Fate of endosulfan in rats and toxicological considerations of apolar metabolites

[¹⁴C]Endosulfan, α or β isomers separately, was administered to rats as a single oral dose and as a dietary supplement for 14 days. No appreciable differences were observed in the fate of the two isomers. Five days after the single dose, 75% of the dose had been voided in the feces and 13% in the urine. Of the total radiocarbon consumed in the diet after 14 days, 56% had been eliminated in the feces and 8% in the urine. Bile collection studies showed that up to 47% of a single oral dose was eliminated from the liver via this route; enterohepatic circulation was not apparent. Maximum [¹⁴C]endosulfan equivalents in body tissue occurred in the kidney and liver, 3 and 1 ppm, respectively, after 14 days of feeding 5 ppm of endosulfan. Apolar metabolites in the excreta and/or tissues were a minor portion of the total residues and consisted of the sulfate, diol, α-hydroxy ether, lactone, and ether derivatives of endosulfan. The sulfate was slightly more toxic to mice than endosulfan, while the other products were less toxic. Neither endosulfan nor its metabolites were active in the Salmonella mutagenicity test. Endosulfan in the diet of rats for 28 days at 50 ppm did not induce liver oxidase enzymes, alter liver or kidney weights, or influence the rate of weight gain of the animals.     

Nile tilapia (Oreochromis niloticus), liver morphology, CYP1A activity and thyroid hormones after Endosulfan dietary exposure

Endosulfan is a worldwide used insecticide suspected to be highly toxic to aquatic organisms, including fish. Most of the available studies have focused in water exposures, although this pollutant can be transferred through food chain. Therefore, in the present study, the effects of Endosulfan on tilapia (Oreochromis niloticus), when administered through the diet. Fish were fed 21 days with diets containing 1 and 0.5 μg g⁻¹ of Endosulfan, after which qualitative histological liver analysis showed that Endosulfan induced hepatocyte destruction, vessel endothelium rupture and increased melanomacrophages aggregates. To test lower environmentally relevant doses of Endosulfan could induce hepatic damage, as well as other negative effects, such as altered phase I metabolism and plasma thyroid hormone levels. Hence, tilapia were orally exposed to 0.1 and 0.001 μg g⁻¹ for 35 days. Low environmentally realistic doses of Endosulfan were still able to induce liver histopathological damage such as increased hepatocyte vacuolization and increased eosinophil granular cell aggregates. Liver cytochrome P450 1A activity, evaluated through ethoxyresorufin-o-deethylase (EROD), was enhanced in tilapia exposed to 0.001 μg g⁻¹, whereas the highest dose had no measurable effects in this enzyme activity. Fish exposed to 0.1 μg g⁻¹ of Endosulfan had depressed T4 plasma levels. Overall, the results of the present study further demonstrate the toxic effects of Endosulfan in tilapia when administered in the diet at environmentally relevant concentrations, which indicates that in the field food chain transfer may also be an importance source of this pollutant.     

Fenthion induced-oxidative stress in the liver of adult rats and their progeny: Alleviation by Artemisia campestris

Fenthion (FEN) is an organophosphate insecticide used in both agricultural and urban areas throughout the world including Tunisia. Recent investigations have proved the crucial role of natural antioxidants to prevent the damage caused by toxic compounds. In this study, we investigated the role of Artemisia campestris (Ac) leaf powder in protection against oxidative damage and hepatotoxicity induced by fenthion in female rats and their pups. Female Wistar rats were divided into four groups: group I served as controls which received standard diet, group II received orally FEN 551 ppm, group III received both 551 ppm of FEN and experimental diet (5% Artemisia) and group IV received experimental diet (5% Artemisia). Oral administration 551 ppm of FEN by drinking water to adult rats caused hepatotoxicity as monitored by the increase in the levels of hepatic markers enzymes (transaminases and lactate dehydrogenase), total cholesterol (TC) and triglycerides (TG), as well as hepatic malondialdehyde (MDA) levels thus causing a drastic alteration in antioxidant defence system. Particularly, the activities of catalase (CAT), superoxide dismutase (SOD), and glutathione peroxidase (GPx) and the level of reduced glutathione (GSH) increased by FEN. These biochemical alterations were accompanied by histological changes marked by leucocytes infiltration, sinusoidal dilatation (moderate peliosis), granuloma inflammatory disorders and necrosis in hepatocytes of dams. While, slight leucocytes infiltration was shown in pups. Treatment with Ac prevented the liver damage induced by FEN, as revealed by inhibition of hepatic lipid peroxidation accompanied by an improvement of liver histopathological changes, CAT and GPx activities except GSH and SOD which were not modified. It could be concluded that A. campestris is promising a protective agent against hepatotoxicity during the exposure to fenthion.     

