mortality until 1 January 2001. Based on dieldrin levels in blood samples taken during the exposure period, available for 343 workers, individual estimates of the total intake of dieldrin were estimated for all individual subjects in the cohort. The estimated total intake ranged from 11 to 7755 mg of dieldrin, with an average of 737 mg. One hundred and seventy-one workers had died before 1 January 2001, compared with an expected number of 226.6, giving a standardized mortality ratio (SMR) of 75.6 [95% confidence interval (CI): 64.6-87.7]. This deficit in total mortality was mainly attributable to a deficit in cardiovascular disease mortality, but cancer mortality was also lower than expected. The observed number of deaths from rectal cancer was significantly higher than expected (SMR = 300.0; 95% CI: 109.5-649.3), but was most pronounced in the low-intake subgroup and appears to be unrelated to exposure to dieldrin and aldrin. This study reinforces the earlier findings that occupational exposure of workers to significant amounts of dieldrin and aldrin has not led to a higher cancer mortality than would be found in an unexposed population.
The different isoforms of the cytochrome P450 (CYP) system can metabolise a suite of classes of lipophilic, anthropogenic compounds. The bioaccumulative potential as well as the toxicity of xenobiotics may be significantly altered in the process. To compare the metabolic ability of different wildlife species, it is important to identify the different iso-enzymes of CYP, which are responsible for the metabolism of different classes of compounds. This can be achieved with in vitro incubation assays. In the present study, preparations of hepatic microsomes of a harbour seal (Phoca vitulina) and a grey seal (Halichoerus grypus) demonstrated that the chlorobornane (CHB) congeners CHB-32 and -62 were metabolised enzymatically to their hydroxylated derivatives. These derivatives were partially characterised by their NCI mass-spectra. Inhibition studies were carried out to identify the specific CYP isoform(s) responsible for the metabolism of CHB-32 and -62. Ketoconazole has been shown to inhibit CYP3A enzymes in human and rat studies. In this study, ketoconazole caused concentration-dependent inhibition of metabolism of CHB-32 and -62, reaching 80% at the 1.0 microM treatment level. Ellipticine (1.0 microM), which has been shown to inhibit CYP1A1/2, also inhibited CHB-32 and -62 metabolism in the microsomes of grey seal, but to a much lower degree of less than 10 and 24%, respectively. In the same experiment the metabolism of 4,4'-dichlorobiphenyl was already inhibited 70% by ellipticine treatment at the same concentration. This non-ortho substituted PCB congener can easily attain a planar molecular configuration, and therefore served as a model CYP1A substrate. Inhibition of chlorobornane metabolism was not observed after the addition of goat anti-rat CYP2B antibodies or Aldrin, which is a model CYP2B substrate in rat. Cautious interpretation is advised for results obtained with so-called selective competitive inhibitors. Regardless, these studies indicated for the first time the possible involvement a CYP3A isoform in the mediation of chlorobornane metabolism in seals. The immunochemical cross-reactivity of mouse, rabbit or sheep anti-rat antibodies in the hepatic microsomes of harbour seal confirmed the presence of CYP1A1/2, CYP1A1, CYP2B1/2, CYP3A and CYP4A isoenzymes. Enantioselective metabolism by the microsomes of harbour seal was observed for both CHB-32 and -62. Stereochemical preferences of biotransformation enzymes can have an influence on the environmental distribution of both enantiomers of optically active compounds.
The effect of the cyclodiene organochlorine pesticides aldrin, dieldrin and endosulfan was assessed on CHO-K1 cultures at fractions of their lethal doses, determined by the neutral red (NRI) incorporation assay (NRI6.25, NRI12.5 and NRI25). Glutathione peroxidase, reductase and S-transferase, and total and oxidised glutathione were evaluated along the standard growth curve of the cultures. After a 24-h incubation with each insecticide, glutathione peroxidase incurred a large increase, while glutathione reductase and S-transferase activities were slightly higher than untreated controls. Unlike oxidised glutathione, the content of total glutathione declined significantly after exposure to cyclodiene insecticides. Changes in cell membrane integrity were assessed by the lactate dehydrogenase (LDH) release assay and lipid peroxidation for a wide range of pesticide concentrations. Membrane leakage and peroxide production were significantly enhanced at concentrations of aldrin and as low as 12.5 microg/ml, whereas dieldrin and endosulfan increased membrane fragility at much higher concentrations.