Gene/Protein Disease Symptom Drug Enzyme Compound
Pivot Concepts:   Target Concepts:
Query: EC:2.4.2.8 (hypoxanthine-guanine phosphoribosyltransferase)
 2,527 document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)

When 7,12-dimethylbenz[a]anthracene (DMBA) and aflatoxin B1 (AFB1) were activated by hepatocytes from Fischer 344 rats fed a diet containing 2% butylated hydroxyanisole (BHA), frequencies of mutation to 6-thioguanine resistance (TGR) at the HGPRTase gene locus and to ouabain resistance (OuR) at the Na+,K(+)-ATPase gene locus in V79 cells were 30-70% less than those obtained with hepatocytes from untreated controls. A difference in the mutation frequency did not occur when dimethylnitrosamine (DMN) was activated by BHA induced- rather than control-hepatocytes. Analysis of hepatocytes from rats fed 2% BHA showed a small (1.5-fold), but significant, increase in glutathione levels over that in the controls but no change in activity of cytochrome P450. Cytosolic glutathione S-transferase (GST) activity was increased 2-3-fold in hepatocytes from rats fed the 2% BHA diet. These results suggest that mutagenic response to DMBA and AFB1 is reduced, at least in part, because of BHA-induction of hepatocyte GST activity; while activation of DMN can occur by pathway(s) unaffected by BHA-induction of these liver enzymes. In contrast to mutation frequencies, significant differences between BHA- and control-activation in the production of sister-chromatid exchange (SCE) and micronucleus formation (MN) were not detected with any of the genotoxins. It was concluded that the mechanism(s) by which SCE and MN occur are likely unrelated to the capacity of BHA to induced activity of hepatic enzymes, e.g. the GSH S-transferases, that directly or indirectly affect mutation end-points.
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PMID:Comparative genotoxicity of 3 procarcinogens in V79 cells as related to glutathione S-transferase activity of hepatocytes from untreated rats and those fed 2% butylated hydroxyanisole. 216 83

The Shope fibroma virus (SFV) DNA ligase gene has been cloned and sequenced, and the biochemical requirements of the gene product have been determined in vitro. The SFV ligase gene maps to the BamHI L1/L2 boundary and spans 1.7 kb. The gene is predicted to encode a 559-amino-acid protein of M(r) = 63,139 which shares 45% amino acid identity with Orthopoxvirus ligases. The C-terminal two-thirds of the protein appears to encode the catalytic domain and shares distant homology with many ligases. The N-terminal homology is shared between only Orthopoxviruses and Leporipoxviruses and suggests that DNA ligases may be composite structures consisting of two independently evolved protein domains. Although the the gene encodes features characteristic of both early and late poxviral genes, Northern analysis showed that SFV ligase is expressed as a late gene product. In order to prove the identity of the protein it was expressed as a glutathione S-transferase fusion in Escherichia coli, affinity purified, and shown to be a Mg2+.ATP-dependent ligase in vitro. The recombinant protein can also form a covalent ligase.AMP complex characteristic of ATP-dependent DNA ligases. The SFV ligase gene can be disrupted and is thus not essential for viral growth in culture. This was shown by recombining a PCR product, encoding a P7.5 promoter and E. coli guanine phosphoribosyltransferase gene (gpt) into the open reading frame, and selecting for gpt+ viruses. This work provides insights into the evolution of Orthopoxviruses and Leporipoxviruses and strains suitable for a detailed analysis of the role DNA ligases play in poxviral recombination.
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PMID:Characterization of the Shope fibroma virus DNA ligase gene. 803 Feb 29

