Mutagenicity of amino acid and glutathione S-conjugates in the Ames test

Exposure to Cis- and Trans-regioisomers of S-(1,2-dichlorovinyl)-L-cysteine and S-(1,2-dichlorovinyl)-glutathione result in quantitatively and qualitatively different cellular effects in RPTEC/TERT1 cells

Bioactivation of trichloroethylene (TCE) via glutathione conjugation is associated with several adverse effects in the kidney and other extrahepatic tissues. Of the three regioisomeric conjugates formed, S-(1,2-trans-dichlorovinyl)-glutathione (1,2-trans-DCVG), S-(1,2-cis-dichlorovinyl)-glutathione and S-(2,2-dichlorovinyl)-glutathione, only 1,2-trans-DCVG and its corresponding cysteine-conjugate, 1,2-trans-DCVC, have been subject to extensive mechanistic studies. In the present study, the metabolism and cellular effects of 1,2-cis-DCVG, the major regioisomer formed by rat liver fractions, and 1,2-cis-DCVC were investigated for the first time using RPTEC/TERT1-cells as in vitro renal model. In contrast to 1,2-trans-DCVG/C, the cis-regioisomers showed minimal effects on cell viability and mitochondrial respiration. Transcriptomics analysis showed that both 1,2-cis-DCVC and 1,2-trans-DCVC caused Nrf2-mediated antioxidant responses, with 3µM as lowest effective concentration. An ATF4-mediated integrated stress response and p53-mediated responses were observed starting from 30µM for 1,2-trans-DCVC and 125µM for 1,2-cis-DCVC. Comparison of the metabolism of the DCVG regioisomers by LC/MS showed comparable rates of processing to their corresponding DCVC. No detectable N-acetylation was observed in RPTEC/TERT1 cells. Instead, N-glutamylation of DCVC to form N-γ-glutamyl-S-(dichlorovinyl)-L-cysteine was identified as a novel route of metabolism. The results suggest that 1,2-cis-DCVC may be of less toxicological concern for humans than 1,2-trans-DCVC, considering its lower intrinsic toxicity and lower rate of formation by human liver fractions.

Metabolism of Glutathione S-Conjugates: Multiple Pathways

Many potentially toxic electrophilic xenobiotics and some endogenous compounds are detoxified by conversion to the corresponding glutathione S-conjugate, which is metabolized to the N-acetylcysteine S-conjugate (mercapturate) and excreted. Some mercapturate pathway components, however, are toxic. Bioactivation (toxification) may occur when the glutathione S-conjugate (or mercapturate) is converted to a cysteine S-conjugate that undergoes a β-lyase reaction. If the sulfhydryl-containing fragment produced in this reaction is reactive, toxicity may ensue. Some drugs and halogenated workplace/environmental contaminants are bioactivated by this mechanism. On the other hand, cysteine S-conjugate β-lyases occur in nature as a means of generating some biologically useful sulfhydryl-containing compounds.

Impact of Nonalcoholic Fatty Liver Disease on Toxicokinetics of Tetrachloroethylene in Mice

Lifestyle factors and chronic pathologic states are important contributors to interindividual variability in susceptibility to xenobiotic-induced toxicity. Nonalcoholic fatty liver disease (NAFLD) is an increasingly prevalent condition that can dramatically affect chemical metabolism. We examined the effect of NAFLD on toxicokinetics of tetrachloroethylene (PERC), a ubiquitous environmental contaminant that requires metabolic activation to induce adverse health effects. Mice (C57Bl/6J, male) were fed a low-fat diet (LFD), high-fat diet (HFD), or methionine/folate/choline-deficient diet (MCD) to model a healthy liver, steatosis, or nonalcoholic steatohepatitis (NASH), respectively. After 8 weeks, mice were orally administered a single dose of PERC (300 mg/kg) or vehicle (aqueous Alkamuls-EL620) and euthanized at various time points (1-36 hours). Levels of PERC and its metabolites were measured in blood/serum, liver, and fat. Effects of diets on liver gene expression and tissue:air partition coefficients were evaluated. We found that hepatic levels of PERC were 6- and 7.6-fold higher in HFD- and MCD-fed mice compared with LFD-fed mice; this was associated with an increased PERC liver:blood partition coefficient. Liver and serum Cmax for trichloroacetate (TCA) was lower in MCD-fed mice; however, hepatic clearance of TCA was profoundly reduced by HFD or MCD feeding, leading to TCA accumulation. Hepatic mRNA/protein expression and ex vivo activity assays revealed decreased xenobiotic metabolism in HFD- and MCD-, compared with LFD-fed, groups. In conclusion, experimental NAFLD was associated with modulation of xenobiotic disposition and metabolism and increased hepatic exposure to PERC and TCA. Underlying NAFLD may be an important susceptibility factor for PERC-associated hepatotoxicity.

Target Organ Metabolism, Toxicity, and Mechanisms of Trichloroethylene and Perchloroethylene: Key Similarities, Differences, and Data Gaps

Trichloroethylene (TCE) and perchloroethylene or tetrachloroethylene (PCE) are high-production volume chemicals with numerous industrial applications. As a consequence of their widespread use, these chemicals are ubiquitous environmental contaminants to which the general population is commonly exposed. It is widely assumed that TCE and PCE are toxicologically similar; both are simple olefins with three (TCE) or four (PCE) chlorines. Nonetheless, despite decades of research on the adverse health effects of TCE or PCE, few studies have directly compared these two toxicants. Although the metabolic pathways are qualitatively similar, quantitative differences in the flux and yield of metabolites exist. Recent human health assessments have uncovered some overlap in target organs that are affected by exposure to TCE or PCE, and divergent species- and sex-specificity with regard to cancer and noncancer hazards. The objective of this minireview is to highlight key similarities, differences, and data gaps in target organ metabolism and mechanism of toxicity. The main anticipated outcome of this review is to encourage research to 1) directly compare the responses to TCE and PCE using more sensitive biochemical techniques and robust statistical comparisons; 2) more closely examine interindividual variability in the relationship between toxicokinetics and toxicodynamics for TCE and PCE; 3) elucidate the effect of coexposure to these two toxicants; and 4) explore new mechanisms for target organ toxicity associated with TCE and/or PCE exposure.

New structural alerts for Ames mutagenicity discovered using emerging pattern mining techniques

The discovered patterns are used to develop new structural alerts for mutagenicity in the Derek Nexus expert system.

Trichloroethylene biotransformation and its role in mutagenicity, carcinogenicity and target organ toxicity

Metabolism is critical for the mutagenicity, carcinogenicity, and other adverse health effects of trichloroethylene (TCE). Despite the relatively small size and simple chemical structure of TCE, its metabolism is quite complex, yielding multiple intermediates and end-products. Experimental animal and human data indicate that TCE metabolism occurs through two major pathways: cytochrome P450 (CYP)-dependent oxidation and glutathione (GSH) conjugation catalyzed by GSH S-transferases (GSTs). Herein we review recent data characterizing TCE processing and flux through these pathways. We describe the catalytic enzymes, their regulation and tissue localization, as well as the evidence for transport and inter-organ processing of metabolites. We address the chemical reactivity of TCE metabolites, highlighting data on mutagenicity of these end-products. Identification in urine of key metabolites, particularly trichloroacetate (TCA), dichloroacetate (DCA), trichloroethanol and its glucuronide (TCOH and TCOG), and N-acetyl-S-(1,2-dichlorovinyl)-L-cysteine (NAcDCVC), in exposed humans and other species (mostly rats and mice) demonstrates function of the two metabolic pathways in vivo. The CYP pathway primarily yields chemically stable end-products. However, the GST pathway conjugate S-(1,2-dichlorovinyl)glutathione (DCVG) is further processed to multiple highly reactive species that are known to be mutagenic, especially in kidney where in situ metabolism occurs. TCE metabolism is highly variable across sexes, species, tissues and individuals. Genetic polymorphisms in several of the key enzymes metabolizing TCE and its intermediates contribute to variability in metabolic profiles and rates. In all, the evidence characterizing the complex metabolism of TCE can inform predictions of adverse responses including mutagenesis, carcinogenesis, and acute and chronic organ-specific toxicity.