Nile tilapia (Oreochromis niloticus), liver morphology,CYP1A activity and thyroid hormones after Endosulfan dietary exposure

Endosulfan is a worldwide used insecticide suspected to be highly toxic to aquatic organisms, including fish. Most of the available studies have focused in water exposures, although this pollutant can be transferred through food chain. Therefore, in the present study, the effects of Endosulfan on tilapia (Oreochromis niloticus), when administered through the diet. Fish were fed 21 days with diets containing 1 and 0.5 μg g⁻¹ of Endosulfan, after which qualitative histological liver analysis showed that Endosulfan induced hepatocyte destruction, vessel endothelium rupture and increased melanomacrophages aggregates. To test lower environmentally relevant doses of Endosulfan could induce hepatic damage, as well as other negative effects, such as altered phase I metabolism and plasma thyroid hormone levels. Hence, tilapia were orally exposed to 0.1 and 0.001 μg g⁻¹ for 35 days. Low environmentally realistic doses of Endosulfan were still able to induce liver histopathological damage such as increased hepatocyte vacuolization and increased eosinophil granular cell aggregates. Liver cytochrome P450 1A activity, evaluated through ethoxyresorufin-o-deethylase (EROD), was enhanced in tilapia exposed to 0.001 μg g⁻¹, whereas the highest dose had no measurable effects in this enzyme activity. Fish exposed to 0.1 μg g⁻¹ of Endosulfan had depressed T4 plasma levels. Overall, the results of the present study further demonstrate the toxic effects of Endosulfan in tilapia when administered in the diet at environmentally relevant concentrations, which indicates that in the field food chain transfer may also be an importance source of this pollutant.     

Effect of diethyl phthalate on rat testicular antioxidant system: A dose-dependent toxicity study

The experiment was designed to study toxic effects of diethyl phthalate (DEP) on testicular lipid peroxidation and testicular antioxidants in male Wistar rats for long-term exposure periods at varying concentrations. Healthy male rats were randomly assigned to five groups of six each. Group I male rats were fed on normal diet and water. Group II male rats were maintained on normal diet mixed with corn oil as oil control. Group III, IV and V rats were given diethyl phthalate (DEP) dissolved in minimal quantity of corn oil mixed with the diet at 10, 25 and 50 mg/kg of the diet/day, respectively, for 150 days. Body weight, testis weights, epididymis weight and the serum testosterone and androstenedione levels showed a significant decrease in the three treated groups. Testicular lipid peroxidation showed a significant dose-dependent increase, while testicular antioxidant enzymes including superoxide dismutase (SOD), glutathione peroxidase (GPx) and glutathione reductase (GR) were significantly decreased. These results confirm that, continuous administration of DEP at various concentrations on a long-term basis induces increased levels of lipid peroxidation leading to dose-dependent reduction in the testicular antioxidant defense system. Increased free radical production at various doses of DEP would result in impairment of the defense system leading to an enhanced dose-dependent reproductive toxic effect.     

