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While acute lindane treatment and chronic ethanol feeding to rats have been associated with hepatic oxidative stress, the possible roles of these stresses in the pathogenesis of hepatic lesions reported in acute lindane intoxication and in those observed in some models of chronic alcoholism have not been established. Our previous studies in rats chronically fed ethanol regimens and then treated with a single intraperitoneal (i.p.) dose of lindane (20 mg/kg) showed that while lindane per se was invariably associated with hepatic oxidative stress, chronic ethanol feeding only produced this stress when the dietary level of vitamin E was relatively low. Chronic ethanol pretreatment did not significantly affect the lindane-associated oxidative stress, and neither chronic ethanol feeding nor acute lindane, single or in combination, produced any histologic and biochemical evidence of liver damage. In the present experiment, the acute dose of lindane was increased to 40 mg/kg, and we have studied a larger number of prooxidant and antioxidant hepatic factors. Male Wistar rats (115.5 +/- 5.4 g) were fed ad lib for 11 weeks a calorically well-balanced and nutritionally adequate basal diet, or the same basal diet plus a 32% ethanol/25% sucrose solution, also ad lib, and were then injected i.p. with a single dose of lindane or with equivalent amounts of corn oil. The results indicated that acute lindane treatment to naive rats increased practically all the prooxidant hepatic factors examined (cytochromes P450 and b5, NADPH cytochrome c reductase, NADPH oxidase), as well as the generation of microsomal superoxide radical and thiobarbituric acid reactive substances of liver homogenates, but did not modify any of the antioxidant hepatic factors studied. Conversely, the chronic administration of ethanol alone did not significantly affect the prooxidant hepatic factors but reduced some of the antioxidants (i.e., the activities of GSH-Px and the contents of alpha-tocopherol and ubiquinols 9 and 10). Although chronic ethanol pretreatment further increased the superoxide generation induced by lindane per se, it did not increase but generally reduced the effects of lindane per se on the other prooxidant factors studied. Furthermore, although acute lindane administration to ethanol-pretreated rats was associated with decreases in GSH and catalase (not affected by ethanol or lindane treatment alone), it did not substantially modify the reducing effects of ethanol feeding per se on GSH-Px, alpha-tocopherol, and ubiquinols. Once again, neither chronic ethanol feeding nor lindane treatment, single or in combination, was associated with any evidence of liver damage.

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Oxidative stress-related parameters in rat brain and liver were evaluated following acute (60 mg/kg i.p., 2 and 24 h after dosing) or short-term (1000 ppm in the diet for 90 days) lindane administration. Both treatments elicited a significant accumulation of lindane in brain and liver, with convulsions observed in short-term and 24-h lindane-treated rats. In these conditions, lindane exposure did not alter brain lipid peroxidation, assessed as thiobarbituric acid reactants formation and spontaneous chemiluminescence, parameters that were enhanced in the liver. The activities of antioxidant enzymes in the brain (superoxide dismutase, catalase, glutathione peroxidase, glutathione reductase and glucose 6-phosphate dehydrogenase) were not modified by acute lindane treatment, while brain glutathione content was significantly reduced by 13%. It is concluded that lindane does not alter the oxidative stress status of the brain as occurs in liver, regardless of the time of exposure of rats to either acute or short-term administration of the insecticide.

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Treatment of rats with daily doses of 20 mg of lindane/kg for 3 consecutive days led to the accumulation of the insecticide in several tissues, including erythrocytes and liver. Lindane did not alter the hematocrit and hemoglobin concentration but reduced methemoglobin levels by 17%. Red blood cells from controls and lindane-treated rats, exposed to t-butyl hydroperoxide, exhibited comparable rates of oxygen uptake and visible chemiluminescence, whereas the induction period that precedes oxygen uptake was significantly enhanced in the latter group. Lindane treatment did not modify the activity of erythrocyte glutathione peroxidase, glucose-6-phosphate dehydrogenase, catalase, and methemoglobin reductase, being the total content of glutathione and superoxide dismutase activity significantly increased. The liver from lindane-treated rats showed an enhanced microsomal pro-oxidant activity, evidenced by higher cytochrome P450 content and NADPH-cytochrome c reductase and NADPH oxidase activities. The higher enzyme activities led to an increased superoxide anion generation (adrenochrome formation) and lipid peroxidation (measured either by the production of thiobarbituric acid reactants and spontaneous visible chemiluminescence). Concomitantly, liver glutathione content and the activity of glutathione peroxidase-glutathione reductase couple were augmented by lindane treatment, without any change in superoxide dismutase activity, together with a reduction in that of catalase. Results suggest that lindane does not alter the prooxidant/antioxidant status of the erythrocyte in conditions of a significant cellular accumulation of the insecticide, which might exert direct action on enzymatic systems leading to enhanced superoxide dismutase activity and glutathione content.(ABSTRACT TRUNCATED AT 250 WORDS)

