Gene/Protein Disease Symptom Drug Enzyme Compound
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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)

Dihalomethanes are metabolized to carbon monoxide both in vivo and in vitro. The reaction is catalyzed by a hepatic microsomal cytochrome P-450 dependent mixed function oxidase system. Bioorganic mechanism studies suggest an initial oxygen insertion reaction followed by rearrangement to a formyl halide intermediate which in turn decomposes to yield carbon monoxide. In vitro studies show that 14C-dichloromethane becomes covalently bound to both microsomal protein and lipid. The similar characteristics of metabolism to carbon monoxide and covalent binding suggests that a common intermediate, perhaps the formyl halide, may be involved. Dihalomethanes are also metabolized to formaldehyde, formic acid, and inorganic halide. A glutathione transferase, located in hepatic cytosol fractions, appears to be involved. Reaction mechanism studies suggest that a S-hydroxymethyl glutathione intermediate may yield formaldehyde or be diverted via formaldehyde dehydrogenase/S-formyl glutathione hydrolase to yield formic acid. Haloforms are also metabolized in vitro to carbon monoxide by a hepatic microsomal cytochrome P-450 dependent mixed function oxidase system. This reaction is a markedly stimulated by sulfhydryl compounds.
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PMID:Metabolism of halogenated methanes and macromolecular binding. 9 15

Dichloromethane (DCM) is metabolized via a glutathione transferase (GST)-dependent pathway to formaldehyde (HCHO), a mutagenic compound that could play an important role in the carcinogenic effects of DCM observed in the liver and lungs of B6C3F1 mice at 2000 and 4000 ppm. Syrian hamsters metabolize DCM more slowly than mice via this pathway, and hamsters exposed to 3500 ppm showed no apparent carcinogenic response. The possible formation of DNA-protein cross-links (DPX) from DCM in both species was examined. Male mice and hamsters were pre-exposed for 2 days (6 hr/day) to 4000 ppm of DCM and on the third day were exposed (6 hr) to a decaying concentration (4500 to 2500 ppm) of [14C]DCM. DPX were detected in mouse liver, but not in mouse lung, hamster liver, or hamster lung. The failure to detect DPX in mouse lung does not exclude their possible formation in a subpopulation of lung cells. Metabolic incorporation of 14C derived from [14C]DCM into DNA suggested a higher rate of turnover of some mouse lung cells than of hamster lung cells, but no large difference in the turnover rates of liver cells in the two species under these conditions. These results demonstrate that HCHO derived from DCM can form DNA-protein cross-links in the liver of the B6C3F1 mouse. The formation of DPX is dependent on the activity of the GST pathway, and species such as hamsters and humans having much lower rates of DCM metabolism via this pathway may not generate toxicologically significant concentrations of HCHO and DPX.
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PMID:Dichloromethane (methylene chloride): metabolism to formaldehyde and formation of DNA-protein cross-links in B6C3F1 mice and Syrian golden hamsters. 158 69

For 25 mutagens in Drosophila the ratio was determined between the induction of sex-linked recessive lethals (SLRL) and the induction of ring-X loss in male adults. For small monofunctional alkylating agents this ratio increases with decreasing s-value from 1.8 for methyl methanesulfonate (MMS) to 27 for ethylnitrosourea (ENU). For multifunctional cross-linking agents, however, the ratio varies within relatively narrow limits, ranging from 0.15 for cisplatin to 0.07 for tris-(1-aziridinyl)phosphineoxide (TEPA), while for most agents the ratio is around 0.12. The number of reactive groups seems to be of minor importance for compounds with more than one functionality as bi- and tri-functional agents show similar ratios. The systemic difference in the ratios between mono- and multi-functional agents suggests that different mechanisms are involved in the induction of SLRLs and ring-X loss. For ethyleneimine (EI) and ethyleneoxide (EO) low ratios of 0.32 and 0.60 respectively were observed which do not correlate with their s-values. An alternative chromosome-breaking mechanism may be responsible for this deviation, possibly alkylation of the phosphate backbone of DNA, followed by an intramolecular displacement of one of the deoxyribose groups by the beta-amino or the beta-hydroxy group. It is felt that the considerable difference between the ratios for monofunctional and multifunctional agents may be of prognostic value and can be used to obtain information on the mechanisms of mutagens with 'unknown' action, provided that structural features are taken into account. Hexamethylphosphoramide (HMPA), hexamethylmelamine (HEMEL), tetramethylurea (TMU) and dimethylpropyleneurea (DMPU) all show SLRL: ring-X loss ratios that match those of multifunctional agents, 0.08, 0.12, 0.08, and 0.16, respectively. The ratios for the pyrrolizidine alkaloids monocrotalin and seniciphilline, 0.053 and 0.24 respectively, also correspond with this group of mutagens. The low ratios for formaldehyde, 2-chloro-acetaldehyde and 2-chloroethyl methanesulfonate, 0.30, 0.052 and 0.36 respectively, are indicative that cross-linking may attribute considerably to their mutagenic action in Drosophila. On the other hand, not all mutagens containing 2 reactive groups act as cross-linking agents. The ratio for 1,2-dibromoethane, 2.7, indicates that it may act as a monofunctional agent. This is in accordance with the proposed activation mechanism by glutathione S-transferase, producing a monofunctional half-mustard derivative (Rannug, 1980; van Bladeren et al., 1981).
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PMID:The ratio of induced recessive lethals to ring-X loss has prognostic value in terms of functionality of chemical mutagens in Drosophila melanogaster. 245 28