Mirex residues in bobwhite quail after aerial application of bait for fire ant control, South Carolina--1975-76

Mirex, the organochlorine compound used for control of the imported fire ant (Solenopsis invicta Buren), was applied aerially under supervision of the South Carolina Plant Pest Regulatory Service in October 1975 to a game management area in Hampton County, S.C. Influenced by recent reports indicating that low levels of mirex were toxic to certain nontarget organisms in laboratory studies, authors initiated a program for monitoring mirex residues in bobwhite quail (Colinus virginianus). Pretreatment residues were recorded on a dry-weight basis in bobwhite quail breast and adipose tissue; conversion factors for determining wet-weight concentrations are approximately as follows: fat, 0.77; and breast, 0.29. Residues ranged from 0.000-0.178 ppm and 0.247-2.763 ppm, respectively. Mirex residues in quail adipose tissue showed up to five-fold increase within the first month after treatment and declined thereafter. A residue peak was noticed the spring following mirex treatment, corresponding with insect emergence. Mirex residues in quail collected in summer 1976 following a fall bait application showed slightly higher residue levels than had birds taken in summer 1975; however, little, if any, human food chain contamination would result in the consumption of birds with residue levels found in this study.     

A two generation chronic mixture toxicity study of Clophen A60 and diethyl phthalate after gestational and lactational exposure in female Wistar rats

Polychlorinated biphenyls and diethyl phthalate are both lipophilic in nature and are likely to be present in the same environmental compartment or bioaccumalate over a period of time, thus a mixture toxicity study was undertaken to evaluate the type of interaction between polychlorinated biphenyls (Clophen A60) and diethyl phthalate over two generations in female Wistar rats. Healthy male and female albino rats of Wistar strain weighing 75-100 g (6-7 weeks old) were randomly assigned to four groups of six each. Group I male and female rats were fed on normal diet and water ad libitum. Group II male and female rats were maintained on normal diet mixed with corn oil as oil control. GroupS III and IV male and female rats were given Clophen A60 and diethyl phthalate dissolved in corn oil mixed with the diet at 50 mg/kg of the diet individually to each group. Group V male and female rats received a mixture of diethyl phthalate and Clophen A60, each dissolved in corn oil mixed with the diet at 50 mg/kg of the diet. Hundred days after the treatment, females were mated with the males in each group for 10 days. Exposure to diethyl phthalate and Clophen A60 was continued throughout mating, gestation until termination at weaning, which was 150 days of total treatment period of the parental generation female rats. Treatment for F1 generation male and female pups (6 males & 6 females) with Clophen A60 and diethyl phthalate individually and in mixture was continued at doses reduced to 25 mg/kg of the diet after they reached 75-100 g in weight. The treatment was carried out similar to the parental generation for a period of 150 days. Liver and serum aspartate aminotransferase, liver cholesterol and glycogen were significantly increased in the F1 generation Clophen A60 + diethyl phthalate treated group, whereas serum cholesterol, liver glutathione and glutathione reductase showed a significant decrease in the F1 generation Clophen A60 + diethyl phthalate treated group as compared to the parental generation mixture and individually treated groups as well as the individually treated F1 generation groups. A significant increase was observed in the liver and serum aspartate aminotransferase activity of Clophen A60 and serum aspartate aminotransferase levels of diethyl phthalate treated F1 generation rats as compared to the parental generation Clophen A60 and diethyl phthalate individually and mixture treated rats. Liver glutathione levels were significantly decreased in the F1 generation Clophen A60 and diethyl phthalate individually treated rats which was similar to the parental generation individually treated rats as compared to the controls. Liver glutathione reductase level was also significantly declined in the diethyl phthalate treated F1 individual group as compared to diethyl phthalate individually treated parental generation rats. Histology of the liver showed fatty degeneration in the mixture treated F1 generation rats as compared to Clophen A60 and diethyl phthalate individually treated F1 rats and parental generation Clophen A60 and diethyl phthalate individually and mixture treated rats. Thus, in spite of dose reduction and continuous exposure over two generation’s to a mixture of diethyl phthalate and Clophen A60 exposed through gestation, lactation and diet leads to a synergistic toxic effect in the F1 generation.     

Organochlorine pesticide residues in small migratory birds, 1964-73.