Although methylene chloride (MC) is readily detectable as a bacterial mutagen, published studies in mammalian cells have been inconclusive. We have previously shown (Graves et al., 1995) that glutathione S-transferase (GST)-mediated metabolism of MC by mouse liver cytosol (S100 fraction) causes DNA single-strand (ss) breaks in CHO cells. In this study, MC GST metabolites were shown to cause mutations at the HPRT locus of CHO cells. The mutagenicity of MC was enhanced by exposing the cells in suspension rather than as attached cultures. The MC GST metabolite formaldehyde was mutagenic in independent experiments, although the number of mutants induced was lower than with the MC. CHO HPRT mutations were also induced by the reference genotoxin 1,2-dibromoethane (1,2-DBE), which is activated to a mutagen by GST-mediated metabolism. Assay of DNA ss breaks and DNA-protein cross-links at mutagenic concentrations of MC, formaldehyde or 1,2-DBE, showed that all three compounds induced DNA ss breaks, but only formaldehyde induced significant DNA-protein cross-linking. These results suggest that whilst formaldehyde may play a role in MC mutagenesis, its weak mutagenicity and the absence of significant DNA-protein cross-linking after MC exposure, leads to the conclusion that the MC DNA damage and resulting mutations are induced by the glutathione conjugate of MC, S-chloromethylglutathione.
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PMID:Mouse liver glutathione S-transferase mediated metabolism of methylene chloride to a mutagen in the CHO/HPRT assay. 860 Mar 70

International scientific publications on the influence of metabolic genotypes on biological indicators of genotoxic risk in environmental or occupational exposure are reviewed. Biomarkers of exposure (substance or its metabolites in biological fluids, urinary mutagenicity, protein and DNA adducts) and of effects (chromosome aberrations (CAs), sister chromatid exchanges (SCEs), micronuclei (Mn), COMET assay, HPRT mutants) have been evaluated according to different genotypes (or phenotypes) of several activating/detoxifying metabolic activities. In less than half the studies (43 out of 95), the influence of genotype on the examined biological indicator was found, of which four report poorly reliable results (i.e., with scarce biological plausibility, because of the inconsistency of modulated effect with the type of enzymatic activity expressed). As regards urinary metabolites, the excretion of mercapturic acids (MA) is greater in subjects with high GST activity, that of 1-pyrenol and other PAH metabolites turns out to be significantly influenced by genotypes CYP1A1 or GSTM1 null, and that of exposure indicators to aromatic amines (AA) (acetylated and non-acetylated metabolites) is modulated by NAT2. In benzene exposure, preliminary results suggest an increase in urinary t, t-muconic acid (t,t-MA) in subjects with some genotypes. On urinary mutagenicity of PAH-exposed subjects, the effects of genotype GSTM1 null, alone or combined with NAT2 slow are reported. When DNA adduct levels are clearly increased in PAH-exposed group (18 out of 22), 7 out of 18 studies report the influence of GSTM1 null on this biomarker, and of the five studies which also examined genotype CYP1A1, four report the influence of genotype CYP1A1, alone or in combination with GSTM1 null. A total of 25 out of 41 publications (61%) evaluating the influence of metabolic polymorphisms on biomarkers of effect (cytogenetic markers, COMET assay, HPRT mutants) do not record any increase in the indicator due to exposure to the genotoxic agents studied, confirming the scarce sensitivity of these indicators (mainly HPRT mutants, Mn, COMET assay) for assessing environmental or occupational exposure to genotoxic substances. Concluding, in determining urinary metabolites for monitoring exposure to genotoxic substances, there is sufficient evidence that genetically-based metabolic polymorphisms must be taken into account in the future. The unfavourable association for the activating/detoxifying metabolism of PAH is also confirmed as a risk factor due to the formation of PAH-DNA adducts. The clearly protective role played by GSTT1 on DEB (and/or related compound)-induced sister chromatid exchanges (SCEs) should be noted. The modulating effects of genotypes on protein adduct levels in environmental and occupational exposure have not yet been documented, and most studies on the influence of genotype on biological indicators of early genotoxic effects report negative results.
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PMID:Biological indicators of genotoxic risk and metabolic polymorphisms. 1101 45