Trichloroethylene: Mechanistic, epidemiologic and other supporting evidence of carcinogenic hazard

The chlorinated solvent trichloroethylene (TCE) is a ubiquitous environmental pollutant. The carcinogenic hazard of TCE was the subject of a 2012 evaluation by a Working Group of the International Agency for Research on Cancer (IARC). Information on exposures, relevant data from epidemiologic studies, bioassays in experimental animals, and toxicity and mechanism of action studies was used to conclude that TCE is carcinogenic to humans (Group 1). This article summarizes the key evidence forming the scientific bases for the IARC classification. Exposure to TCE from environmental sources (including hazardous waste sites and contaminated water) is common throughout the world. While workplace use of TCE has been declining, occupational exposures remain of concern, especially in developing countries. The strongest human evidence is from studies of occupational TCE exposure and kidney cancer. Positive, although less consistent, associations were reported for liver cancer and non-Hodgkin lymphoma. TCE is carcinogenic at multiple sites in multiple species and strains of experimental animals. The mechanistic evidence includes extensive data on the toxicokinetics and genotoxicity of TCE and its metabolites. Together, available evidence provided a cohesive database supporting the human cancer hazard of TCE, particularly in the kidney. For other target sites of carcinogenicity, mechanistic and other data were found to be more limited. Important sources of susceptibility to TCE toxicity and carcinogenicity were also reviewed by the Working Group. In all, consideration of the multiple evidence streams presented herein informed the IARC conclusions regarding the carcinogenicity of TCE.

Genotoxicity of haloalkene and haloalkane glutathione S-conjugates in porcine kidney cells

The genotoxicity of the glutathione S-conjugates S-(12-dichlorovinyl)glutathione (DCVG), S-(1,2,2-trichlorovinyl)glutathione (TCVG), S-(1,2,3,4,4-pentachlorobutadienyl)glutathione (PCBG) and S-(2-chloroethyl)glutathione (CEG) was investigated in LLC-PK1, a cultured line of porcine kidney cells that exhibits many properties of proximal tubular cells. DNA damage caused by treatment of the cells with the S-conjugates was estimated by determining the induction of unscheduled DNA synthesis (UDS) after inhibition of replicative DNA synthesis in confluent LLC-PK1 monolayers. DCVG-, TCVG- and PCBG-induced dose-dependent UDS at concentrations not causing cytotoxicity, as determined by the release of lactate dehydrogenase into the medium. Acivicin, which inhibits irreversibly gamma-glutamyl-transpeptidase (GGT) and aminooxyacetic acid, an inhibitor of cysteine conjugate beta-lyase, blocked DCVG-, TCVG- and PCBG-induced genotoxicity. CEG, however, was genotoxic in subconfluent cells and this was not dependent on GGT and beta-lyase activities. The DNA damaging effects in kidney cells of DCVG, TCVG and PCBG, which are metabolites of the nephrocarcinogens trichloroethylene, tetrachloroethylene and hexachlorobutadiene, respectively, suggest that the parent haloalkenes are potentially genotoxic in the rat kidney, the target organ for both acute toxicity and carcinogenicity.

N-biotinyl-S-(1,2-dichlorovinyl)-L-cysteine sulfoxide as a potential model for S-(1,2-dichlorovinyl)-L-cysteine sulfoxide: characterization of stability and reactivity with glutathione and kidney proteins in vitro

S-(1,2-Dichlorovinyl)-L-cysteine sulfoxide (DCVCS) is a reactive and potent nephrotoxic metabolite of the human trichloroethylene metabolite S-(1,2-dichlorovinyl)-L-cysteine (DCVC). Because DCVCS covalent binding to kidney proteins likely plays a role in its nephrotoxicity, in this study biotin-tagged DCVCS, N-biotinyl-DCVCS (NB-DCVCS), was synthesized, and its stability in buffer alone and in the presence of rat blood or plasma was characterized in vitro. In addition, reactivity toward GSH and covalent binding to selected model enzymes and isolated kidney proteins were characterized. The half-lives of NB-DCVCS (39.6 min) and the DCVCS (diastereomer 1, 14.4 min; diastereomer 2, 6 min) in the presence of GSH were comparable. Incubating the model enzymes glutathione reductase and malate dehydrogenase with 10 μM NB-DCVCS for 3 h at 37 °C followed by immunoblotting using antibiotin antibodies demonstrated that glutathione reductase and malate dehydrogenase were extensively modified by NB-DCVCS. When rat kidney cytosol (6 μg/μL) was incubated with NB-DCVCS (312.5 nM to 5 μM) for 3 h at 37 °C followed by immunoblotting, a concentration-dependent increase in signal with multiple proteins with different molecular weights was observed, suggesting that NB-DCVCS binds to multiple kidney proteins with different selectivity. Incubating rat kidney cytosol with DCVCS (10-100 μM) prior to the addition of NB-DCVCS (2.5 μM) reduced the immunoblotting signal, suggesting that NB-DCVCS and DCVCS compete for the same binding sites. A comparison of the stability of NB-DCVCS and DCVCS in rat blood and plasma was determined in vitro, and NB-DCVCS exhibited higher stability than DCVCS in both media. Collectively, these results suggest that NB-DCVCS shows sufficient stability, reactivity, and selectivity to warrant further investigations into its possible use as a tool for future characterization of the role of covalent modification of renal proteins by DCVCS in nephrotoxicity.

Enzymes Involved in Processing Glutathione Conjugates

Many potentially toxic electrophiles react with glutathione to form glutathione S-conjugates in reactions catalyzed or enhanced by glutathione S-transferases. The glutathione S-conjugate is sequentially converted to the cysteinylglycine-, cysteine- and N-acetyl-cysteine S-conjugate (mercapturate). The mercapturate is generally more polar and water soluble than the parent electrophile and is readily excreted. Excretion of the mercapturate represents a detoxication mechanism. Some endogenous compounds, such as leukotrienes, prostaglandin (PG) A2, 15-deoxy-Δ^12,14-PGJ₂, and hydroxynonenal can also be metabolized to mercapturates and excreted. On occasion, however, formation of glutathione S- and cysteine S-conjugates are bioactivation events as the metabolites are mutagenic and/or cytotoxic. When the cysteine S-conjugate contains a strong electron-withdrawing group attached at the sulfur, it may be converted by cysteine S-conjugate β-lyases to pyruvate, ammonium and the original electrophile modified to contain an –SH group. If this modified electrophile is highly reactive then the enzymes of the mercapturate pathway together with the cysteine S-conjugate β-lyases constitute a bioactivation pathway. Some endogenous halogenated environmental contaminants and drugs are bioactivated by this mechanism. Recent studies suggest that coupling of enzymes of the mercapturate pathway to cysteine S-conjugate β-lyases may be more common in nature and more widespread in the metabolism of electrophilic xenobiotics than previously realized.