Chlorinated hydrocarbon pesticide burdens, especially those of DDT and its metabolites, have been determined for 19 species of small terrestrial migratory birds killed chiefly at Florida television towers from 1964 to 1973. All 128 samples were sorted into pools by species. All pooled samples except one contained DDE and often DDT and DDD; dieldrin was present in 60 of the samples; but no PCB's were detected. In small subsamples, sigma DDT (p,p'-DDT, p,p'-DDD, and p,p'-DDE) residues sometimes differed between males and females, adults and immatures, and northbound and southbound migrants but results of these comparisons were inconclusive. Sigma DDT burdens were highest in adipose tissue and much lower in liver and brain samples. Especially among birds taken since 1970 have the pesticide levels in adipose tissue been at low levels, generally less than 3 ppm sigma DDT. These low quantities are comparable to those quoted in other reports on birds of similar trophic levels. The insectivorous and/or partly granivorous birds feeding on or near the ground tended to have higher sigma DDT levels than did the more arboreal species.     

Effects of N-acetylcysteine on oxidative responses in the liver of fenthion exposed Cyprinus carpio

The aim of this study was to evaluate the effects of different N-acetylcysteine doses on the tolerance to fenthion-induced oxidative stress, alterations in glutathione metabolism and cholinesterase specific activities in the liver by using freshwater fish Cyprinus carpio (Cyprinidae) as a model organism. An acute toxicity study was carried out to determine 96-h median lethal concentration of fenthion for this species (2.16 mg/L) and 80% of this concentration was applied in toxicity studies. Four groups, each containing eight fish were constituted as follows: Control group, fenthion treated group, 0.5 or 400 mg/kg NAC-injected + fenthion-treated groups. Biochemical analyses were carried out spectrophotometrically. Fenthion treatment significantly decreased total glutathione and glutathione levels, glutathione/glutathione disulfide ratio together with glutathione reductase and γ-glutamylcysteine synthetase specific enzyme activities. The higher dose of N-acetylcysteine increased the toxic effects of fenthion and γ-glutamyl transpeptidase specific activity while decreasing glutathione S-transferase specific activity. However, injection of the lower dose provided a limited protection against fenthion toxicity. In all exposure groups, lipid peroxidation increased and total protein levels decreased, while protein depletion was prevented by low dose of N-acetylcysteine application. Acetylcholinesterase and butyrylcholinesterase activities were at similar levels in the liver of C. carpio. A dose-dependent inhibition was observed in butyrylcholinesterase activity by N-acetylcysteine application. The results showed that fenthion had a significant oxidative stress inducing potential through the reduction of glutathione redox capacity. The critical point for overcoming oxidative stress by N-acetylcysteine in fenthion toxicity was the selection of the dose; N-acetylcysteine exerted its toxic effects by means of oxidative stress in fish liver at the higher dose.     

In vivo chlorpyrifos induced oxidative stress: Attenuation by antioxidant vitamins

Chlorpyrifos (O,O′-diethyl O-3,5,6-trichloro-2-pyridyl phosphorothionate, CPF) exposure in rats causes elevation in the levels of thiobarbituric acid reactive substances (TBARS) and inhibition of acetylcholinesterase (AChE), superoxide dismutase (SOD), catalase (CAT), and glucose-6-phosphate dehydrogenase (G6PDH) activities in the liver, kidney, spleen, and brain of rats. The sublethal exposure of CPF also causes decrease in the levels of reduced glutathione (GSH) and consequent increase in oxidized glutathione (GSSG) levels, resulting in a significant decrease in GSH/GSSG ratio in all the rat tissues tested. These results clearly indicate that CPF exposure causes oxidative stress in rat tissues. However, CPF exposure to rats fed with antioxidant vitamins (vitamin A, E, and C) for 1 month, prevented derangement of these antioxidant parameters. The accumulation of TBARS was also not seen in tissues of rats fed with antioxidant vitamins on CPF exposure. AChE activity, which is sensitive to OP pesticides, was also not significantly inhibited in these rats on CPF exposure. The present findings clearly show that oral intake of a mixture of vitamin A, E, and C, protects the rats from CPF induced oxidative stress and suggesting that this treatment alleviates the toxicity of this pesticide.     