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Rats treated with increasing doses of pp'-DDT (60, 100 and 180 mg/kg body wt.) i.p., for 24 h, showed a dose-independent increase in liver cytochrome P450 levels, together with an increase in lipid peroxidation, measured as production of thiobarbituric acid reactants. This oxidant condition elicited in the liver by DDT was not accompanied by any change in the activity of NADPH-cytochrome c reductase or in the rate of superoxide anion generation by liver microsomal fraction. The activities of superoxide dismutase and glutathione peroxidase were found to be increased in the higher dose DDT-treated rats, without any change in those from catalase and glutathione reductase. The results presented showed an oxidant condition in the liver elicited by DDT treatment of rats, without any adequate hypothesis proposed to explain these data.

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Parameters related to oxidative stress in rat liver and erythrocytes were studied after short-term administration (60 and 90 days) of 1000 ppm of lindane in the diet. Lindane induced an oxidative stress condition in the liver, which is related to an enhancement in microsomal NADPH-cytochrome c reductase and NADPH oxidase activities, superoxide radical formation and cytochrome P450 content, produced independently of the time of treatment. Also, decreased activities of glutathione peroxidase and catalase were concomitantly observed. Although these changes were paralleled by an increase in lipid peroxidation indices, such as production of thiobarbituric acid reactants and spontaneous chemiluminescence, no evidence of liver injury was obtained. Lindane treatment did not exert quantitatively important changes in the pro-oxidant/anti-oxidant status of the erythrocyte, with reduction in the red blood cell mass possibly reflecting actions of the insecticide on the erythropoietic process.

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The administration of lindane (60 mg/kg) to fed rats diminished the content of hepatic glutathione (GSH) 4 h after treatment, which was recovered at 24 h. At these experimental times, the activities of glutathione peroxidase, glutathione reductase, glutathione-S-transferases and gamma-glutamyltransferase in the liver of lindane-treated rats and control animals were comparable. Liver GSH turnover, measured after a pulse of [35S]cysteine, was enhanced by 69% (P < 0.05) in lindane-treated rats 24 h after intoxication compared to controls, with a 63% (P < 0.05) increase in the estimated rate of GSH synthesis. It is concluded that lindane enhances GSH synthesis in rat liver 24 h after treatment as a consequence of the decrement in its content observed at early times of intoxication (4 h), thus allowing the recovery of the normal level of hepatic GSH.

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1. Lindane administered to untreated rats or rats pretreated with phenobarbital (PB) or 3-methylcholanthrene (MC) increased liver lipid peroxidation, of the same magnitude in all groups. 2. PB pretreatment produced a 50% increase in lipid peroxidation (TBAR) by liver homogenates and microsomes, an effect accompanied by increases in cytochrome P-450, NADPH-cytochrome P-450 reductase, NADPH oxidase and microsomal superoxide anion production, MC pretreatment resulted in increases in liver cytochrome P-450 and NADPH oxidase only. 3. Pretreatment of rats with PB, but not MC or lindane, gave increases in glutathione peroxidase and reductase. 4. Pretreatment with PB, but not MC, increased liver GSH. Lindane decreased liver GSH to the same extent as PB plus lindane. 5. Biliary GSH, GSSG and bile flow were decreased by lindane to similar extents in all groups. 6. Lindane induced periportal necrosis with haemorrhagic foci in all groups. 7. Data presented indicate that the early lipid peroxidative response of liver to lindane was unchanged by PB- or MC-stimulated hepatic microsomal enzyme induction.