Globin monoadducts and cross-links provide evidence for the presence of S-(1,2-dichlorovinyl)-L-cysteine sulfoxide, chlorothioketene, and 2-chlorothionoacetyl chloride in the circulation in rats administered S-(1,2-dichlorovinyl)-L-cysteine

S-(1,2-Dichlorovinyl)-L-cysteine (DCVC), a mutagenic and nephrotoxic metabolite of trichloroethylene, is bioactivated to S-(1,2-dichlorovinyl)-L-cysteine sulfoxide (DCVCS) and chlorothioketene and/or 2-chlorothionoacetyl chloride by cysteine conjugate S-oxidase (S-oxidase) and cysteine conjugate beta-lyase (beta-lyase), respectively. Previously, we identified DCVCS-globin monoadducts and cross-links upon treating rats with DCVCS or incubating erythrocytes with DCVCS. In this study, the formation of DCVC-derived reactive intermediates was investigated after rats were given a single (230 or 460 micromol/kg, i.p.) or multiple (3 or 30 micromol/kg daily for 5 days) DCVC doses. LC/ESI/MS of trypsin-digested globin peptides revealed both S-oxidase and beta-lyase-derived globin monoadducts and cross-links consistent with in vivo DCVC bioactivation by both pathways. MS/MS analyses of trypsin-digested fractions of globin from one of the rats treated with multiple 30 micromol/kg DCVC doses led to identification of beta-lyase-derived monoadducts on both Cys93 and Cys125 of the beta-chains. While rats dosed with the 230 micromol/kg DCVC dose exhibited beta-lyase-dependent monoadducts and cross-links only (four out of four rats), rats given the 460 micromol/kg DCVC dose (two out of four) and rats administered the multiple DCVC doses (two out of four) exhibited both beta-lyase- and S-oxidase-derived monoadducts and cross-links. Because previous incubations of erythrocytes with DCVC did not result in detection of DCVCS-derived monoadducts or cross-links and had only resulted in detection of beta-lyase-derived monoadducts and cross-links, the DCVCS-globin monoadducts and cross-links detected in this study are likely the result of DCVC bioactivation outside the circulation and subsequent translocation of DCVCS and N-acetylated DCVCS into the erythrocytes.

Cysteine conjugate beta-lyase activity of rat erythrocytes and formation of beta-lyase-derived globin monoadducts and cross-links after in vitro exposure of erythrocytes to S-(1,2-dichlorovinyl)-L-cysteine

S-(1,2-Dichlorovinyl)-L-cysteine (DCVC), a mutagenic and nephrotoxic metabolite of trichloroethylene, can be bioactivated to reactive metabolites, S-(1,2-dichlorovinyl)-L-cysteine sulfoxide (DCVCS) or chlorothioketene and/or 2-chlorothionoacetyl chloride, by cysteine conjugate S-oxidase (S-oxidase) and cysteine conjugate beta-lyase (beta-lyase), respectively. Previously, we characterized the reactivity of DCVCS with Hb upon incubation of erythrocytes with DCVCS and provided evidence for the formation of distinct DCVCS-Hb monoadducts and cross-links in both isolated erythrocytes and rats given DCVCS. In the present study, we investigated DCVC bioactivation and Hb adduct formation in isolated rat erythrocytes incubated with DCVC (9 and 450 microM) at 37 degrees C and pH 7.4. The results suggested that no DCVCS monoadducts or cross-links were formed; however, LC/electrospray ionization/MS and matrix-assisted laser desorption/ionization/MS of trypsin-digested globin peptides revealed the presence of beta-lyase-derived globin monoadducts and cross-links. Adducts and cross-links in which the sulfur atom of the reactive sulfur intermediates were replaced by oxygen have also been detected. Use of SDS-PAGE provided additional evidence for globin cross-link formation in the presence of DCVC. Interestingly, the MS results suggest that the observed peptide selectivity of the beta-lyase-derived reactive sulfur/oxygen-containing species was different than that previously observed with DCVCS. While these results suggested that erythrocytes have beta-lyase but not S-oxidase activity, further support for this hypothesis was obtained using S-(2-benzothiazolyl)-L-cysteine, an alternative substrate for beta-lyases. Collectively, the results demonstrate the utility of Hb adducts and cross-links to characterize the metabolic pathway responsible for DCVC bioactivation in erythrocytes and to provide distinct biomarkers for each reactive metabolite.

Detection of multiple globin monoadducts and cross-links after in vitro exposure of rat erythrocytes to S-(1,2-dichlorovinyl)-L-cysteine sulfoxide and after in vivo treatment of rats with S-(1,2-dichlorovinyl)-L-cysteine sulfoxide

S-(1,2-dichlorovinyl)- L-cysteine sulfoxide (DCVCS), a Michael acceptor produced by an FMO3-mediated oxidation of the trichloroethylene metabolite S-(1,2-dichlorovinyl)- L-cysteine (DCVC), is a more potent nephrotoxicant than DCVC. Because DCVCS incubations with N-acetyl- L-cysteine at pH 7.4, 37 degrees C resulted in the formation of three diastereomeric monoadducts and one diadduct, globin monoadducts and cross-links formed after in vitro incubations of rat erythrocytes with DCVCS (0.9-450 microM) for 2 h and those present at 30 min after in vivo treatment of rats with DCVCS (23 and 230 micromol/kg) were characterized. ESI/MS of intact globin chains revealed adduction of 1 DCVCS moiety on the beta2 chain at the three lowest DCVCS concentrations and on the beta1 chain after the in vivo treatment with 230 micromol/kg DCVCS. Interestingly, intact globin dimers and trimers were detectable by ESI/MS with all DCVCS concentrations in vitro (also by SDS-PAGE) and in vivo. LC/MS and MALDI/FTICR of trypsin digested peptides from globin samples obtained after in vitro (450 microM DCVCS) or in vivo exposure to DCVCS (230 micromol/kg) suggested the formation of DCVCS monoadducts not only with Cys93 and Cys125 of the beta chains but also with Cys13 of the alpha chains, whereas no monoadducted peptides were detected at lower DCVCS concentrations in vitro or in vivo. However, LC/MS and MALDI-TOF/TOF suggested the presence of several DCVCS-derived peptide cross-links both in vivo and in vitro at all DCVCS exposure levels. Collectively, the results indicate at least 4 out of the 5 cysteine moieties of the rat hemoglobin heterodimer may be alkylated by DCVCS, in reactions that could also lead to the formation of multiple cross-links. DCVCS- and N-acetyl-DCVCS (NA-DCVCS)-derived globin cross-links containing GSH and Cys were also detected by mass spectrometry, providing strong evidence for the reactivity and/or cross-linking ability of DCVCS, NA-DCVCS, and their GSH or Cys conjugates in both the in vitro and the in vivo. Thus, hemoglobin adducts and cross-links may be useful biomarkers to investigate the possible presence of DCVCS in circulation after DCVC or trichloroethylene exposure.

Formation of three N-acetyl-L-cysteine monoadducts and one diadduct by the reaction of S-(1,2-dichlorovinyl)-L-cysteine sulfoxide with N-acetyl-L-cysteine at physiological conditions: chemical mechanisms and toxicological implications

Previously, our laboratory has shown that S-(1,2-dichlorovinyl)-L-cysteine sulfoxide (DCVCS), a Michael acceptor produced by a flavin-containing monooxygenase 3 (FMO3)-mediated oxidation of S-(1,2-dichlorovinyl)-L-cysteine (DCVC), is a more potent nephrotoxicant than DCVC. In the present study, we characterized reactions of DCVCS with nucleophilic amino acids. DCVCS incubations with N-acetyl-L-cysteine (NAC) at pH 7.4 and 37 degrees C for 1 h resulted in the formation of three monoadducts and one diadduct characterized by LC/MS, 1H NMR, and 1H-detected heteronuclear single quantum correlation. The formation of all adducts (with relative ratios of 29, 31, 24, and 12%, respectively) was rapid and time-dependent; the half-lives of the two DCVCS diastereomers in the presence of NAC were 13.8 (diastereomer I) and 9.4 min (diastereomer II). Adducts 1 and 2 were determined to be diastereomers of S-[1-chloro-2-(N-acetyl-L-cystein- S-yl)vinyl]-L-cysteine sulfoxide formed by Michael addition of NAC to the terminal vinylic carbon of DCVCS followed by loss of HCl. Adduct 4 was determined to be S-[2-chloro-2-(N-acetyl-L-cystein- S-yl)vinyl]-L-cysteine sulfoxide formed from the initial Michael addition product followed by a less favorable loss of HCl and/or by a rearrangement of adduct 2 through the formation of a cyclic chloronium ion. The addition of another molecule of NAC to monoadducts 1, 2, or 4 resulted in the formation of the novel diadduct, S-[2,2-( N-acetyl-L-cystein-S-yl)vinyl]-L-cysteine sulfoxide (adduct 3), whose detection in relatively large amount suggests that DCVCS could act as a cross-linking agent. DCVCS was not reactive with N-acetyl-L-lysine or L-valinamide at similar incubation conditions. Collectively, the results suggest selective reactivity of DCVCS toward protein sulfhydryl groups. Furthermore, the cross-linking properties of DCVCS may in part explain its high nephrotoxic potency.