Reproductive toxicity in pseudopregnant and pregnant rats following postimplantational exposure: Effects of the herbicide dinoseb

In Day 10 decidualized pseudopregnant rats fed dinoseb in the diet from Days 6 through 9 of pseudopregnancy, uterine wet weight was reduced in the groups fed 100 to 750 ppm (the highest dose tested). Uterine protein and glycogen concentrations in these animals were reduced in a dose-related manner. In Day 16 pregnant rats, orally fed dinoseb from Days 6 through 15 of pregnancy, placental protein and glycogen concentrations were diminished at 200 ppm and greater. Pregnant rats fed dinoseb (Days 6–16) showed reductions in their embryonic survival rates at 200 ppm and greater. The fetal survival rates at birth, from pregnant rats which were similarly administered dinoseb, were reduced at 150 ppm and greater. Fetal weight of fetuses from dams given dinoseb (200 ppm) was diminished. These results from decidualized pseudopregnant and pregnant rats indicate a toxic role for dinoseb in the intrauterine environment. This toxicity is apparently responsible for a decline in fertility in pregnant rats. Moreover, 200 ppm dinoseb seems to be reproductively critical.     

The in vivo effect of mirex on soluble hepatic enzymes in the rat

Adult male and female rats fed dietary mirex in concentrations of 10, 20, 30, 40, and 50 ppm for 4 weeks exhibited significant decreases in liver levels of lactic dehydrogenase, malic dehydrogenase, sorbitol dehydrogenase, glutamic oxaloacetic transaminase, and glutamic pyruvic transaminase as compared to control levels. Enzyme losses were cytoplasmic and decreased in magnitude with increased time of exposure and dietary mirex concentrations. Serum sorbitol dehydrogenase levels were increased above control levels during the first week of mirex exposure while hepatic sorbitol dehydrogenase levels were concomitantly decreased below the control levels. Hepatic glutamic oxaloacetic transaminase levels were significantly decreased during the first week for all dietary mirex concentrations as were the other enzymes at the 40 and 50 ppm mirex concentrations. The magnitude of the enzyme decreases in female rat tissue was consistently lower than enzyme decreases in the male rat tissue fed equivalent dietary mirex dosages. Liver weights for male rats increased significantly at all dietary mirex levels during week one. However, only animals receiving the 40 and 50 ppm dietary mirex levels showed significant liver weight increases at the end of week 4. Female rat liver weights were increased at the 30 and 40 ppm mirex dietary levels after 4 weeks. No significant differences in body weights were observed for any dietary level of mirex. Mirex hepatic residues appeared to be equal for both sexes. No gross histological alterations were observed following treatment.     

Determination of toxicity of trichloroacetic acid in rats: 50 days drinking water study

This study aims to investigate the effects of the trichloroacetic acid (TCA) on serum marker enzymes [aspartate aminotransferase (AST), alanin aminotransferase (ALT), creatine phosphokinase (CPK), acid phosphatase (ACP), alkaline phosphatase (ALP) and lactate dehydrogenase (LDH)], antioxidant defense systems [Reduced glutathione (GSH), glutathione reductase (GR), superoxide dismutase (SOD), glutathione-S-transferase (GST) and catalase (CAT)] and lipid peroxidation content (Malondialdehyde, MDA) in various tissues of rats. TCA (2000 ppm) as drinking water was administered orally to rats (Sprague-Dawley albino) ad libitum for 50 days continuously. TCA treatments caused different effects on the serum marker enzymes, antioxidant defense systems and the MDA content in experimented rats compared to controls. Results showed that TCA caused a significant increase in serum AST, ALT, CPK and ACP activity. The lipid peroxidation end product MDA slightly increased in the erythrocytes, liver and kidney of rats treated with TCA, whereas did not change in the brain. In addition, antioxidant enzyme activity such as CAT and SOD significantly increased in the brain, liver and kidney tissues of TCA induced group whereas the ancillary enzyme GR and the drug metabolizing enzyme GST activity did not significantly change in the all tissues. The observations presented led us to conclude that the administration of subchronic TCA promotes lipid peroxidation content, elevates tissue damage serum marker enzymes and fluctuates in the antioxidative systems in rats. Also the rats resisted to oxidative stress via antioxidant mechanism but the antioxidant mechanism could not prevent the increases in lipid peroxidation in rat’s tissues. These data, along with the determined changes suggest that TCA produced substantial systemic organ toxicity in the erythrocyte, liver, brain and kidney during the period of a 50-day subchronic exposure.     