N-nitrodimethylamine is metabolized oxidatively to N-nitrohydroxymethylmethylamine, which decomposes to yield formaldehyde and N-nitromethylamine. All four compounds and N-nitromethylamine were tested for their ability to induce DNA single strand breaks in hepatocytes and in SV 40-transformed Chinese hamster embryo cell lines. Only the two monoalkylnitramines were positive. They induced single strand breaks in hepatocytes, but were not effective in the other cells. Formaldehyde and N-nitrohydroxymethylmethylamine were toxic to the cells. None of the compounds tested was able to induce selective DNA amplification in the two transformed cell lines. Enzymes involved in drug metabolism were assayed in the hamster cell lines. The activity of UDP-glucuronosyltransferase and cytosolic epoxide hydrolase were not detectable. N-nitrodimethylamine demethylation was low. The content of reduced glutathione and the activities of glutathione transferase and membrane bound epoxide hydrolase were comparable to values obtained in the rat liver.
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PMID:Determination of DNA single strand breaks and selective DNA amplification by N-nitrodimethylamine and analogs, and estimation of the indicator cells' metabolic capacities. 300 87

The biochemical effects of methyl chloride were investigated in tissues of F-344 rats and B6C3F1 mice (both sexes). Activities of GST were 2-3 times higher in livers of male B6C3F1 mice, compared with those of female mice, and with rats of both sexes. In kidneys GST activities of (male) mice were about 7 times lower than those found in livers. The activity of FDH was higher in livers of mice (both sexes) than in those of rats. No obvious sex difference was found in livers of rats and mice with respect to FDH. In kidneys, however, (minor) differences in FDH activities occurred between male and female B6C3F1 mice (4.7 vs. 3.1 nmol/min per mg). Sex differences of FDH activity in kidneys were not observed in F-344 rats. The microsomal transformation (by cytochrome P-450) of methyl chloride and S-methyl-L-cysteine to formaldehyde in tissues of B6C3F1 mice occurred preferentially in the liver. More formaldehyde was produced in liver microsomes of male, compared to those of female mice. Kidney microsomes metabolized methyl chloride to formaldehyde much less than liver microsomes. After a single exposure of mice of both sexes to 1000 ppm methyl chloride no elevation in formaldehyde concentrations was observed in livers and kidneys ex vivo. The determination of DNA lesions, using the alkaline elution technique, revealed no DNA-protein crosslinks in kidneys of male B6C3F1 mice after exposure to methyl chloride (1000 ppm, 6 h day-1, 4 days) and gave only minor evidence of single-strand breaks. Lipid peroxidation (production of TBA reactive material), induced by single exposure to methyl chloride (1000 ppm, 6 h), was very pronounced in livers of male and female mice. Smaller increases in peroxidation were observed in the kidneys of exposed mice. The theory that renal tumors observed in male mice after chronic exposure of the test animals to high (1000 ppm) concentrations of methyl chloride, are evoked by intermediates and in situ produced formaldehyde is proven unlikely by our results.
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PMID:Biochemical effects of methyl chloride in relation to its tumorigenicity. 335 Aug 44

