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Query: EC:2.5.1.18 (
glutathione S-transferase
)
22,582
document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)
In this study we demonstrate that
chloroform
, a widely used industrial solvent, a medicinal chemical and a common drinking water contaminant, reduces the number of detectable preneoplastic enzyme-altered foci [gamma-glutamyltranspeptidase-positive (GGT+) and placental form
glutathione S-transferase
-positive (
GST
-P+)] in the liver of male Fischer 344 rats. The animals were given a partial hepatectomy and 18 h later received a single oral dose of either 0.5 mmol/kg diethylnitrosamine (DENA) or saline. Two weeks later, groups of 12 animals were started on drinking water containing phenobarbital with varying concentrations (200-1800 mg/l) of
chloroform
fro 12 weeks. Treated and control animals were killed and the number and the volume of GGT+ and
GST
-P+ expressing hepatic foci were tabulated. The numbers of foci per unit volume (and per unit area), the percent focal volume and the focal liver were reduced by
chloroform
in a dose-dependent manner. The mean focal volume was not influenced by
chloroform
. A plausible explanation for these results could be that
chloroform
exerts its focal inhibitory effect either by selectively killing the putative initiated cells, by retarding the inherent growth rate of enzyme-altered cells or by reducing the effectiveness of the promoter, phenobarbital. The available evidence suggests that the first hypothesis is the most likely explanation for these observations. These results are consistent with earlier studies showing that
chloroform
inhibits tumorigenesis in rodents.
...
PMID:Chloroform inhibits the development of diethylnitrosamine-initiated, phenobarbital-promoted gamma-glutamyltranspeptidase and placental form glutathione S-transferase-positive foci in rat liver. 135 81
The
glutathione S-transferase
activity in liver and kidney cytosol was significantly decreased in short term diabetes induced with streptozotocin, whereas no decrease in the transferase was observed in phenobarbital-treated diabetic rats. Toxicity of
chloroform
was potentiated in streptozotocin- or phenobarbital-treated rats. The decrease in liver cytosolic and microsomal
glutathione S-transferase
activity was observed in long term diabetic rats, and only microsomal transferase activity was restored by insulin treatment. There was no release of glutathione S-transferases into the serum in the diabetic rats, and the transferases were not inhibited by streptozotocin in vitro. These results showed that
glutathione S-transferase
activity decreased during diabetes, and this decrease may contribute to altering drug metabolism and toxicity in diabetes.
...
PMID:Glutathione S-transferases and chloroform toxicity in streptozotocin-induced diabetic rats. 276 Nov 28
The ability of S-9 fractions isolated from the livers of 4-, 12-, and 26-month-old male inbred F344 rats to activate and metabolize the hepatocarcinogen aflatoxin B1 [(AFB1) CAS: 1162-65-8] was studied. The following observations were made: The activation of AFB1 to compounds that are mutagenic in the Ames Salmonella-microsome test and to compounds that covalently bind DNA in vitro was similar for liver S-9 from 4- and 12-month-old rats. A 30-50% decrease in the activation of AFB1 occurred in rats between 12 and 26 months of age. The in vitro metabolism of AFB1 to
chloroform
-soluble and water-soluble metabolites was similar for 4- and 12-month-old rats and decreased significantly in rats after 12 months of age. The proportion of most of the
chloroform
-soluble metabolites of AFB1 formed by liver S-9 from 4-, 12-, and 26-month-old rats was similar. However, the proportion of aflatoxicol (CAS: 29611-03-8) produced by liver S-9 increased approximately twofold in rats between 12 and 26 months of age. The cytochrome P450 content and the NADPH cytochrome c reductase activity of liver microsomes decreased 40-45% in rats between 12 and 26 months of age. However, the activities of UDPglucuronyltransferases and most forms of
glutathione S-transferase
did not change significantly with increasing age in liver microsomes and cytosol, respectively.
...