This paper reviews studies published in the international scientific literature evaluating the influence of genetically based metabolic polymorphisms on biological indicators of genotoxic risk in environmental or occupational exposure. Exposures due to life style (i.e. diet or smoking) were not considered. Indicators are subdivided into internal dose indicators (concentration of the substance or its metabolites in biological fluids, urinary mutagenicity, adducts of hemoglobin, plasma proteins and DNA), and early biological effects (chromosome aberrations, sister chromatid exchanges, micronuclei, COMET assay, HPRT mutants). The metabolic genotypes (or phenotypes) examined by various authors are: ALDH2 (aldehyde dehydrogenase), CYP (P450 cytochrome) 1AI, CYP1A2, CYP2E1, CYP2D6, EPHX (epoxidohydrolase), NAT2 (N-acetyl transferase), NQO1 (NAD(P)H: kinone oxidoreductase), PON1 (paraoxonase), GST (glutathione S-transferase) M1, GSTT1 and GSTP1. In more than half the studies (52 out of 96), no influence of genotype was found in the biological indicator. This may be due either to the poor sensitivity of the indicator used, or to low exposure. In studies examining the effect of genotype on the indicator, the biological plausibility of the result was evaluated, i.e., whether the effect is consistent with the type of enzymatic activity expressed. Four studies reported not very reliable results and suggest either the unfavourable influence of genotype GSTM1 with high detoxifying activity, or enzymatic activity poorly involved in the metabolism of the xenobiotics in question (NAT2 in the case of PAH). As regards urinary metabolites of genotoxic agents, eight studies reported the modulating effect of genotype. The urinary excretion of mercapturic acids was greater in subjects with high GST activity. In exposure to PAH, urinary 1-pyrenol and PAH metabolites turn out to be significantly influenced by genotypes CYP1A1 or GSTM1 null; in exposure to aromatic amines, the influence of NAT2 on exposure indicators (levels of acetylated and non-acetylated metabolites) was confirmed. Exposure to benzene led to an increase in t-t-MA in some genotypes, although experimental verification is still necessary. As regards urinary mutagenicity, the effect of genotype GSTM1 null is reported, and of the same genotype combined with NAT2 slow, in non-smoking individuals subjected to high exposure to PAH and in cigarette-smoking/coke-oven workers. Lastly, the determination of urinary metabolites in monitoring exposure to genotoxic substances, provides sufficient evidence that genetically based metabolic polymorphisms must be taken into account in the future. There is still little evidence regarding the importance of genotype on the level of protein adducts in environmental and occupational exposure. A relatively large number of publications (22) dealt with DNA adduct levels in PAH exposure. In 18 studies, the biological indicator clearly increases with respect to values in control subjects. Of these studies, seven reported the influence of GSTM1 null on DNA adducts and, of the five studies which also examined genotype CYP1A1, four reported the influence on DNA adduct level of genotype CYP1A1, alone or in combination with GSTM1 null. It therefore seems as if the unfavourable association for the activating/detoxifying metabolism of PAH is a risk factor for the formation of PAH-DNA adducts. Most publications (25 out of 41; 61%) dealing with metabolic polymorphisms in effect indicators (cytogenetic markers, COMET assay, HPRT mutants) did not report any increase in the indicator due to exposure to the genotoxic agents studied. These indicators of genotoxic damage, including mainly the frequency of HPRT mutants (100%), Mn (90%) and the COMET assay (67%), are not sufficiently sensitive in revealing exposure, confirming that they are not particularly suitable for measuring exposure to genotoxic substances in occupational or environmental exposures. It is therefore difficult to assess the influence of metabolic genotypes by means of this type of biological indicator. The few positive results reported for SCE in occupational studies mentioned the influence of genotype ALDH2, either alone or in combination with genotype CYP2E1 in exposure to CVM, or in combination with GSTM1 null in exposure to epichlorohydrin. For CA the results showed unfavourable combinations of genotypes CYP2E1, GSTM1 and PON1 in exposure to pesticides, and GSTM1 null in combination with NAT2 slow in exposure to urban air. All the remaining studies on the effect of genotype on biological indicators of cytogenetic damage reported negative results.
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PMID:[Biomarkers of gentotoxic risk and metabolic polymorphism]. 1118 84