The irritating aldehyde acrolein was injected intraperitoneally into mice. A single injection at 4 mg/kg gave rise to a 5-fold increase in plasma total lactate dehydrogenase (LDH) activity, with the peak after approximately 10 h. The pattern of LDH isoenzymes was not altered. Repeated injections (daily or weekly) caused a progressively less pronounced effect on the LDH activity. Experiments with formaldehyde and crotonaldehyde gave essentially the same results. The LD50 for acrolein i.p. in mice was increased from a level of 7 mg/kg to a level of 12 mg/kg by pretreatment with sublethal doses of 4 mg/kg/day for 5 days. Thus, the response to repeated acrolein injections, in terms of LDH and LD50, indicates an acquired tolerance against the irritant. Likewise, pretreatment with formaldehyde or crotonaldehyde could induce tolerance, in terms of LDH activity, towards a subsequent injection of acrolein. Histopathological examination revealed that spleen, adrenals and thymus were affected. The thymus markedly decreased in size after repeated injections of acrolein, crotonaldehyde or formaldehyde. Adrenalectomized mice given acrolein showed no thymus atrophy. A single injection of aldehyde caused an increased level of the adrenal hormone corticosterone in blood plasma. Adrenalectomized mice still showed a certain tolerance, in terms of LDH activity, after repeated injections of acrolein, but the increase in plasma LDH activity was smaller than for normal animals. Treatment with acrolein for six days did not change the level of reduced glutathione or the glutathione S-transferase activity in liver cytosol, but the rate of glutathione synthesis was increased. It is concluded that adrenalectomy does not completely prevent the development of tolerance in mice. It is possible that an increased metabolism can partially explain the acquired tolerance.
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PMID:The acute effects of single and repeated injections of acrolein and other aldehydes. 671 20

Dihalomethanes are metabolized to carbon monoxide (CO) both in vivo and in vitro. The reaction is catalyzed by the hepatic microsomal cytochrome P-450 dependent mixed function oxidase system. Reaction mechanism studies suggest an initial oxygen insertion reaction followed by rearrangement to a formyl halide intermediate, which in turn decomposes to yield CO. In vitro studies show that [14C]dichloromethane becomes covalently bound to both microsomal protein and lipid. The similar characteristics of metabolism to CO and covalent suggest that a common intermediate, perhaps the formyl halide, may be involved. Dihalomethanes are also metabolized for formaldehyde, formic acid, and inorganic halide. A glutathione transferase located in hepatic cytosol fractions appears to be involved. Reaction mechanism studies suggest that a S-hydroxymethyl glutathione intermediate may yield formaldehyde or be diverted via formaldehyde dehydrogenase/S-formyl glutathione hydrolase to yield formic acid. Haloforms are also metabolized to carbon monoxide both in vivo and in vitro by a hepatic microsomal cytochrome P-450 dependent mixed function oxidase system. In vitro, this reaction is markedly stimulated by sulfhydryl compounds. Reaction mechanism studies suggest an initial oxygen insertion reaction followed by rearrangement to a dihalocarbonyl intermediate, which in turn reacts with sulfhydryl reagents to yield a thiol-S-formyl halide. Subsequent attack by other sulfhydryl compounds would result in the formation of CO and a disulfide.
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PMID:Halogenated methanes: metabolism and toxicity. 677 82

Dichloromethane (DCM) is efficiently utilized as a carbon and energy source by aerobic, Gram-negative, facultative methylotrophic bacteria. It also serves as a sole carbon and energy source for a nitrate-respiring Hyphomicrobium sp. and for a strictly anaerobic co-culture of a DCM-fermenting bacterium and an acetogen. The first step of DCM utilization by methylotrophs is catalyzed by DCM dehalogenase which, in a glutathione-dependent substitution reaction, forms inorganic chloride and S-chloromethyl glutathione. This unstable intermediate decomposes to glutathione, inorganic chloride and formaldehyde, a central metabolite of methylotrophic growth. Genetic studies on DCM utilization are beginning to shed some light on questions pertaining to the evolution of DCM dehalogenases and on the regulation of DCM dehalogenase expression. DCM dehalogenase belongs to the glutathione S-transferase supergene family. Analysis of the amino acid sequences of two bacterial DCM dehalogenases reveals 56% identity, and comparison of these sequences to those of glutathione S-transferases indicates a closer relationship to class Theta eukaryotic glutathione S-transferases than to a number of bacterial glutathione S-transferases whose sequences have recently become available. dcmA, the structural gene of the highly substrate-inducible DCM dehalogenase, is carried in most DCM utilizing methylotrophs on large plasmids. In Methylobacterium sp. DM4 its expression is governed by dcmR, a regulatory gene located upstream of dcmA, dcmR encodes a trans-acting factor which negatively controls DCM dehalogenase formation at the transcriptional level. Our working model thus assumes that the dcmR product is a repressor which, in the absence of DCM, binds to the promoter region of dcmA and thereby inhibits initiation of transcription.
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PMID:Microbes, enzymes and genes involved in dichloromethane utilization. 776 35

