Bacterial cysteine conjugate beta-lyase and the metabolism of cysteine S-conjugates: structural requirements for the cleavage of S-conjugates and the formation of reactive intermediates

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.

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.

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.

Enzymatic activation of sulfur for incorporation into biomolecules in prokaryotes

Sulfur is a functionally important element of living matter. Incorporation into biomolecules occurs by two basic strategies. Sulfide is added to an activated acceptor in the biosynthesis of cysteine, from which methionine, coenzyme A and a number of biologically important thiols can be constructed. By contrast, the biosyntheses of iron sulfur clusters, cofactors such as thiamin, molybdopterin, biotin and lipoic acid, and the thio modification of tRNA require an activated sulfur species termed persulfidic sulfur (R-S-SH) instead of sulfide. Persulfidic sulfur is produced enzymatically with the IscS protein, the SufS protein and rhodanese being the most prominent biocatalysts. This review gives an overview of sulfur incorporation into biomolecules in prokaryotes with a special emphasis on the properties and the enzymatic generation of persulfidic sulfur as well as its use in biosynthetic pathways.

Induction of dedifferentiated clones of LLC-PK1 cells upon long-term exposure to dichlorovinylcysteine

Dichlorovinylcysteine (DCVC), the key metabolite of the nephrotoxic and nephrocarcinogenic chemicals, trichloroethylene and dichloroacetylene, exerts potent acute cellular toxicity in LLC-PK1 cells (Vamvakas S., Bittner, D., Dekant, W. and Anders, M.W. (1992). Events that precede and that follow S-(1,2-dichlorovinyl)-L-cysteine-induced release of mitochondrial Ca2+ and their association with cytotoxicity to renal cells. Biochem. Pharmacol. 44, 1131-1138). In the present study we investigated whether long-term exposure of LLC-PK1 cells to low, non-cytotoxic concentrations of DCVC results in stable morphological and biochemical dedifferentiation. After 7 weeks exposure to 1 and 5 microM DCVC, morphologically changed single cells were picked under the microscope and cultured in absence of DCVC for 4-8 weeks. In contrast to the physiological cuboidal shape of untreated LLC-PK1 cells, the clones derived from long-term exposure to DCVC consisted of elongated, spindle-shaped cells tending to form irregular borders. Moreover, glucose uptake, pH-dependent ammonia production and dome formation, important indicators of the renal tubule origin of the LLC-PK1 cells, were severely impaired in the clones. In addition to the loss of membrane polarity, the clones exhibited altered composition of the nuclear matrix and intermediate filament proteins by two-dimensional gel electrophoresis, increased poly(ADP-ribosyl)ation of nuclear proteins and enhanced expression of c-fos. The induction of dedifferentiated LLC-PK1 clones with stable characteristics upon long-term exposure to the nephrocarcinogen DCVC may represent a useful in vitro model to study biochemical alterations involved in chronic renal toxicity and carcinogenicity.

Bioactivation of cysteine conjugates of 1-nitropyrene oxides by cysteine conjugate beta-lyase purified from Peptostreptococcus magnus

To determine the role of cysteine conjugate beta-lyase (beta-lyase) in the metabolism of mutagenic nitropolycyclic aromatic hydrocarbons, we determined the effect of beta-lyase on the mutagenicities and DNA binding of cysteine conjugates of 4,5-epoxy-4,5-dihydro-1-nitropyrene (1-NP 4,5-oxide) and 9,10-epoxy-9,10-dihydro-1-nitropyrene (1-NP 9,10-oxide), which are detoxified metabolites of the mutagenic compound 1-nitropyrene. We purified beta-lyase from Peptostreptococcus magnus GAI0663, since P. magnus is one of the constituents of the intestinal microflora and exhibits high levels of degrading activity with cysteine conjugates of 1-nitropyrene oxides (1-NP oxide-Cys). The activity of purified beta-lyase was optimal at pH 7.5 to 8.0, was completely inhibited by aminooxyacetic acid and hydroxylamine, and was eliminated by heating the enzyme at 55 degrees C for 5 min. The molecular weight of beta-lyase was 150,000, as determined by fast protein liquid chromatography. S-Arylcysteine conjugates were good substrates for this enzyme. As determined by the Salmonella mutagenicity test, 5 ng of beta-lyase protein increased the mutagenicity of the cysteine conjugate of 1-NP 9,10-oxide (10 nmol per plate) 4.5-fold in Salmonella typhimurium TA98 and 4.1-fold in strain TA100. However, beta-lyase had little effect on the cysteine conjugate of 1-NP 4,5-oxide (10 nmol per plate). Both conjugates exhibited only low levels of mutagenicity with nitroreductase-deficient strain TA98NR. In vitro binding of 1-NP oxide-Cys to calf thymus DNA was increased by adding purified beta-lyase or xanthine oxidase.(ABSTRACT TRUNCATED AT 250 WORDS)