PMID:Metabolism, covalent binding, and mutagenicity of aflatoxin B1 by liver extracts from rats of various ages. 391 13
The effects of food deprivation, carbohydrate restriction and ethanol consumption on the metabolism of eight volatile hydrocarbons (benzene, toluene, styrene,
chloroform
, carbon tetrachloride, 1,2-dichloroethane, 1,1-dichloroethylene and trichloroethylene) in rats were compared with the effects of enzyme induction by phenobarbital (PB), polychlorinated biphenyl (PCB) and 3-methylcholanthrene (MC) on the metabolism of these compounds. Although causing a marked increase both in microsomal protein and cytochrome p-450 contents, PB (80 mg/kg per day for three days) and PCB (a single dose of 500 mg/kg) induced only a limited range of enzyme activity: PB increased the metabolism of toluene, styrene,
chloroform
, carbon tetrachloride and trichloroethylene, and PCB only increased those of toluene, styrene and trichloroethylene. MC (20 mg/kg per day for three days) had no effect on the metabolism of any of the hydrocarbons studied. In contrast, food deprivation, carbohydrate restriction and three-week ingestion of ethanol (2.0 g/day), each enhanced the metabolism of all the hydrocarbons with little or no increase in microsomal protein and cytochrome P-450 contents. PB, PCB and MC treatments enhanced the activity of enzymes involved in conjugation reactions, UDP-glucuronyltransferase and
glutathione S-transferase
, whereas the dietary manipulation and ethanol consumption produced no significant effect on these enzymes. It is concluded that ethanol consumption. lowered carbohydrate intake and food deprivation affect the metabolism and toxicity of volatile hydrocarbons differently from PB, PCB or MC.
...
PMID:Enhanced metabolism of volatile hydrocarbons in rat liver following food deprivation, restricted carbohydrate intake, and administration of ethanol, phenobarbital, polychlorinated biphenyl and 3-methylcholanthrene: a comparative study. 392 Aug 36
The effect of
chloroform
treatment on the hepatic glutathione S-transferases was studied in phenobarbital-treated rats. The apparent isozymic composition of glutathione S-transferases in hepatic cytosol was changed after
chloroform
treatment. Glutathione S-transferases AA, A, B, C, and D + E were observed in hepatic cytosol from untreated rats; in contrast, the catalytic activity associated with basic glutathione S-transferases, such as AA, A, B, and C, decreased with time after
chloroform
treatment. Glutathione S-transferase B was not detectable 2 hr after
chloroform
treatment, and glutathione S-transferases AA and C were scarcely detectable after 5 hr. Twenty-four hours after
chloroform
treatment, glutathione S-transferases A and C were clearly detectable as was D + E and a small amount of B. Hepatic cytosolic
glutathione S-transferase
activity was decreased by
chloroform
treatment, and reached a minimum at 5 hr after treatment. Corresponding to the decrease of hepatic cytosol
glutathione S-transferase
activity, serum
glutathione S-transferase
activity was elevated maximally 5 hr after
chloroform
treatment and returned to almost normal by 24 hr. Treatment of rats with SKF 525-A or cysteine inhibited the
chloroform
-induced elevation of serum
glutathione S-transferase
activity. The chromatographic properties of the glutathione S-transferases present in serum were similar to
glutathione S-transferase
D + E. Furthermore, after incubation of partially purified cytosolic glutathione S-transferases with
chloroform
in the presence of hepatic microsomes and NADPH, only transferase D + E was detected. The addition of bilirubin to partially purified cytosolic
glutathione S-transferase
decreased the basic character of glutathione S-transferases B and C. In conclusion,
chloroform
caused a release of hepatic cytosolic glutathione S-transferases into serum. Both the active metabolite of
chloroform
, which was produced by the microsomal cytochrome P-450 system, and bilirubin, which was increased by
chloroform
treatment, played roles in altering the properties of the glutathione S-transferases.
...
PMID:Chloroform-induced alteration of glutathione S-transferase activity. 396 26
Previous work demonstrated that exposure of laboratory animals including fish to certain organochlorine (OC) insecticides altered the tissue distribution of a subsequent tracer dose of the same [14C]OC. In the present study, 10- to 20-g rainbow trout were exposed to 15 ppm dieldrin in the diet. Fish were subsequently challenged at 2-week intervals with an intraperitoneal injection of 0.1 mg/kg [14C]dieldrin and viscera (liver, bile, mesenteric fat, kidney, and intestine) analyzed for radioactivity, 24 hr later. After 10 and 12 weeks of dieldrin pretreatment, [14C]dieldrin was significantly elevated relative to controls in liver (200%), bile (500%), and fat (500 and 1200% for 10 and 12 weeks, respectively) of pretreated fish. Other tissues were unchanged.