The individual genotoxic response of cultured human lymphocytes to diepoxybutane (DEB), an epoxide metabolite of 1,3-butadiene, shows a bimodal distribution. Blood donors can be classified as either DEB-sensitive or DEB-resistant on the basis of the frequency of sister chromatid exchanges (SCEs) induced by DEB in whole-blood lymphocyte cultures. The genetic basis of this phenomenon has thusfar been unknown. To investigate if differences in the ability of individuals to detoxify DEB could explain the bimodal response, sister chromatid exchanges (SCEs) induced by a 48-h treatment with DEB (2 and 5 microM) were analyzed in whole-blood lymphocyte cultures of 20 human donors with known genotypes of two polymorphic glutathione S-transferases (GSTs), GSTT1 and GSTM1. Both polymorphisms include a homozygous null genotype lacking the respective GST gene and isozyme. The mean frequency of SCEs/cell was 1.6 times higher among GSTT1 null donors (n = 8) than GSTT1 positive donors (n = 12) at both 2 microM DEB (mean 67.3 versus 40.9) and 5 microM DEB (mean 123.2 versus 77.5), with no overlapping in DEB-induced individual SCE frequencies between the two genotypes. Thus, all DEB-sensitive individuals were of the GSTT1 null genotype, while all DEB-resistant persons had a detectable GSTT1 gene. A significant (P < 0.05) negative correlation (r = -0.65 at 5 microM, r = -0.56 at 2 microM) was obtained in the GSTT1 positive donors between DEB-induced individual SCE frequency and RBC GSTT1 activity, measured by formaldehyde formation from dichloromethane; the GSTT1 null individuals showed no GSTT1 activity. At 5 microM DEB, the lymphocyte cultures of the GSTT1 null donors also had a significantly decreased replication index, indicating an impact of GSTT1 genotype on the cytotoxicity of DEB. No influence on DEB-induced SCEs or cytotoxic effects was observed for GSTM1 genotype. It is concluded that sensitivity to in vitro SCE induction by DEB is explained by the lack of GSTT1.
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PMID:Role of GSTT1 and GSTM1 genotypes in determining individual sensitivity to sister chromatid exchange induction by diepoxybutane in cultured human lymphocytes. 778 40

To get a better insight into the pathophysiology of the nasal changes induced by formaldehyde-ozone mixtures, a 3-day inhalation study was carried out in rats, using intermittent exposure to formaldehyde (3.6 ppm) and ozone (0.4 ppm) alone or in combination and focusing on biochemical and histopathological changes in rat nasal respiratory epithelium. Formaldehyde dehydrogenase, glutathione S-transferase, glutathione reductase, and glucose-6-phosphate dehydrogenase activities in this epithelium were not affected by the individual compounds. However, combined exposure to formaldehyde and ozone resulted in slightly decreased activities of these enzymes. Formaldehyde was found to induce rhinitis, degeneration, frank necrosis, hyperplasia and squamous metaplasia of the ciliated and non-ciliated nasal respiratory epithelium, while ozone induced disarrangement, flattening and slight basal cell hyperplasia of the non-ciliated cuboidal epithelium accompanied by influx of neutrophils. Proliferating cell nuclear antigen (PCNA) expression was elevated not only in nasal areas showing ozone-induced histopathological changes but also in the otherwise normal-appearing epithelium of the nasal septum. No interactive effects were found with respect to proliferative response of the nasal respiratory epithelium after exposure to the formaldehyde-ozone mixture. The present study did not provide evidence of a major role of glutathione and glutathione-dependent enzymes in the pathogenesis of nasal lesions induced by formaldehyde and/or ozone, demonstrated the potential of ozone to affect the mucociliary epithelium lining the nasal septum, and suggested that PCNA expression is a sensitive tool for detection of early effects of respiratory irritants.
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PMID:Biochemical and histopathological changes in nasal epithelium of rats after 3-day intermittent exposure to formaldehyde and ozone alone or in combination. 791 Dec 63


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