Formation and toxicity of anesthetic degradation products

Toxic degradation products are formed from a range of old and modern anesthetic agents. The common element in the formation of degradation products is the reaction of the anesthetic agent with the bases in the carbon dioxide absorbents in the anesthesia circuit. This reaction results in the conversion of trichloroethylene to dichloroacetylene, halothane to 2-bromo-2-chloro-1,1-difluoroethylene, sevoflurane to 2-(fluoromethoxy)-1,1,3,3,3-pentafluoro-1-propene (Compound A), and desflurane, isoflurane, and enflurane to carbon monoxide. Dichloroacetylene, 2-bromo-2-chloro-1,1-difluoroethylene, and Compound A form glutathione S-conjugates that undergo hydrolysis to cysteine S-conjugates and bioactivation of the cysteine S-conjugates by renal cysteine conjugate beta-lyase to give nephrotoxic metabolites. The elucidation of the mechanisms of formation and bioactivation of degradation products has allowed for the safe use of anesthetics that may undergo degradation in the anesthesia circuit.

Bioactivation mechanisms of haloalkene cysteine S-conjugates modeled by gas-phase, ion-molecule reactions

Glutathione conjugate formation plays important roles in the detoxification and bioactivation of xenobiotics. A range of nephrotoxic haloalkenes undergo bioactivation that involves glutathione and cysteine S-conjugate formation. The cysteine S-conjugates thus formed may undergo cysteine conjugate beta-lyase-catalyzed biotransformation to form cytotoxic thiolates or thiiranes. In the studies presented here, cysteine conjugate beta-lyase-catalyzed biotransformations were modeled by anion-induced elimination reactions of S-(2-bromo-1,1, 2-trifluoroethyl)-N-acetyl-L-cysteine methyl ester, S-(2-chloro-1,1, 2-trifluoroethyl)-N-acetyl-L-cysteine methyl ester, and S-(2-fluoro-1,1,2-trifluoroethyl)-N-acetyl-L-cysteine methyl ester in the gas phase. Examination of these processes in the gas phase allowed direct observation of the formation of cysteine S-conjugate-derived thiolates and thiiranes, whose formation is inferred from condensed-phase results. The cysteine S-conjugates of these haloethenes exhibit distinctive patterns of mutagenicity that are thought to be correlated with the nature of the products formed by their cysteine conjugate beta-lyase-catalyzed biotransformation. In particular, S-(2-bromo-1,1,2-trifluoroethyl)-L-cysteine is mutagenic, whereas the chloro and fluoro analogues are not. It has been proposed that the mutagenicity of S-(2-bromo-1,1, 2-trifluoroethyl)-L-cysteine is correlated with the greater propensity of the bromine-containing cysteine S-conjugate to form a thiirane compared with those of the chlorine- or fluorine-containing conjugates. The ease of thiirane formation is consistent with the gas-phase results presented here, which show that the bromine-containing conjugate has a greater propensity to form a thiirane on anionic base-induced elimination than the chloro- or fluoro-substituted analogues. The blocked cysteine S-conjugates were deprotonated by gas-phase ion-molecule reactions with hydroxide, methoxide, and ethoxide ions and then allowed to decompose. The mechanisms for these decompositions are discussed as well as the insights into the bioactivation of these cysteine S-conjugates provided by the further decompositions of thiolate intermediates.

Mutagenicity of trichloroethylene and its metabolites: implications for the risk assessment of trichloroethylene

This article addresses the evidence that trichloroethylene (TCE) or its metabolites might mediate tumor formation via a mutagenic mode of action. We review and draw conclusions from the published mutagenicity and genotoxicity information for TCE and its metabolites, chloral hydrate (CH), dichloroacetic acid (DCA), trichloroacetic acid (TCA), trichloroethanol, S-(1, 2-dichlorovinyl)-l-cysteine (DCVC), and S-(1, 2-dichlorovinyl) glutathione (DCVG). The new U.S. Environmental Protection Agency proposed Cancer Risk Assessment Guidelines provide for an assessment of the key events involved in the development of specific tumors. Consistent with this thinking, we provide a new and general strategy for interpreting genotoxicity data that goes beyond a simple determination that the chemical is or is not genotoxic. For TCE, we conclude that the weight of the evidence argues that chemically induced mutation is unlikely to be a key event in the induction of human tumors that might be caused by TCE itself (as the parent compound) and its metabolites, CH, DCA, and TCA. This conclusion derives primarily from the fact that these chemicals require very high doses to be genotoxic. There is not enough information to draw any conclusions for trichloroethanol and the two trichloroethylene conjugates, DCVC and DCVG. There is some evidence that DCVC is a more potent mutagen than CH, DCA, or TCA. Unfortunately, definitive conclusions as to whether TCE will induce tumors in humans via a mutagenic mode of action cannot be drawn from the available information. More research, including the development and use of new techniques, is required before it is possible to make a definitive assessment as to whether chemically induced mutation is a key event in any human tumors resulting from exposure to TCE.

Biotransformation, excretion, and nephrotoxicity of the hexachlorobutadiene metabolite (E)-N-acetyl-S-(1,2,3,4, 4-pentachlorobutadienyl)-L-cysteine sulfoxide

Hexachlorobuta-1,3-diene (HCBD) is nephrotoxic in rodents. Its toxicity is based upon a multistep bioactivation pathway. Conjugation with glutathione by glutathione S-transferases to form (E)-S-(1,2,3,4,4-pentachlorobutadienyl)-L-glutathione (PCBG), further processing to the corresponding cysteine S-conjugate, and finally processing to a reactive thioketene are thought to be responsible for the observed nephrotoxic effects. A novel metabolite, identified as (E)-N-acetyl-S-(1,2,3,4, 4-pentachlorobutadienyl)-L-cysteine sulfoxide (N-AcPCBC-SO), was described after administration of [14C]HCBD to male Wistar rats. This metabolite is formed by sulfoxidation of N-acetyl-S-(1,2,3,4, 4-pentachlorobutadienyl)-L-cysteine (N-AcPCBC) mediated by cytochrome P450 3A and has been found to be cytotoxic to proximal tubular cells in vitro without activation by beta-lyase. In rats, given HCBD in vivo, only one diastereomer of the sulfoxide is excreted; however, in rat hepatic microsomes two diastereomers, (R)- and (S)-N-AcPCBC-SO, are formed. This study focuses on the mechanisms responsible for this discrepancy and on a possible contribution of N-AcPCBC-SO to the nephrotoxicity of HCBD in vivo. (R,S)-N-AcPCBC-SO (1:1 mixture of both diastereomers) and N-acetyl-alpha-methyl-S-(1,2,3,4,4-pentachlorobutadienyl)-d, L-cysteine sulfoxide (alpha-Me-N-AcPCBC-SO) were administered iv to male and female Wistar rats (20, 40, and 80 micromol/kg of body weight). alpha-Me-N-AcPCBC-SO cannot be cleaved by cysteine conjugate beta-lyase even if alpha-Me-N-AcPCBC-SO is deacetylated by acylases. Excretion of gamma-glutamyltranspeptidase, protein, and glucose in the urine, indicative for kidney damage, and histopathological examination of the kidneys showed marked differences in the renal damage in male and female rats after application of N-AcPCBC-SO and alpha-Me-N-AcPCBC-SO. Necroses of the kidney tubules were only found in male, but not female, rats. Major sex-specific differences were observed in the elimination of sulfoxides; the (R)-isomer was excreted in a 5-10-fold excess to the (S)-isomer after application of (R,S)-N-AcPCBC-SO. After purification, both isomers were administered to male rats resulting in the urinary excretion of (R)-N-AcPCBC-SO after giving the (R)-isomer; treatment with (S)-N-AcPCBC-SO, however, revealed the formation of (S)-N-acetyl-S-(2-glycinylcystein-S-yl-1,3,4, 4-tetrachlorobutadienyl)-L-cysteine. The results show major sex-specific differences in the nephrotoxic potency of N-AcPCBC-SO and alpha-Me-N-AcPCBC-SO. However, both N-AcPCBC-SO and alpha-Me-N-AcPCBC-SO are nephrotoxic in males, suggesting the formation of a vinyl sulfoxide as an additional, beta-lyase-independent mechanism in HCBD-caused nephrotoxicity.