Modulatory influence of arecanut on the mouse hepatic xenobiotic detoxication system and skin papillomagenesis

The modulatory influence of arecanut, a masticatory in several human populations, on the levels of biotransformation system enzymes in mouse liver has been studied. Swiss albino mice of either sex (4 weeks old) were fed on diets containing 0.25%, 0.5%, or 1% arecanut (w/w) for 5 weeks. In addition, a group of mice received a 1% arecanut diet for 36 weeks. The findings revealed a significant increase in hepatic levels of cytochrome b5, cytochrome P-450, malondialdehyde (MDA), and glutathione S-transferase (GST). The hepatic -SH content was depressed by 0.5% and 1% arecanut diets. Long-term feeding of a 1% arecanut diet elicited changes similar to those seen following treatment for 5 weeks. Arecanut-modulated profiles of biotransformation enzymes and antioxidant levels are suggestive of its influence in the process of carcinogenesis induced by bioactivated electrophilic species of potential chemical carcinogens among habitual arecanut chewers. Arecanut was also tested for its potency either to induce or to alter 7,12-dimethylbenz[a]anthracene (DMBA)-induced papillomagenesis in the skin of the mouse. Animals put on a 1% arecanut diet and treated with a standard two-stage protocol for tumor induction developed a 5.41 tumor burden (control value: 5.76) along with 100% incidence of mice bearing papillomas (control value: 94.4%), thus signifying that dietary intake of 1% arecanut for 18 weeks could not induce/alter the mouse skin tumorigenesis pattern.

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.

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.

Mutagenicity and cytotoxicity of two regioisomeric mercapturic acids and cysteine S-conjugates of trichloroethylene

The mutagenicity, cytotoxicity and metabolism of two regioisomic L-cysteine- and N-acetyl-L-cysteine-S-conjugates of trichloroethylene were studied. The 1,2-dichlorovinyl(1,2-DCV) isomers of both the cysteine conjugate and the mercapturate were much stronger mutagens in the Ames test with Salmonella typhimurium TA2638 when compared to the corresponding 2,2-dichlorovinyl (2,2-DCV) isomers. Similarly, the 1,2-DCV isomers were more cytotoxic towards isolated rat kidney proximal tubular cells, as assessed by inhibition of alpha-methylglucose uptake, than the 2,2-DCV isomers. The 3-4-fold higher rate of beta-lyase-dependent activation of S-(1,2-dichlorovinyl)-L-cysteine (1,2-DCV-Cys) when compared to S-(1,2-dichlorovinyl)-L-cysteine (2,2-DCV-Cys) as well as the different nature of the reactive intermediates formed is probably responsible for these structure-dependent effects. The cytotoxicity of N-acetyl-S-(1,2-dichlorovinyl)-L-cysteine (1,2-DCV-NAc) toward isolated kidney cells showed a delayed time course as compared to that of 1,2-DCV-Cys, probably due to the relatively low rate of deacetylation of 1,2-DCV-NAc. The time course of cytotoxicity of N-acetyl-S-(2,2-dichlorovinyl)-L-cysteine (2,2-DCV-NAc), however, parallelled that of 2,2-DCV-Cys. Due to the relatively high rate of N-acetylation and low rate of beta-lyase activation, for 2,2-DCV-Nac the beta-lyase activation step may be rate limiting. Different rates of cellular uptake also may play a role in time course of toxicity of the cysteine conjugates and the mercapturic acids in the renal cells.

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.