Antioxidant and immune potential marker enzymes assessment in the various tissues of rats exposed to indoleacetic acid and kinetin: A drinking water study

In the present study, the influence of two different PGRs, indoleacetic acid (IAA) and kinetin (Kn) on immune potential enzymes, adenosine deaminase (ADA) and myeloperoxidase (MPO), and antioxidant defense enzymes such as glutathione peroxidase (GPx), glutathione reductase (GR), and superoxide dismutase (SOD) in various tissues of rats were investigated during the treatment as a drinking water model. 100 ppm of IAA and Kn as drinking water were administered orally to rats (Sprague-Dawley albino) ad libitum for 21 days continuously. The PGRs treatments caused different effects on the immune potential and antioxidant defense enzymes of experimented rats compared to controls. Results show that IAA caused a significant decrease in GR activity in the lungs and liver and an increase in the spleen. Also, IAA caused a significant decline in GPx activity in the lungs and an increase in the heart. SOD was significantly reduced in the heart, while increased in the lungs. Furthermore, IAA caused a significant decrease in ADA activity in the heart and blood whereas an increase in the kidney and spleen. MPO activity was also significantly increased in the heart by IAA treatment. The activity of enzymes were also seriously affected by Kn; GR activity decreased in the lungs, brain, and blood while GPx activity decreased in the spleen, brain, and heart. ADA activity was also significantly reduced in the blood whereas MPO activity rose in the spleen. In addition, SOD activity lowered in all tissues except for lungs where a significant increment was determined. As a conclusion, the results indicate that PGRs might affect on antioxidant and immune potential enzymes. These data, along with the determined changes suggest that PGRs produced substantial systemic organ toxicity in the erythrocyte, liver, brain, heart, lungs, spleen, and kidney during the period of a 21-day subacute exposure.     

Influence of subacute and subchronic treatment of abcisic acid and gibberellic acid on serum marker enzymes and erythrocyte and tissue antioxidant defense systems and lipid peroxidation in rats

This study describes the subacute and subchronic effects of two plant growth regulators (PGRs) [abcisic acid (ABA) and gibberellic acid (GA₃)] on serum marker enzymes [aspartate aminotransferase (AST), alanine aminotransferase (ALT), creatine phosphokinase (CPK) and lactate dehydrogenase (LDH), γ-glutamil transpeptidase (GGT)], antioxidant defense systems [reduced glutathione (GSH), glutathione reductase (GR), glutathione peroxidase (GPx), superoxide dismutase (SOD), glutathione-S-transferase (GST) and catalase (CAT)] and lipid peroxidation level (Malondialdehyde = MDA) in various tissues of rats. Rats (Sprague-Dawley albino) were exposed to 75 ppm (parts per million) of ABA and GA₃. Seventy-five parts per million of PGRs as drinking water was administered orally ad libitum for 25 and 50 days continuously. The PGRs treatments caused different effect on the serum marker enzymes, antioxidant defense systems and the content of MDA in comparison to those of control rats. Results show that ABA caused a significant decrease in serum LDH and CPK activity with both periods. Also, GA₃ significantly decreased serum AST, CPK, and LDH activity with subacute and decreased serum ALT, CPK, LDH, and GGT treated with subchronic periods. The lipid peroxidation end product MDA significantly increased in the erythrocyte, liver, brain, and muscle of rats treated with both the period of GA₃ without significantly change in the erythrocyte and muscle of rats treated with the subacute period of ABA. The GSH levels were significantly depleted in the erythrocyte and brain of rats treated with both the period of GA₃ without any change in the erythrocyte, liver, brain, and muscle of rats treated with both the period of ABA. Also GSH levels in the muscle significantly depleted with the subchronic period of GA₃. Antioxidant enzyme activities such as SOD significantly decreased in the erythrocyte, liver and brain tissues but increased in the muscle tissue of rats treated with both the periods of GA₃. Meanwhile, SOD significantly decreased in liver and brain, and increased in muscle of rats treated with both the period of ABA. While CAT significantly decreased in the all tissues of rats treated with both the period of GA₃, decreased in the liver and muscle of rats treated with both the periods of ABA too. On the other hand, the ancillary enzyme GPx and GR activity in the erythrocytes, liver, brain and muscle were either significantly depleted or not changed with two periods of PGRs. The drug metabolizing enzyme GST activity significantly decreased in the brain of rats treated with subacute period of PGRs but increased in the erythrocytes of rats treated with subacute period of GA₃. As a conclusion, ABA and GA₃ had significantly increased the activity of hepatic damage enzymes. Also the rats resisted to oxidative stress via antioxidant mechanism. However, the antioxidant mechanism could not prevent the increases in lipid peroxidation in rat’s tissues. These data, along with changes, suggest that PGRs produced substantial systemic organ toxicity in the erythrocyte, liver, brain, and muscle during the period of a 25-day subacute and 50-day subchronic exposure.     