Glutathione-dependent bioactivation of haloalkenes

Several halogenated alkenes are nephrotoxic in rodents. A mechanism for the organ-specific toxicity of these compounds to the kidney has been elucidated. The mechanism involves hepatic glutathione conjugation to dihaloalkenyl or 1,1-difluoroalkyl glutathione S-conjugates, which are cleaved by gamma-glutamyltransferase and dipeptidases to cysteine S-conjugates. Haloalkene-derived cysteine S-conjugates may have four fates in the organism: (a) They may be substrates for renal cysteine conjugate beta-lyases, which cleave them to form reactive intermediates identified as thioketenes (chloroalkene-derived S-conjugates), thionoacyl halides (fluoroalkene-derived S-conjugates not containing bromide), thiiranes, and thiolactones (fluoroalkene-derived S-conjugates containing bromine); (b) cysteine S-conjugates may be N-acetylated to excretable mercapturic acids; (c) they may undergo transamination or oxidation to the corresponding 3-mercaptopyruvic acid S-conjugate; (d) finally, oxidation of the sulfur atom in halovinyl cysteine S-conjugates and corresponding mercapturic acids forms Michael acceptors and may also represent a bioactivation reaction. The formation of reactive intermediates by cysteine conjugate beta-lyase may play a role in the target-organ toxicity and in the possible renal tumorigenicity of several chlorinated olefins widely used in many chemical processes.

Trichloroethylene health risk assessment: a new and improved process

Trichloroethylene (TCE), an environmental contaminant of National concern, is the focus of a new health risk assessment process incorporating the Proposed Cancer Risk Assessment Guidelines. This paper describes not only how TCE became an environmental problem for the Air Force, but also details the new Risk Assessment process envisioned by the Environmental Protection Agency's (EPA) National Center for Environmental Assessment (NCEA). Insights on epidemiological evaluations, both past and future, and their impact on the cancer classification of TCE are discussed. Examples of how physiologically based pharmacokinetics and dose-response characterization described in the new Cancer Guidelines are applied to TCE are provided. In addition, a variety of modeling techniques are discussed for the development of reference doses (oral exposure) and reference concentrations (inhalation exposures) for TCE. Finally, the role of risk communication is included. This new process provides an example of how interagency (EPA, Department of Defense. Department of Energy) and extramural (industry, academia) partnerships can provide greater gains to the nation, as a whole, than any of the parts on their own.

Trichloroethylene cancer risk: simplified calculation of PBPK-based MCLs for cytotoxic end points

Cancer risk assessments for trichloroethylene (TCE) based on linear extrapolation from bioassay results are questionable in light of new data on TCE's likely mechanism of action involving induced cytotoxicity, for which a threshold-type dose-response model may be more appropriate. Previous studies have shown that if a genotoxic mechanism for TCE is assumed, algebraic methods can considerably simplify the use of physiologically based pharmacokinetic (PBPK) models to estimate virtually safe environmental concentrations for humans based on rodent cancer-bioassay data. We show here how such methods can be extended to the case in which TCE is assumed to induce cancer via cytotoxicity, to estimate environmentally safe concentrations based on rodent toxicity data. These methods can be substituted for the numerical methods typically used to calculate PBPK-effective doses when these are defined as peak concentrations. We selected liver and kidney as plausible target tissues, based on an analysis of rodent TCE-bioassay data and on a review of related data bearing on mechanism. Tumor patterns in rodent bioassays are shown to be consistent with our estimates of PBPK-based, effective cytotoxic doses to mice and rats used in these studies. When used with a margin of exposure of 1000, our method yielded maximum concentration levels for TCE of 16 ppb (87 micrograms/m3) for TCE in air respired 24 hr/day, 700 ppb (3.8 mg/m3) for TCE in air respired for relatively brief daily periods (e.g., 0.5 hr while showering/bathing), and 210 micrograms/liter for TCE in drinking water assuming a daily 2-liter ingestion. Cytotoxic effective doses were also estimated for occupational respiratory exposures. These estimates indicate that the current OSHA permissible exposure limit for TCE would produce metabolite concentrations that exceed an acute no observed adverse effect level for hepatotoxicity in mice. On this basis, the OSHA TCE limit is not expected to be protective.

Sulfoxidation of mercapturic acids derived from tri- and tetrachloroethene by cytochromes P450 3A: a bioactivation reaction in addition to deacetylation and cysteine conjugate beta-lyase mediated cleavage

In the present study we investigated the formation of sulfoxides from N-acetyl-S-(1,2,2-trichlorovinyl)-L-cysteine (N-Ac-TCVC), N-acetyl-S-(1,2-dichlorovinyl)-L-cysteine (N-Ac-1,2-DCVC), and N-acetyl-S-(2,2-dichlorovinyl)-L-cysteine (N-Ac-2,2-DCVC), which are formed in the glutathione dependent bioactivation of tri- and tetrachloroethene. The first aim was to elucidate the enzymes involved in these oxidation reactions. N-Ac-TCVC, N-Ac-1,2-DCVC, and N-Ac-2,2-DCVC are oxidized to the corresponding sulfoxides mainly, if not exclusively, by cytochrome P450 enzymes in liver microsomes of untreated male rats, since no role for the flavin-containing monooxygenase (FMO) could be demonstrated by heat inactivation experiments and by the use of n-octylamine. The sulfoxidation rates were increased when using liver microsomes of phenobarbital and dexamethasone pretreated male rats as well as liver microsomes of dexamethasone pretreated female rats, while no sulfoxide formation was observed in liver microsomes of untreated female rats, suggesting an involvement of cytochrome P450 3A. Also, troleandomycin, a specific chemical inhibitor for cytochrome P450 3A, drastically reduced sulfoxidation rates. The observed rates of sulfoxidation also correlated well with the rates of oxidation of testosterone at the 6-beta-position, a specific marker for P450 3A activity. The second aim of this study was to compare the cytotoxicity of the sulfoxides with the cytotoxicity of the corresponding mercapturic acids in isolated rat renal epithelial cells. Both mercapturic acids and the corresponding sulfoxides were cytotoxic. Cytotoxicity of the mercapturic acids could be blocked by (aminooxy)acetic acid (AOAA), an inhibitor of cysteine conjugate beta-lyase, while the cytotoxicity of the sulfoxides was not influenced by this treatment. Moreover, the sulfoxides were significantly more cytotoxic than the corresponding mercapturic acids at equimolar doses. The results show that mercapturic acids derived from TRI and PER are oxidized to sulfoxides by microsomal monooxygenases from rat liver. The cytotoxicity of the produced sulfoxides could not be reduced by AOAA, consistent with a role of the sulfoxides as direct acting electrophiles (i.e., Michael acceptor substrates).