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Rats treated with diets containing 20 ppm of alpha- or gamma-hexachlorocyclohexane (HCH) for 15 or 30 days showed increased levels of liver cytochrome P-450 followed by increased production of both thiobarbituric acid reactants by liver homogenates and microsomes and superoxide anion production by liver microsomes. In these animals superoxide dismutase (SOD) activity was also increased. In consequence, the ratio between SOD activity and microsomal superoxide radical (O2-.) production showed a slight increase after 15 days of treatment. However, after 30 days, there was a tendency for this ratio to decrease. Other parameters studied were liver glucose-6-phosphate dehydrogenase, glutathione peroxidase, glutathione reductase and catalase (CAT) activities. Among them, only CAT activity showed a 26% and 38% increase after 15 or 30 days of treatment with the alpha-isomer. It is suggested that when lipid peroxidation is involved in the mechanism of toxicity of a xenobiotic, this parameter can be used to determine the no-observed-effect level.

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1. Lindane (60 mg/kg) administered orally to rats increased liver cytochrome P-450 content and superoxide radical (O2-.) generation 24 h after treatment, while formation of thiobarbituric acid reactants and NADPH/ADP-supported microsomal chemiluminescence were significantly increased 4 h after treatment. 2. Hepatic superoxide dismutase (SOD) and catalase decreased 6 h after lindane treatment and SOD/O2-. ratio progressively decreased during 4 to 24 h after lindane treatment. 3. Morphological evidence of hepatic cell injury after lindane treatment was seen at all times studied, and appeared to increase with time. 4. Lindane administration results in time-dependent oxidative stress in liver which involves an early component (4-6 h) related to the reductive metabolism of lindane, and a late component (24 h) associated with the induction of cytochrome P-450; the biochemical changes correlated with the observed morphological lesions.

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1. Four hours after treatment of rats with lindane (60 mg/kg), hepatic GSH content was decreased (22%) and GSSG was increased (20%), while biliary concentration and excretion of both GSH and GSSG and bile flow were diminished. These changes coincide with the onset of hepatic lipid peroxidation. 2. The changes induced by lindane at 4 h disappeared at 6 h after treatment, but liver GSSG content (91%), biliary GSSG excretion (133%) and bile flow (42%) were enhanced at 24 h. 3. The data indicate that lindane treatment elicits marked changes in hepatocyte glutathione status, with a decrease in the GSH/GSSG ratio at early (2-4 h) and late (24 h) periods of poisoning.

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Foi estudada a atividade de fosfatases acida e alcalina de rim e figado de ratos, tratados por 60 e 90 dias com 900 ppm de hexaclorociclohexano tecnico. Verificou-se uma diminuicao de 46% e 32% na atividade da fosfatase alcalina, respectivamente de figado e rim, apos 60 dias de tratamento com hexaclorociclohexano, sendo que apos 90 dias, a diminuicao dessa atividade e de 37% e 40%, em relacao aos controles. Nao se observou na atividade de fosfatose acida de figado e rim

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Ratos Wistar machos, com 30 dias de idade, foram submetidos a intoxicacao experimental, com 100 ppm de HgCl2, por via oral.Os niveis de lipoperoxidacao hepatica e renal foram avaliados, medindo-se a quantidade total de malonildialdeido (MDA) produzido por homogenados desses orgaos. Nao se obteve nenhuma alteracao na quantidade de MDA produzida pelos homogenados. Cortes histologicos desses orgaos, nos animais tratados, nao mostraram alteracoes, quando comparados com os do grupo controle

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Rabbit muscle aldolase (RMA) is 96 per cent inhibited in the presence of beta-bromopyruvic acid (BPA) in a molar ratio of 1/250, during 60 minutes incubation. The chemical reaction of higher significance in this phenomenon is the alkylation of -SHgroups of both apparent and buried types, with formation of S-pyruvil-cystein. The previous treatment of the enzyme with FDP protects aldolase, decreasing the rate of inhinition by BPA to about 56 per cent. FDP protection of the enzyme protects nearly 5-SH groups against the alkylating effect of BPA. Cyanogen bromide hydrolysis of the carboxymethylated protein results in the classical formation of 4 fragments, peptides F1, the NH-2terminal; F2, the COOH-terminal; F3, the active site containing peptide; and F4, a small peptide located between F2 F3. The protection bestowed upon the enzyme by FDP, against the alkylating effect of BPA, is located in the F1, F2, and F3 either in BPA treated aldolases or in the BPA treated FDP-aldolase. Part of the inhibiting effect of BPA is then attributed to the possible interaction between this compound and the basic aminoacids in the aldolase molecule.

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