Bioactivation of hexachlorobutadiene by glutathione conjugation

Glutathione (GSH) conjugation reactions in the metabolism of hexachlorobutadiene (HCBD), in rats and mice, initiate a series of metabolic events resulting in the formation of reactive intermediates in the proximal tubular cells of the kidney. The GSH S-conjugate 1-(glutathion-S-yl)-1,2,3,4,4-pentachlorobutadiene (GPCB), which is formed by conjugation of HCBD with GSH in the liver, is not reactive and is eliminated from the liver in the bile or plasma, or both. GPCB may be translocated intact to the kidney and processed there by gamma-glutamyl transpeptidase and dipeptidases to the corresponding cysteine S-conjugate. Alternatively, gamma-glutamyl transpeptidase and dipeptidases present in epithelial cells of the bile duct and small intestine may catalyse the conversion of GPCB to cysteine S-conjugates. The kidney concentrates both GSH and cysteine S-conjugates and processes GSH conjugates to cysteine S-conjugates. A substantial fraction of HCBD cysteine S-conjugate thus concentrated in the kidney is metabolized by renal cysteine conjugate beta-lyase to reactive intermediates. The selective formation of reactive intermediates in the kidney most likely accounts for the organ-specific effects of HCBD. Alternatively, cysteine S-conjugates may be acetylated to yield excretable mercapturic acids.

Is the toxicity of cysteine conjugates formed during mercapturic acid biosynthesis relevant to the toxicity of covalently bound drug residues?

In this brief review, we have focused on the relevance of the data on cysteine conjugate toxicity to the potential hazard of bound drug residues. A resonable scenario, based on assumptions as well as literature data, has been presented for the release of cysteine conjugates of drug residues from protein. Furthermore, we have presented evidence that should this occur, the conjugate would be bioavailable. Finally, the mechanisms which could lead to cysteine conjugate-induced toxicity have been discussed. The question which must be answered is, how realistic is the treat of toxicity to the consumer from cysteine-bound drug residues in food products? Based on the data presented here, the danger is minimal, though it cannot be excluded. This is particularly true of the potential for renal complications. However, an important caveat which must not be overlooked is the marked species differences in cysteine conjugate toxicity. Though S-(1,2LD50-dichlorovinyl)-L-cysteine (DCVC) is a renal toxin in rodent models (LD50 = 66-83 mg/kg) [88], a single dose of 4-5 mg/kg causes fatal aplastic anemia in calves [44,59]. Though such a response has never been reported for any other cysteine conjugate, these data must be reckoned with if attempts are made to place acceptable limits on the amount of residues allowable in food products.

Assessment of unscheduled DNA synthesis in a cultured line of renal epithelial cells exposed to cysteine S-conjugates of haloalkenes and haloalkanes

The ability of S-(1,2-dichlorovinyl)-L-cysteine (DCVC), S-(1,2,2-trichlorovinyl)-L-cysteine (TCVC), S-(1,2,3,4,4-pentachlorobutadienyl)-L-cysteine (PCBC), S-(2-chloro-1,1,2-trifluoroethyl)-L-cysteine (CTFEC) and S-(2-chloroethyl)-L-cysteine (CEC) to induce DNA repair was investigated in LLC-PK1, a cultured line of porcine kidney tubular epithelial cells. DNA repair due to exposure of the cells to the S-conjugates was determined as unscheduled DNA synthesis (UDS) after inhibition of replicative DNA synthesis in confluent LLC-PK1 monolayers. DCVC, TCVC and PCBC induced dose-dependent UDS in LLC-PK1 at concentrations which did not impair the viability of the cells compared to untreated controls; higher concentrations were cytotoxic, resulting in lactate dehydrogenase leakage into the medium. Cell death was also induced by CTFEC, which failed to exert genotoxicity. CEC induced the highest response among these cysteine conjugates without impairing cell viability. Inhibition of cysteine conjugate beta-lyase with aminooxyacetic acid abolished the effects of DCVC, TCVC, PCBC and CTFEC but did not influence the genotoxicity of CEC.