Cysteine conjugate beta-lyase-catalyzed bioactivation of bromine-containing cysteine S-conjugates: stoichiometry and formation of 2,2-difluoro-3-halothiiranes

1,1-Dichloroalkene-derived S-(1-chloroalkenyl)-L-cysteine conjugates, but not 1,1-difluoroalkene-derived S-(2,2-dihalo-1,1-difluoroethyl)-L-cysteine conjugates, are mutagenic in the Ames test. Recent studies have showed, however, that bromine-containing, 1,1-difluoroalkene-derived S-(2-bromo-2-halo-1,1-difluoroethyl)-L-cysteine conjugates are mutagenic [Finkelstein, M. B., et al. (1994) Chem. Res. Toxicol. 7, 157-163] and that alpha-thiolactones are formed as reactive intermediates and glyoxylate as a terminal product [Finkelstein, M. B., et al. (1995) J. Am. Chem. Soc. 117, 9590-9591]. The present studies were undertaken to examine the stoichiometry of cysteine conjugate beta-lyase-catalyzed product formation from a panel of bromine-containing and bromine-lacking cysteine S-conjugates and to search for additional metabolites. The cysteine S-conjugates were incubated with rat renal homogenates, and pyruvate:product (glyoxylate, bromide, fluoride, dihaloacetate, trihaloethene) ratios were measured. Pyruvate:glyoxylate ratios for S-(2-bromo-1,1,2-trifluoroethyl)-L-cysteine, S-(2-bromo-2-chloro-1,1-difluoroethyl)-L-cysteine, and S-(2,2-dibromo-1,1-difluoroethyl)-L-cysteine ranged from 1:0.13 to 1:0.16. With S-(2-bromo-2-chloro-1,1-difluoroethyl)-L-cysteine and S-(2-bromo-1,1,2-trifluoroethyl)-L-cysteine, pyruvate:bromide ratios were 1:1, but with the dibrominated conjugate S-(2,2-dibromo-1,1-difluoroethyl)-L-cysteine, the pyruvate:bromide ratio was 1:1.2. All bromine-containing cysteine S-conjugates gave less than complete conversion to fluoride. A search for additional metabolites led to the consideration of 2,2-difluoro-3-halothiiranes as putative intermediates. 2,2-Difluoro-3-halothiiranes may arise by internal displacement of bromide and cyclization of 2-bromo-2-halo-1,1-difluoroethanethiolates, which are beta-elimination products of cysteine S-conjugates. Such halogenated thiiranes may eliminate sulfur to give 1,1-difluoro-2-haloethenes. GC/MS analysis showed that trifluoroethene, 2-chloro-1,1-difluoroethene, and 2-bromo-1,1-difluoroethene were terminal products of S-(2-bromo-1,1,2-trifluoroethyl)-L-cysteine, S-(2-bromo-2-chloro-1,1-difluoroethyl)-L-cysteine, and S-(2,2-dibromo-1,1-difluoroethyl)-L-cysteine, respectively. The bromine-lacking conjugate S-(2-chloro-1,1,2-trifluoroethyl)-L-cysteine did not yield glyoxylate or trifluoroethene as products, but the formation of chlorofluoroacetate was confirmed. The pyruvate:chlorofluoroacetate ratio was 1:0.38, indicating that other products are formed. This is the first report of the stoichiometry of the beta-lyase-catalyzed biotransformation of haloalkene-derived cysteine S-conjugates and of the formation of 2,2-difluoro-3-halothiiranes as reactive intermediates in the biotransformation of bromine-containing cysteine S-conjugates.

Renal activation of trichloroethene and S-(1,2-dichlorovinyl)-L-cysteine and cell proliferative responses in the kidneys of F344 rats and B6C3F1 mice

Covalent binding of reactive intermediates formed by renal beta-lyase activation of S-(1,2-dichlorovinyl)-L-cysteine (DCVC) has been suggested to be responsible for the greater renal sensitivity of rats than mice to the carcinogenic effects of chronic treatment with trichloroethene (TRI). Previous work demonstrated that the activation of DCVC results in acid-labile adducts to protein that can be distinguished from adducts formed by other pathways of TRI metabolism. By analyzing acid-labile adduct formation, the relationship between DCVC formation and activation from TRI and increases in rates of cell division in the kidneys of male F344 rats and B6C3F1 mice could be investigated. The delivered dose of DCVC from an oral dose of 1000 mg/kg TRI was approximately six times greater in rats than mice. However, renal activation of DCVC in mice was approximately 12 times greater than in rats. Therefore, the overall activation of TRI was about two times greater in mice than rats. Induction of cell replication in liver and kidney following doses of 1, 5, or 25 mg/kg DCVC or 1000 mg/kg TRI was also measured through the use of miniosmotic pumps that delivered BrdU subcutaneously for 3 d. Acid-labile adduct formation from DCVC and TRI displayed a consistent relationship with increased cell replication in mice and between mice and rats. Both cell replication and acid-labile adduct formation in rats given 25 mg/kg DCVC were approximately equal to that observed in mice given 1 mg/kg. Increased cell replication was not observed in rats receiving 1 or 5 mg/kg DCVC or 1000 mg/kg TRI, nor were there histological signs of nephrotoxicity. Thus, net activation of TRI by the cysteine S-conjugate pathway was found to be greater in mice than rats and these findings appeared related to differences in cell proliferative responses of the kidneys of the two species. Based on these data, it would appear that other factors must contribute to the greater sensitivity of the rat to the induction of renal carcinogenesis by TRI.

Increased incidence of renal cell tumors in a cohort of cardboard workers exposed to trichloroethene

A retrospective cohort study was carried out in a cardboard factory in Germany to investigate the association between exposure to trichloroethene (TRI) and renal cell cancer. The study group consisted of 169 men who had been exposed to TRI for at least 1 year between 1956 and 1975. The average observation period was 34 years. By the closing day of the study (December 31, 1992) 50 members of the cohort had died, 16 from malignant neoplasms. In 2 out of these 16 cases, kidney cancer was the cause of death, which leads to a standard mortality ratio of 3.28 compared with the local population. Five workers had been diagnosed with kidney cancer: four with renal cell cancers and one with a urothelial cancer of the renal pelvis. The standardized incidence ratio compared with the data of the Danish cancer registry was 7.97 (95% CI: 2.59-18.59). After the end of the observation period, two additional kidney tumors (one renal cell and one urothelial cancer) were diagnosed in the study group. The control group consisted of 190 unexposed workers in the same plant. By the closing day of the study 52 members of this cohort had died, 16 from malignant neoplasms, but none from kidney cancer. No case of kidney cancer was diagnosed in the control group. The direct comparison of the incidence on renal cell cancer shows a statistically significant increased risk in the cohort of exposed workers. Hence, in all types of analysis the incidence of kidney cancer is statistically elevated among workers exposed to TRI.(ABSTRACT TRUNCATED AT 250 WORDS)

Glutathione-dependent bioactivation of xenobiotics

Glutathione conjugation has been identified as an important detoxication reaction. However, in recent years several glutathione-dependent bioactivation reactions have been identified. Current knowledge on the mechanisms and the possible biological importance of these reactions are discussed. 1. Dichloromethane is metabolized by glutathione conjugation to formaldehyde via S-(chloromethyl)glutathione. Both compounds are reactive intermediates and may be responsible for the dichloromethane-induced tumorigenesis in sensitive species. 2. Vicinal dihaloalkanes are transformed by glutathione S-transferase-catalyzed reactions to mutagenic and nephrotoxic S-(2-haloethyl)glutathione S-conjugates. Electrophilic episulphonium ions are the ultimate reactive intermediates formed. 3. Several polychlorinated alkenes are bioactivated in a complex, glutathione-dependent pathway. The first step is hepatic glutathione S-conjugate formation followed by cleavage to the corresponding cysteine S-conjugates, and, after translocation to the kidney, metabolism by renal cysteine conjugate beta-lyase. Beta-Lyase-dependent metabolism of halovinyl cysteine S-conjugates yields electrophilic thioketenes, whose covalent binding to cellular macromolecules is responsible for the observed toxicity of the parent compounds. 4. Finally, hepatic glutathione conjugate formation with hydroquinones and aminophenols yields conjugates that are directed to gamma-glutamyltransferase-rich tissues, such as the kidney, where they undergo alkylation or redox cycling reactions, or both, that cause organ-selective damage.