Metabolism and toxicity of metribuzin in mouse liver

Metribuzin was hepatotoxic in mice when administered intraperitoneally (ip) at sublethal doses of 150 to 250 mg/kg. Four dose-dependent abnormalities were evident. Histopathological examination revealed a fulminant centrilobular hepatic necrosis. The serum glutamic-pyruvic transaminase (GPT) activity was elevated. The liver glutathione (GSH) content was almost completely depleted. There was extensive covalent binding of radiocarbon from [carbonyl-¹⁴C]metribuzin to liver proteins and also high blood levels of metribuzin fragments. Each of these four effects of metribuzin on the liver or blood was alleviated or blocked in mice pretreated with piperonyl butoxide (PB), which inhibits the cytochrome P-450-dependent monooxygenase. PB also reduced the lethality of metribuzin by three-fold. In contrast, pretreatment with diethyl maleate to suppress the liver GSH content increased the lethality of metribuzin by twofold. The hepatotoxicity and acute lethality of metribuzin were probably due to reactive intermediates which are normally detoxified by GSH conjugation. The principal urinary metabolites of metribuzin in mice and rats are mercapturic acids, which arise via metribuzin sulfoxide or deaminometribuzin sulfoxide reacting with GSH. Sulfoxidation therefore appears to activate metribuzin to an electrophilic metabolite which, in the absence of GSH, binds to tissue proteins producing hepatotoxicity.     

Dimethoate induced biochemical perturbations in rat pancreas and its attenuation by cashew nut skin extract

The significant antiradical activity of cashew skin extract was previously described. In this investigation, the extent of protection offered by cashew nut skin extract (CSE) against the damage induced in rat pancreas by sub chronic doses dimethoate (DM), an organophosphorous pesticide was studied. Rats were supplemented with CSE at 20 mg/kg b.w./d after a daily dose of DM at 40 mg/kg/d b.w. for 2 months. Weekly random blood glucose, oral glucose tolerance test (OGTT); pancreatic damage markers like amylase and lipase; oxidative damage markers such as reactive oxygen species generated, extent of lipid peroxidation, host antioxidant defenses like reduced glutathione (GSH); GSH-dependent enzyme activities viz., glutathione peroxidase (GPx), glutathione S-transferase (GST), glutathione reductase (GR); free radical scavenger enzymes viz., catalase and superoxide dismutase (SOD); xenobiotic metabolizing enzymes like DT-diaphorase and NADPH-diaphorase were measured in the four different groups namely (1) control, (2) DM treated, (3) CSE supplemented, (4) CSE supplements following DM treatment. Random blood glucose levels increased significantly on exposure to DM compared to that in control rats (119 ± 5 mg/dl vs. 92 ± 4 mg/dl), while the blood glucose levels in CSE supplemented rats were comparable to that of controls. DM treated rats exhibited impaired glucose tolerance at the end of two months as indicated by OGTT, while DM treated rats with CSE supplements showed normal glucose tolerance. Pancreatic specific marker enzymes like amylase and lipase in serum were restored to normalcy in rats supplemented with CSE following treatment with DM which otherwise was increased in the DM treated rats. Distinctly lower levels of GSH, increased levels of ROS, higher extent of lipid peroxidation, along with alterations in antioxidant enzymes and increase in xenobiotic metabolizing enzymes were evident in pancreas of DM treated rats. However, CSE supplement ameliorated the biochemical alterations in the pancreatic milieu in DM treated rats. Treatment with CSE significantly protected rat pancreas from injury, thus ameliorating and restoring tissue antioxidant status and also conferring normal glucose tolerance. The active components present in cashew skin extract can perhaps be effective in reducing the extent of pancreatic injury and in overcoming tissue damage caused by exposure to dimethoate.     