Chloroform
/methanol extractions revealed a time-dependent increase in label disposition to carcass lipid in controls but not in pretreated fish. Altered disposition could not be explained by changes in total body lipid or induction of total cytochrome P-450 or ethoxyresorufin-O-deethylase, pentoxyresorufin-O-deethylase,
glutathione S-transferase
, or UDP glucuronosyltransferase activities. In vivo assessment of [14C]dieldrin metabolism revealed no increase in hepatic and only a slight (22%) increase in biliary polar:nonpolar concentration ratio after 9 weeks 20 ppm dieldrin pretreatment. Results suggest that constitutive changes in liver integral to dieldrin sequestration, transport, or excretion may be an adaptive response of trout to chronic OC exposure.
...
PMID:Chronic dieldrin exposure increases hepatic disposition and biliary excretion of [14C]dieldrin in rainbow trout. 850 3
Trihalomethanes (THMs) are the most prevalent disinfection by-products identified in chlorinated drinking water. Among the THMs,
chloroform
(
CHCl3
) generally occurs at the highest concentration in finished water, but the concentrations of each of the brominated THMs (CHBrCl2, CHBr2Cl, and CHBr3) can exceed that of
CHCl3
. Each of these four THMs was carcinogenic in rodents in chronic oral dosing studies. This study assessed THM mutagenicity in a strain of Salmonella typhimurium TA1535 that was transfected with rat theta-class
glutathione S-transferase
T1-1 (+GST). The +GST strain and its nontransfected parent strain (-GST) were employed in a plate-incorporation assay and exposed for 24 hr to the vapor of individual THMs at concentrations up to 25,600 ppm in sealed Tedlar bags. Base-substitution revertants were produced in the +GST strain in a dose-dependent fashion by CHBrCl2 but not by
CHCl3
. At 4800 ppm CHBrCl2, which produced a calculated agar concentration of 0.67 mM, there were 419 +/- 75 revertants per plate compared to a spontaneous level of 23 +/- 5.
CHCl3
produced a doubling of revertants only at the two highest concentrations tested (19,200 and 25,600 ppm). These results indicate that bromination of THMs confers the capability for theta-class
GST
-mediated transformation to mutagenic intermediates at low substrate concentrations, suggesting the possibility of a similar activation route in humans. Further, the very low affinity of the GSH-dependent pathway for
CHCl3
demonstrates that different THMs can induce adverse effects via different mechanisms, indicating that risk evaluations of THMs should not treat members of this class as if they shared a common mode of action.
...
PMID:Glutathione S-transferase-mediated mutagenicity of trihalomethanes in Salmonella typhimurium: contrasting results with bromodichloromethane off chloroform. 916 83
F344 rats were exposed to drinking water mixtures of seven of the most common groundwater contaminants associated with hazardous waste sites [arsenic, benzene,
chloroform
, chromium, lead, phenol, and trichloroethylene (TCE)] as the full mixture or submixtures of the organic and/or inorganic chemicals. The lowest concentrations (1x) of the individual chemicals were environmentally realistic and below what would be expected to induce significant short-term toxicity. This study was intended to determine if previously reported increases in localized hepatocellular proliferation in response to these chemicals might be correlated with increased risk for hepatocarcinogenesis. Rats were exposed via a drinking water solution to the full seven- chemical mixture (at 1x and 10x concentrations), submixtures of the organic or inorganic chemicals (at 10x concentrations), a mixture of TCE, lead, and
chloroform
(TLC submixture at 10x and 100x concentrations), or deionized water as a control. The rats were evaluated for promotion of placental glutathione-S-transferase (
GST
-P) positive preneoplastic liver cell foci after diethylnitrosamine (DEN) initiation and partial hepatectomy. Focus formation, cell proliferation, and apoptosis were evaluated after exposure to DEN or saline controls, the chemical mixtures or deionized water controls, or combinations of these treatments. The total number and area of
GST
-P positive foci in DEN-treated rats exposed to the full seven-chemical mixture was increased as compared with the DEN-water controls, but this was statistically significant only for total focus area in the 1x dose group. In DEN-treated rats, the inorganic or TLC submixtures resulted in a significant reduction in number and area of
GST
-P positive foci. Focus area also was decreased in the organic submixture-treated group, but not significantly. Hepatocellular proliferation was not significantly changed in the chemical mixture saline groups as compared with the mixture water controls. After DEN treatment, however, cell proliferation was significantly decreased after the 10x seven-chemical and organic mixture treatments and the 100x TLC mixture treatment. Different groups showed either increased or decreased apoptotic rates which did not correlate well with proliferation rates or focus formation. Mixtures of these seven chemicals, therefore, did not appear to act as promoters of hepatic foci at environmentally relevant concentrations, and some mixture combinations appeared to decrease promotional activity.