Bioactivation of nephrotoxins and renal carcinogens by glutathione S-conjugate formation

Evidence has been accumulating that several classes of compounds are converted by glutathione conjugate formation to toxic metabolites. The aim of this review is to summarize the current knowledge on the biosynthesis and toxicity of glutathione S-conjugates derived from halogenated alkenes, and hydroquinones and quinones. Different types of toxic glutathione conjugates have been identified in detail; (i) conjugates which are converted to toxic metabolites in an enzyme-catalyzed multistep mechanism and (ii) conjugates which serve as a transport form for toxic quinones will be discussed. The kidney is the main, with some compounds the exclusive, target organ for compounds metabolized by these pathways. Selective toxicity to the kidney is easily explained due to the capability of the kidney to accumulate intermediates formed by processing of S-conjugates and to bioactivate these intermediates to toxic metabolites. The influences of other factors participating in the renal susceptibility and influencing human risk assessment for these compounds are discussed.

Glutathione-dependent toxicity

1. Recent studies show that glutathione conjugate formation is an important bioactivation mechanism for several groups of compounds with implications for organ-selective toxicity and carcinogenicity. 2. Vicinal dihaloalkanes, such as 1,2-dihaloethanes, yield S-(2-haloalkyl)glutathione conjugates that give rise to highly electrophilic episulphonium ions, which are involved in the cytotoxicity and mutagenicity of 1,2-dihaloethanes. 3. Nephrotoxic haloalkenes are metabolized to S-(haloalkenyl)- or S-(haloalkyl)-glutathione conjugates which, after metabolism to the corresponding cysteine conjugates, are bioactivated by renal cysteine conjugate beta-lyase to yield cytotoxic or mutagenic metabolites. 4. Finally, hepatic glutathione conjugate formation with hydroquinones and aminophenols yields conjugates that are directed to gamma-glutamyltransferase-rich tissues, such as the kidney, where they undergo alkylation or redox cycling reactions, or both, that cause organ-selective damage.

Biological monitoring of bidi rollers with respect to genotoxic hazards of occupational tobacco exposure

Smokeless tobacco habits are associated with a high incidence of oropharyngeal cancer in India. Hence, the biological effects of occupational exposure to smokeless tobacco used for making bidis (the Indian version of cigarettes) were studied in 2 groups of bidi rollers designated BR-K and BR-S and in control subjects with no tobacco habits. Specific tobacco exposure and the electrophilic burden were determined by estimating urinary cotinine and thioethers respectively. Urine mutagenicity was tested with the Ames assay using Salmonella typhimurium strains TA98 and TA100. While cotinine was not detected in control samples, the mean cotinine levels (mmole/mole creatinine) in the BR-K and BR-S groups were 0.79 +/- 0.30 and 0.09 +/- 0.03 respectively. Urinary thioether excretion (mmole/mole creatinine) was significantly elevated in the BR-S group 4.59 +/- 0.52; p less than 0.001) but it was lower in the BR-K group (0.54 +/- 0.08; p less than 0.001) compared to the control (1.83 +/- 0.34). Furthermore, beta-glucuronidase-treated samples from both groups of bidi rollers exhibited increased mutagenicity to TA98 compared to the control group; in addition, BR-S samples exhibited direct mutagenicity to TA98. The results show that occupational tobacco exposure modulates the glutathione conjugation pathway and increases the mutagenic burden of bidi rollers.

Metabolism of 14C-dichloroethyne in rats

1. The metabolism of 14C-dichloroethyne was studied in rats by inhalation in a dynamic nose-only exposure system. 14C-Dichloroethyne was generated in 95-99% yield from 14C-trichloroethene by alkaline dehydrochlorination. 2. After inhalation of 20 ppm and 40 ppm dichloroethyne for 1 h, the retention rates were 17.6% and 15.6% of the radioactivity introduced into the exposure system, respectively. During the period of observation (96 h), almost quantitative elimination of the dose was observed. Elimination with urine accounted for 60.0% (40 ppm) and 67.8% (20 ppm) of absorbed radioactivity and elimination with faeces for 27% (40 ppm) and 27.7% (20 ppm), 3.4-3.5% remained in the carcasses. 3. Metabolites of dichloroethyne identified are: N-acetyl-S-(1,2-dichlorovinyl)-L-cysteine, dichloroethanol, dichloroacetic acid, oxalic acid and chloroacetic acid in urine; N-acetyl-S-(1,2-dichlorovinyl-L-cysteine in faeces. 4. In bile of rats exposed to 40 ppm of dichloroethyne, S-(1,2-dichlorovinyl)glutathione was the only metabolite identified. Biliary cannulation did not influence the renal excretion of N-acetyl-S-(1,2-dichlorovinyl)-L-cysteine, indicating that glutathione conjugate formation occurs in the kidney. 5. The results suggest that two metabolic pathways are operative in dichloroethyne metabolism in vivo. Cytochrome P450-dependent oxidation represents a minor pathway accounting for the formation of 1,1-dichloro compounds after chlorine migration. The major pathway is the biosynthesis of toxic glutathione conjugates. Organ-specific toxicity and carcinogenicity of dichloroethyne is due most likely to the topographical distribution of gamma-glutamyl transpeptidase which is concentrated mainly in the kidney in rats.

Bioactivation of xenobiotics by formation of toxic glutathione conjugates

Evidence has been accumulating that several classes of compounds are converted by glutathione conjugate formation to toxic metabolites. The aim of this review is to summarize the current knowledge on the biosynthesis and toxicity of glutathione S-conjugates derived from halogenated alkanes, halogenated alkenes, and hydroquinones and quinones. Different types of toxic glutathione conjugates have been identified and will be discussed in detail: (i) conjugates which are transformed to electrophilic sulfur mustards, (ii) conjugates which are converted to toxic metabolites in an enzyme-catalyzed multistep mechanism, (iii) conjugates which serve as a transport form for toxic quinones and (iv) reversible glutathione conjugate formation and release of the toxic agent in cell types with lower glutathione concentrations. The kidney is the main, with some compounds the exclusive, target organ for compounds metabolized by pathways (i) to (iii). Selective toxicity to the kidney is easily explained due to the capability of the kidney to accumulate intermediates formed by processing of S-conjugates and to bioactivate these intermediates to toxic metabolites. The influences of other factors participating in the renal susceptibility are discussed.

Sulfur-containing proreactive intermediates: hydrolysis and mutagenicity of halovinyl 2-nitrophenyl disulfides

Chemical cleavage of the sulfur-sulfur bond in halovinyl and fluoroalkyl 2-nitrophenyl disulfides is expected to yield halovinyl and fluoroalkyl thiols identical to those formed by cysteine conjugate beta-lyase catalyzed cleavage of the corresponding cysteine S-conjugates. To study the potential use of disulfides as precursors for these thiols, whose transformation to acylating agents is most likely responsible for cysteine S-conjugate mutagenicity, we determined the mutagenicity of several halovinyl and fluoroalkyl 2-nitrophenyl disulfides and identified products formed by hydrolysis of these disulfides, 1,2,3,4,4-Pentachlorobutadienyl 2-nitrophenyl disulfide, 1,2,2-trichlorovinyl 2-nitrophenyl disulfide, 1-fluro-2,2-dichlorovinyl 2-nitrophenyl disulfide and 1,2-dichloro-3,3,3-trifluropropenyl 2-nitrophenyl disulfide were mutagenic in nitroreductase deficient strains of Salmonella typhimurium TA100; as haloalkyl cysteine S-conjugates, 1,1-difluoro-2,2-dichloroethyl 2-nitrophenyl disulfide and 1-chloro-1,2,2-trifluroethyl 2-nitrophenyl disulfide were not mutagenic. Hydrolysis of 1,2,3,4,4-pentachlorobutadienyl 2-nitrophenyl disulfide and 1,2,2-trifluorethyl 2-nitrophenyl disulfide in presence of diethylamine resulted in tetrachlorothiobutenoic acid diethylamide and chlorofluorothionoacetic acid diethylamide. The differences in mutagenicity between halovinyl and fluoroalkyl disulfides are most likely responsible to their different abilities to react with DNA-constituents. Products formed from the mutagenic 1,2,3,4,4-pentachlorobutadienyl 2-nitrophenyl disulfide modified 2'-deoxyguanosine-3'-monophosphate and DNA as detected by 32Phosphorus-postlabeling, whereas products formed from the nonmutagenic 1-chloro-1,2,2-trifluoroethyl 2-nitrophenyl disulfide did not result in detectable 2'-deoxyguanosine-3'-monophosphate and DNA modification.