The overall objective of this study was to evaluate a continuum of biomarkers in blood and urine for their sensitivities as indicators of low level occupational exposures to 1,3 butadiene (BD). The study design was largely cross-sectional, with biological samples collected within a short timeframe. Personal 8-h BD exposure measures were made on several occasions over a 60-day period for each potentially exposed worker in order provide maximum accuracy for this independent variable and to accommodate the different expression intervals of the several biomarkers. Co-exposures to styrene, toluene and benzene were also measured. The study included 24 BD monomer production workers (mean BD exposure=0.642 mg/m(3)), 34 polymerization workers (mean BD exposure=1.794 mg/m(3)) and 25 controls (mean BD exposure=0.023 mg/m(3)). The several biomarkers were measured by a consortium of investigators at different locations in the US and Europe. These biomarkers included: (1) metabolic genotypes (CYP2E1, EH, GST M1, GST T1, ADH2, ADH3), determined in Prague and Burlington, VT; (2) urinary M1 and M2 metabolites (1,2-dihydroxy-4-[N-acetylcysteinyl]-butane and 1-hydroxy-2-[N-acetylcysteinyl]-3-butene, respectively), determined in Albuquerque, NM and Leiden; (3) hemoglobin adducts (N-[2-dihydroxy-3-butenyl]valine=HBVal and N-[2,3,4-trihydroxybutyl]valine=THBVal), determined in Amsterdam and Chapel Hill, NC, respectively; (4) HPRT mutations determined by autoradiographic assay in Galveston, TX, with slides re-read in Burlington, VT; (6) hypoxanthine-guanine phosphoribosyltransferase (HPRT) mutations determined by cloning assay in Leiden with mutational spectra characterized in Burlington, VT; (7) sister chromatid exchanges and chromosome aberrations determined by standard methods and FISH analysis in Prague. Urinary M1 and M2 metabolites and HBVal and THBVal hemoglobin adducts were all significantly correlated with BD exposure levels, with adducts being the most highly associated. No significant relationships were observed between BD exposures and HPRT mutations or any of the cytogenetic endpoints, regardless of method of assay.
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PMID:Biomarkers for assessing occupational exposures to 1,3-butadiene. 1139 5

In the human glutathione S-transferase (GST) mu gene family, homozygous deletion of GSTM1 is the null phenotype (frequency of approximately 50% in Caucasians). In the current study, GSTM1 status was determined in human cell lines using reverse transcriptase, polymerase chain reaction, and immunochemistry. Cell lines were challenged with a range of doses of styrene-7,8-oxide (SO) and then toxicity and genotoxicity were monitored. Toxicity was determined by growth in flasks and genotoxicity by cloning in microplates in the presence/absence of 6-thioguanine, to detect mutations at the hypoxanthine phosphoribosyltransferase (hprt) locus. A SO concentration-dependent decrease in survival was observed for all cell lines, with GSTM1-deficient lines being more sensitive. The IC(50)s of deficient and proficient cell lines were 0.45 and 0.55 mM SO, respectively. The difference between survival of GSTM1-deficient and -proficient cell lines approached statistical significance. The background mutation frequency of GSTM1-deficient cell lines was 2 x 10(-5), and that of GSTM1-proficient cell lines was 3 x 10(-6). GSTM1-deficient cell lines were significantly more sensitive than GSTM1-proficient cell lines to mutation induction for concentrations up to 2.5 mM SO (P < 0.001, regression analysis). These results suggest that cell lines containing metabolically competent GSTM1 are able to efficiently use GSTM1 to conjugate SO and reduce its hazard. This supports the epidemiological evidence that GSTM1 influences sensitivity to chemical carcinogenesis and subsequent risk of cancer induction.
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PMID:Role of glutathione S-transferase mu (GSTM1) in styrene-7,8-oxide toxicity and mutagenicity. 1142 77

We evaluated our data on the occupational exposure to styrene in lamination workers. The battery of parameters included markers of external and internal exposure and biomarkers of biological effects and susceptibility. DNA repair capacities have been determined in both exposed and control groups. Styrene workplace concentration significantly correlated with styrene concentration in blood, exhaled air and urinary mandelic acid. Haemoglobin and O(6)-styrene oxide (SO)-guanine DNA adducts were significantly higher in exposed subjects as compared to controls and correlated with exposure parameters. In styrene-exposed workers 1-SO-adenine DNA adducts were detected (2.6 per 10(9) dNp), while in controls these adducts were below the detection limit. 1-SO-adenine adduct levels were affected by both acute and cumulative exposure (P=0.001, F=86.0 and P=0.017, F=59.0, respectively) and associated with cytochrome P450 2E1 (CYP2E1) polymorphisms (R(2)=0.442). Mutant frequencies (MF) at the hypoxanthine-guanine phosphoribosyltransferase (HPRT) locus appeared to accumulate with exposure over time and were associated with glutathione S-transferase P1 (GSTP1) polymorphism. DNA repair capacity increased with the exposure, except for the group exposed to the highest styrene concentration. In this particular group, increased DNA repair capacity to remove oxidative DNA damage was found.
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PMID:The role of various biomarkers in the evaluation of styrene genotoxicity. 1289 75