...
PMID:Lack of promotional effects of groundwater contaminant mixtures on the induction of preneoplastic foci in rat liver. 1052 94
The aim of this study was to determine the chronic toxicity of a mixture of chlorinated alkanes and alkenes (CA) consisting of
chloroform
, 1,1-dichloroethane, 1,1-dichloroethylene, 1,1,1-trichloroethane, trichloroethylene, and tetrachloroethylene. These chlorinated organic solvents were present in the underground water near an electronic appliances manufactory in Taoyuan, Taiwan. Male and female weanling ICR mice were treated with low-, medium-, and high-dose CA mixtures in drinking water for 16 and 18 mo, respectively. A significant number of male mice treated with the high-dose CA mixture developed tail alopecia and deformation, which was not prominent in CA-treated female mice. Medium- and high-dose CA mixtures induced marginal increases of liver and lung weights, blood urea nitrogen, and serum creatinine levels in male mice. In female mice, the high-dose CA mixture increased liver, kidney, and uterus and ovary total weights, without affecting serum biochemistry parameters. CA mixtures had no effects on the total glutathione content or the level of
glutathione S-transferase
activity in the livers and kid- neys of male and female mice. Treatments with CA mixtures produced a trend of increasing frequency of hepatocelluar neoplasms in male mice, compared to male and female controls and CA-treated female mice. The high-dose CA mixture induced a significantly higher incidence of mammary adenocarcinoma in female mice. The calculated odds ratios of mammary adenocarcinoma in female mice induced by low-, medium-, and high-dose CA mixtures were 1.14, 1.37, and 3.53 times that of the controls, respectively. The low-dose CA mixture induced a higher incidence of cysts and inflammation in and around the ovaries. This study has demonstrated that the CA mixture is a potential carcinogen to male and female mice. These animal toxicology data may be important in assessing the health effects of individuals exposed to the CA mixture.
...
PMID:Chronic toxicity of a mixture of chlorinated alkanes and alkenes in ICR mice. 1191 91
This study evaluates the influence of genetic polymorphism at GSTM1, GSTM3 and GSTT1 gene loci on oral cancer risk among Indians habituated to the use of, smokeless tobacco, bidi or cigarette. DNA extracted from white blood cells of 297 cancer patients and 450 healthy controls by the proteinase K phenol-
chloroform
extraction procedure were analyzed by the polymerase chain reaction (PCR) and PCR-restriction fragment length polymorphism (RFLP) analyses. Lifetime tobacco exposure was evaluated as a risk factor in relation to the polymorphism at the
GST
gene loci using logistic regression analysis. There was no significant difference in the distribution of the GSTM3 and GSTT1 genotypes between oral cancer patients and controls. In contrast, a significant 3-fold increase in risk was seen for patients with the GSTM1 null genotype (age adjusted OR = 3.2, 95% CI 2.4-4.3). The impact of the GSTM1 null genotype on oral cancer risk was also analyzed in separate groups of individuals with different tobacco habits. The odds ratio associated with the GSTM1 null genotype was 3.7 (95% CI 2.0-7.1) in tobacco chewers, 3.7 (5% CI 1.3-7.9) in bidi smokers and 5.7 (95% CI 2.0-16.3) in cigarette smokers. Furthermore, increased lifetime exposure to chewing tobacco appeared to be associated with a 2-fold increase in oral cancer risk in GSTM1 null individuals. The results suggest that the GSTM1 null genotype is a risk factor for development of oral cancer among Indian tobacco habitues.
...
PMID:Polymorphism at GSTM1, GSTM3 and GSTT1 gene loci and susceptibility to oral cancer in an Indian population. 1201 53
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