Consideration of the target organ toxicity of trichloroethylene in terms of metabolite toxicity and pharmacokinetics

Trichloroethylene (TRI) is readily absorbed into the body through the lungs and gastrointestinal mucosa. Exposure to TRI can occur from contamination of air, water, and food; and this contamination may be sufficient to produce adverse effects in the exposed populations. Elimination of TRI involves two major processes: pulmonary excretion of unchanged TRI and relatively rapid hepatic biotransformation to urinary metabolites. The principal site of metabolism of TRI is the liver, but the lung and possibly other tissues also metabolize TRI, and dichlorovinyl-cysteine (DCVC) is formed in the kidney. Humans appear to metabolize TRI extensively. Both rats and mice also have a considerable capacity to metabolize TRI, and the maximal capacities of the rat versus the mouse appear to be more closely related to relative body surface areas than to body weights. Metabolism is almost linearly related to dose at lower doses, becoming dose dependent at higher doses, and is probably best described overall by Michaelis-Menten kinetics. Major end metabolites are trichloroethanol (TCE), trichloroethanol-glucuronide, and trichloroacetic acid (TCA). Metabolism also produces several possibly reactive intermediate metabolites, including chloral, TRI-epoxide, dichlorovinyl-cysteine (DCVC), dichloroacetyl chloride, dichloroacetic acid (DCA), and chloroform, which is further metabolized to phosgene that may covalently bind extensively to cellular lipids and proteins, and, to a much lesser degree, to DNA. The toxicities associated with TRI exposure are considered to reside in its reactive metabolites. The mutagenic and carcinogenic potential of TRI is also generally thought to be due to reactive intermediate biotransformation products rather than the parent molecule itself, although the biological mechanisms by which specific TRI metabolites exert their toxic activity observed in experimental animals and, in some cases, humans are not known. The binding intensity of TRI metabolites is greater in the liver than in the kidney. Comparative studies of biotransformation of TRI in rats and mice failed to detect any major species or strain differences in metabolism. Quantitative differences in metabolism across species probably result from differences in metabolic rate and enterohepatic recirculation of metabolites. Aging rats have less capacity for microsomal metabolism, as reflected by covalent binding of TRI, than either adult or young rats. This is likely to be the same in other species, including humans. The experimental evidence is consistent with the metabolic pathways for TRI being qualitatively similar in mice, rats, and humans. The formation of the major metabolites--TCE, TCE-glucuronide, and TCA--may be explained by the production of chloral as an intermediate after the initial oxidation of TRI to TRI-epoxide.(ABSTRACT TRUNCATED AT 400 WORDS)

Metabolism of trichloroethene--in vivo and in vitro evidence for activation by glutathione conjugation

The metabolism of trichloroethene by glutathione conjugation was investigated in rat liver subcellular fractions and in male rats in vivo. In the presence of glutathione, rat liver microsomes transformed [14C]trichloroethene to S-(1,2-dichlorovinyl)glutathione (DCVG) identified by gas chromatography mass spectrometry after hydrolysis to the corresponding cysteine S-conjugate and chemical derivatisation. In bile of rats given 2.2 g/kg trichloroethene. DCVG was present in concentrations of 5 nmol (7 ml bile collected over 9 h) and identified by thermospray mass spectrometry after HPLC-purification. E- and Z-N-acetyl-dichlorovinyl-L-cysteine (3.1 nmol present in the pooled 24-h urine) were identified by GC/MS after methylation and butylation as urinary metabolites of trichloroethene (2.2 g/kg, orally). The presented results demonstrate that glutathione-dependent metabolism of trichloroethene is a minor route in the biotransformation of this haloalkene in rats. Formation of S-(1,2-dichlorovinyl)-glutathione, processing to S-(1,2-dichlorovinyl)-L-cysteine and metabolism of this S-conjugate by cysteine beta-lyase in the kidney to reactive and genotoxic intermediates may account for the nephrocarcinogenicity observed after long time administration of trichloroethene in male rats.

Influence of aging on chemically induced hepatotoxicity: role of age-related changes in metabolism

The effects on hepatotoxicity of age-associated changes in drug metabolism are not always straightforward. In the case of allyl alcohol hepatotoxicity in male rats, there is a good relationship between increased metabolic activation by liver alcohol dehydrogenase and enhanced hepatotoxicity in old age. With regard to two other hepatotoxicants, some tentative conclusions about the role of metabolism can be drawn, but they must be tempered with caution due to gaps in the available information. Acetaminophen-induced hepatotoxicity is reduced in old age, and decreased formation of the toxic intermediate may be the reason. There is a prominent effect of aging on acetaminophen conjugation, a shift from sulfation to glucuronidation, but this change does not affect total clearance. The situation with carbon tetrachloride is difficult to interpret because the final outcome is unaltered hepatotoxicity in old age. Nevertheless, the available data suggest that an age-associated decrease in activation of carbon tetrachloride is counterbalanced by a loss in resistance to lipid peroxidation. These conclusions are summarized in Table 5. Again, it must be emphasized that all of these age-dependent changes in toxicity could be related to effects on other systems that are not necessarily involved in the metabolism of hepatotoxicants. Future research is needed to identify pathways of metabolic activation and detoxification in which age-dependent changes occur that result in significant changes in hepatotoxicity. The entire sequence of events from changes at the molecular level to their sequelae at the level of the cell, tissue and intact animal should be investigated, and the results should be confirmed in more than one mammalian model of aging. The aim would be to identify basic mechanisms that result in increased hazard for the aged liver from exposure to toxic compounds.

Mutagenicity of tetrachloroethene in the Ames test--metabolic activation by conjugation with glutathione

The mutagenicity of tetrachloroethene (tetra) and its S conjugate, S-(1,2,2-trichlorovinyl)glutathione (TCVG) was investigated using a modified Ames preincubation assay. TCVG was a potent mutagen in presence of rat kidney particulate fractions containing high concentrations of gamma-glutamyl transpeptidase (GGT) and dipeptidases. Purified tetra was not mutagenic without exogenous metabolic activation or under conditions favoring oxidative metabolism. Preincubation of tetra with purified rat liver glutathione (GSH) S-transferases in presence of GSH and rat kidney fractions resulted in a time-dependent formation of TCVG as determined by (HPLC) analysis and in an unequivocal mutagenic response in the Ames test. Experiments with tetra in the isolated perfused rat liver demonstrated TCVG formation and its excretion with the bile; bile collected after the addition of tetra to the isolated perfused liver was unequivocally mutagenic in bacteria in the presence of kidney particulate fractions. The mutagenicity was reduced in all cases by the GGT inhibitor serine borate or the beta-lyase inhibitor aminooxyacetic acid. These results support the suggestion that cleavage of the GSH S conjugate formed from tetra by the enzymes of the mercapturic acid pathway and by beta-lyase may be involved in the nephrocarcinogenic effects of this haloalkene in rats.