Mutagenicity of benzyl S-haloalkyl and S-haloalkenyl sulfides in the Ames-test

The mutagenicity of benzyl 1,2,3,4,4-pentachlorobutadienyl sulfide (BPBS) and benzyl 1,2-dichlorovinyl sulfide (BDVS) was studied in the Ames preincubation assay to investigate the hypothesis that the mutagenic effect of the cysteine S-conjugates S-(pentachlorobutadienyl)-L-cysteine and S-(1,2-dichlorovinyl)-L-cysteine is associated with their metabolism to unstable thiols. Under conditions enabling cytochrome P-450-dependent benzylic hydroxylation of BPBS and BDVS, both benzyl sulfides were mutagenic. These results in combination with the lack of mutagenicity observed with benzaldehyde and with the tert-butyl analogues, which cannot be metabolized to a hemimercaptal, indicate that the formation of unstable thiols is responsible for the mutagenic effects of the benzyl sulfides and the corresponding cysteine S-conjugates. Benzyl 2-chloro-1,1,2-trifluoroethyl sulfide, which also undergoes benzylic hydroxylation, was negative in the Ames-Test; this is in agreement with the observed lack of mutagenicity of the corresponding S-conjugate S-(2-chloro-1,1,2-trifluoroethyl)-L-cysteine. Also, benzyl 2-chloroethyl sulfide, which, along with the corresponding S-conjugate S-(2-chloroethyl)-L-cysteine, does not require bioactivation, was a potent, direct-acting mutagen in the Ames-Test.

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.

Cytotoxicity of cysteine S-conjugates: structure-activity relationships

The cytotoxicity of cysteine S-conjugates was investigated in freshly isolated rat renal proximal tubule cells. The study was designed to determine the contribution of the thiols and of the acylating intermediates formed by cysteine conjugate beta-lyase to the initiation of cytotoxicity. Cell viability was determined by trypan blue exclusion and by lactate dehydrogenase leakage. The S-conjugates S-(1,2,2-trichlorovinyl)-L-cysteine, S-(1,2,3,3,3-pentachloro-prop-1-enyl)-L-cysteine and S-(1,2,3,4,4-pentachlorobuta-1,3-dienyl)-L-cysteine, at a concentration of 0.2 mM, reduced cell viability compared to controls from 85% to less than 50% after 3 h. The alpha-chlorinated enethiols formed from these S-conjugates are transformed to acylating intermediates. The S-conjugate S-(2-chlorovinyl)-L-cysteine forms an enethiol, which cannot transform to an acylating intermediate and did not reduce cell viability at 0.2 mM; at 1 mM, it resulted in a very slight reduction of cell viability after 3 h. S-(pentachlorophenyl)-L-cysteine and S-benzyl-L-cysteine, which form stable thiols after metabolism by beta-lyase, were not cytotoxic at a concentration of 1 mM. The direct acting S-(2-chloroethyl)-L-cysteine (0.2 mM) reduced cell viability after 3 h from 85% to 90% (control) to 40%. The results obtained suggest that reactions of the initial thiol-metabolites with biological macromolecules do not contribute to the induction of cytotoxicity by cysteine S-conjugates and indicate that acylating intermediates formed by cysteine conjugate R-lyase induce cytotoxic effects by non-selective acylation of cellular macromolecules.

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.

Induction of unscheduled DNA synthesis and micronucleus formation in Syrian hamster embryo fibroblasts treated with cysteine S-conjugates of chlorinated hydrocarbons

S-(chloroethyl)-cysteine (CEC) and S-(1,2-dichlorovinyl)-cysteine (DCVC) have been proposed as intermediates in the metabolic transformation of the carcinogens 1,2-dichloroethane and 1,1,2-trichloroethylene. We have tested the ability of CEC and DCVC to induce DNA repair and genotoxic effects at the chromosomal level by comparative assessment of unscheduled DNA synthesis induction and micronucleus formation in Syrian hamster embryo fibroblasts. CEC induced a potent and dose-dependent response in both assays, whereas DCVC treatment resulted in a comparatively weak induction of DNA repair and failed to raise micronucleus formation above control rates. Inhibition of cysteine conjugate beta-lyase diminished the effect of DCVC, but had no influence on the genotoxicity of CEC either in the unscheduled DNA synthesis or micronucleus assay.