1,3-Butadiene (BD) is an important industrial chemical and pollutant. Its ability to induce genetic damage and cause hematological malignancies in humans is controversial. We have examined chromosome damage by fluorescence in situ hybridization (FISH) and mutations in the HPRT gene in the blood of Chinese workers exposed to BD. Peripheral blood samples were collected and cultured from 39 workers exposed to BD (median level 2 ppm, 6 h time-weighted average) and 38 matched controls in Yanshan, China. No difference in the level of aneuploidy or structural changes in chromosomes 1, 7, 8, and 12 was detected in metaphase cells from exposed subjects in comparison with matched controls, nor was there an increase in the frequency of HPRT mutations in the BD-exposed workers. Because genetic polymorphisms in glutathione S-transferase (GST) enzymes and microsomal epoxide hydrolase (EPHX1) may affect the genotoxic effects of BD and its metabolites, we also related chromosome alterations and gene mutations to GSTT1, GSTM1 and EPHX1 genotypes. Overall, there was no effect of variants in these genotypes on numerical or structural changes in chromosomes 1, 7, 8 and 12 or on HPRT mutant frequency in relation to BD exposure, but the GST genotypes did influence background levels of both hyperdiploidy and HPRT mutant frequency. In conclusion, our data show no increase in chromosomal aberrations or HPRT mutations among workers exposed to BD, even in potentially susceptible genetic subgroups. The study is, however, quite small and the levels of BD exposure are not extremely high, but our findings in China do support those from a similar study conducted in the Czech Republic. Together, these studies suggest that low levels of occupational BD exposure do not pose a significant risk of genetic damage.
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PMID:Lack of increased genetic damage in 1,3-butadiene-exposed Chinese workers studied in relation to EPHX1 and GST genotypes. 1503 20

In order to cast light on carcinogen-specific molecular mechanisms underlying experimental hepatocarcinogenesis in rats, in vivo mutagenicity and mutation spectra of known genotoxic rat hepatocarcinogens N-nitrosopyrrolidine (NPYR), and 2-amino-3-methylimidazo[4,5-f]quinoline (IQ), as well as the nongenotoxic hepatocarcinogen di(2-ethylhexyl)phthalate (DEHP) and the noncarcinogen acetaminophen (AAP), were investigated in guanine phosphoribosyltransferase (gpt) delta transgenic rats, a recently developed animal model for genotoxicity analysis. After 13-wk treatment, glutathione S-transferase placental form (GST-P)-positive liver cell foci were significantly increased in NPYR-treated and IQ-treated rats. In the DEHP-treated rats, marked hepatomegaly with centrilobular hypertrophy of hepatocytes occurred, although GST-P staining was consistently negative. Positive mutagenicity was detected in IQ- and NPYR-treated rats. Mutant frequencies (MFs) in the liver DNA were 188.0 x 10(-6) and 56.5 x 10(-6), approximately 35-fold and 10-fold higher, respectively, than that of nontreatment control rats (5.5 x 10(-6)). There were no increases in MFs in the DEHP- or AAP-treated rats as compared to the nontreatment control value. IQ induced mainly base substitutions leading to G:C to T:A transversions (56.9%) and deletions of G:C base pairs. In contrast, NPYR primarily caused specific A:T to G:C transitions (49.3%), which are very rare in the other groups. These data provided support for the conclusion that IQ and NPYR hepatocarcinogenesis depends on genotoxic processes and specific DNA adduct formation while DEHP exerts its influence via a nongenotoxic promotional pathway. Our data also indicate that analysis of specific in vivo mutational responses with transgenic animal models can provide crucial information for understanding the molecular mechanisms underlying chemical carcinogenesis.
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PMID:In vivo mutational analysis of liver DNA in gpt delta transgenic rats treated with the hepatocarcinogens N-nitrosopyrrolidine, 2-amino-3-methylimidazo[4,5-f]quinoline, and di(2-ethylhexyl)phthalate. 1548 47


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