Selenium and vitamin E, natural antioxidants, protect rat cerebral cortex against dimethoate-induced neurotoxicity

Pesticides have been used in agriculture to enhance food production by eradicating unwanted insects and controlling disease vectors, nevertheless occupational exposure to high levels of these compounds can lead to neurodegenerative disorders, characterized by serious oxidative and neurotoxic effects. However, there is a lack of consensus as to which determinations are best used to quantify future risks arising from xenobiotic exposure and natural antioxidant interventions. Our study aims to determine the potential ability of selenium and/or vitamin E, used as nutritional supplements, to alleviate oxidative stress in cerebral cortex tissue induced by dimethoate, an organophosphorus pesticide. Adult Wistar rats were exposed either to dimethoate (0.2 g/L of drinking water), dimethoate + selenium (0.5 mg/kg of diet), dimethoate + vitamin E (100 mg/kg of diet), or dimethoate + selenium + vitamin E, for 30 days. Exposure to dimethoate increased malondialdehyde levels, protein carbonyl groups and advanced oxidation protein products, while Na⁺K⁺-ATPase, acetylcholinesterase and butyrylcholinesterase activities decreased in the cerebral cortex. An increase in glutathione peroxidase, superoxide dismutase and catalase activities and a decrease in glutathione, non-protein thiols and vitamin C levels were observed. Administration of selenium and/or vitamin E through the diet in dimethoate treated rats ameliorated the biochemical parameters cited above. The histological findings confirmed the biochemical results. The model of this study that we employed characterized the relationships between dimethoate-induced neurotoxicity and its alleviation by natural antioxidants like selenium and vitamin E. These elements may be considered beneficial for the protection of cerebral cortex against injury induced by dimethoate.     

Dose-dependent sub-chronic toxicity of diethyl phthalate in female Swiss mice

The experiment was conducted to study the after effects of administering DEP at different doses to female Swiss mice for a period of 90 days. Group I mice were fed on normal diet and water ad libitum. Group II mice were maintained on normal diet mixed with corn oil at 8.25 mg/kg of the diet/day as oil control. Group III, IV and V mice were given diethyl phthalate dissolved in corn oil mixed with the diet at 10, 25 and 50 mg/kg of the diet/day, which is approximately equal to 1.25, 3.125 and 6.25 mg/kg body weight/day. A significant dose dependent increase was observed in serum acid phosphatase (ACP) whereas, serum and liver triglycerides levels showed a significant increase only in the high-dose treated group. Significant dose-dependent increase in serum aspartate and alanine aminotransferase (AST and ALT) and liver glycogen was observed. Serum lactate dehydrogenase (LDH) was significantly increased only in 25 and 50 ppm DEP-treated mice. Liver cholesterol was significantly increased in all the treated groups. Liver histology by light microscopy showed intracellular vacuolations in all the treated groups which was much more evident in the 25 and 50 ppm DEP-treated mice while hepatocellular degeneration and hypertrophy of the hepatocytes was evident in 50 ppm DEP-treated mice. Proliferation of mitochondria and peroxisomes was evident in the electron micrographs of the 10 ppm DEP-treated mice while 25 and 50 ppm DEP-treated mice showed increase in lipid droplets and severe mitochondrial proliferation.