Evidence for the active renal secretion of S-pentachlorophenyl-N-acetyl-L-cysteine by female rats

Application of physiologically-based pharmacokinetic modeling to explore the role of kidney transporters in renal reabsorption of perfluorooctanoic acid in the rat

Renal elimination and the resulting clearance of perfluorooctanoic acid (PFOA) from the serum exhibit pronounced sex differences in the adult rat. The literature suggests that this is largely due to hormonally regulated expression of organic anion transporters (OATs) on the apical and basolateral membranes of the proximal tubule cells that facilitate excretion and reabsorption of PFOA from the filtrate into the blood. Previously developed PBPK models of PFOA exposure in the rat have not been parameterized to specifically account for transporter-mediated renal elimination. We developed a PBPK model for PFOA in male and female rats to explore the role of Oat1, Oat3, and Oatp1a1 in sex-specific renal reabsorption and excretion of PFOA. Descriptions of the kinetic behavior of these transporters were extrapolated from in vitro studies and the model was used to simulate time-course serum, liver, and urine data for intravenous (IV) and oral exposures in both sexes. Model predicted concentrations of PFOA in the liver, serum, and urine showed good agreement with experimental data for both male and female rats indicating that in vitro derived physiological descriptions of transporter-mediated renal reabsorption can successfully predict sex-dependent excretion of PFOA in the rat. This study supports the hypothesis that sex-specific serum half-lives for PFOA are largely driven by expression of transporters in the kidney and contribute to the development of PBPK modeling as a tool for evaluating the role of transporters in renal clearance.

Ochratoxin a and mitotic disruption: mode of action analysis of renal tumor formation by ochratoxin A

The mycotoxin and food contaminant ochratoxin A (OTA) is a potent renal carcinogen in rodents, but its mode of action (MoA) is still poorly defined. In 2006, the European Food Safety Authority concluded that there is a "lack of evidence for the existence of OTA-DNA adducts" and thus insufficient evidence to establish DNA reactivity as a MoA for tumor formation by OTA. In reviewing the available database on OTA toxicity, a MoA for renal carcinogenicity of OTA is developed that involves a combination of genetic instability and increased proliferative drive as consequences of OTA-mediated disruption of mitosis, whereby the organ- and site-specificity of tumor formation by OTA is determined by selective renal uptake of OTA into the proximal tubule epithelium. The proposed MoA is critically assessed with respect to concordance of dose-response of the suggested key events and tumor formation, their temporal association, consistency, and biological plausibility. Uncertainties, data gaps and needs for further research are highlighted.

Degradation of chlorinated nitroaromatic compounds

Chlorinated nitroaromatic compounds (CNAs) are persistent environmental pollutants that have been introduced into the environment due to the anthropogenic activities. Bacteria that utilize CNAs as the sole sources of carbon and energy have been isolated from different contaminated and non-contaminated sites. Microbial metabolism of CNAs has been studied, and several metabolic pathways for degradation of CNAs have been proposed. Detoxification and biotransformation of CNAs have also been studied in various fungi, actinomycetes and bacteria. Several physicochemical methods have been used for treatment of wastewater containing CNAs; however, these methods are not suitable for in situ bioremediation. This review describes the current scenario of the degradation of CNAs.

Gender differences in kidney function

Sex hormones influence the development of female (F) and male (M) specific traits and primarily affect the structure and function of gender-specific organs. Recent studies also indicated their important roles in regulating structure and/or function of nearly every tissue and organ in the mammalian body, including the kidneys, causing gender differences in a variety of characteristics. Clinical observations in humans and studies in experimental animals in vivo and in models in vitro have shown that renal structure and functions under various physiological, pharmacological, and toxicological conditions are different in M and F, and that these differences may be related to the sex-hormone-regulated expression and action of transporters in the apical and basolateral membrane of nephron epithelial cells. In this review we have collected published data on gender differences in renal functions, transporters and other related parameters, and present our own microarray data on messenger RNA expression for various transporters in the kidney cortex of M and F rats. With these data we would like to emphasize the importance of sex hormones in regulation of a variety of renal transport functions and to initiate further studies of gender-related differences in kidney structure and functions, which would enable us to better understand occurrence and development of various renal diseases, pharmacotherapy, and drug-induced nephrotoxicity in humans and animals.

Toxicokinetics of the mycotoxin ochratoxin A in F 344 rats after oral administration

Ochratoxin A (OTA), a mycotoxin produced by several fungi of Aspergillus and Penicillium species, is a nephrotoxin and a renal carcinogen in rodents. This study was performed to investigate the biotransformation and toxicokinetics of this important food contaminant. Male (n=18) and female (n=18) F344 rats were administered a single dose of OTA (0.5 mg/kg b.w.) in corn oil by gavage. Animals (n=3) were sacrificed 24, 48, 72, 96, 672, and 1,344 hours after OTA administration and concentrations of OTA and OTA-metabolites in urine, feces, blood, liver, and kidney were determined by HPLC with fluorescence detection and/or by LC-MS/MS. Recovery of unchanged OTA in urine amounted to 2.1% of dose in males and 5.2% in females within 96 h. In feces, only 5.5% respectively 1.5% of dose were recovered. The major metabolite detected was OTalpha; low concentrations of OTA-glucosides were also present in urine. The maximal blood levels of OTA were observed between 24 and 48 h after administration and were appromixately 4.6 micromol/l in males and 6.0 micromol/l in females. Elimination of OTA from blood followed first-order kinetics with a half-life of approximately 230 h. In liver of both male and female rats, OTA-concentrations were less than 12 pmol/g tissue, with a maximum at 24 h after administration. In contrast, OTA accumulated in the kidneys, reaching a concentration of 480 pmol/g tissue in males 24 h after OTA-administration. Generally, tissue concentrations in males were higher than in females. OTalpha was not detected in liver and kidney tissue of rats administered OTA, and the OTalpha concentrations in blood were low (10-15 nmol/l). The high concentrations of OTA in kidneys of male rats may, in part, explain the organ- and gender-specific toxicity of OTA.

Gender differences in the membrane transport of endogenous and exogenous compounds

Gender differences have been well described in pharmacokinetics and contribute to the interindividual variation in drug disposition, therapeutic response, and drug toxicity. Sex-related differences in the membrane transport of endogenous substrates and xenobiotics have been reported in various organs of the body including kidney, liver, intestine, and brain. These gender-related differences in transport systems could also contribute to interindividual variability in pharmacokinetics and pharmacodynamics. This review will focus on current knowledge of gender-associated differences in the transport of endogenous and exogenous compounds in a variety of body organs and will discuss the implications and the clinical significance of these observations.

Sex hormone-regulated renal transport of perfluorooctanoic acid

The biological half-life (t1/2) of perfluorooctanoic acid (PFOA) in male rats is 70 times longer than that in female rats. The difference is mainly due to the difference in renal clearance (CL(R)), which was significantly reduced by probenecid, suggesting that PFOA is excreted by organic anion transporter(s). Castration of male rats caused a 14-fold increase in the CL(R) of PFOA, which made it comparable with that of female rats. The elevated PFOA CL(R) in castrated males was reduced by treating them with testosterone. Treatment of male rats with estradiol increased the CL(R) of PFOA. In female rats, ovariectomy caused a significant increase in CL(R) of PFOA, which was reduced by estradiol treatment. Treatments of female rats with testosterone reduced the CL(R) of PFOA as observed in castrated male rats. To identify the transporter molecules that are responsible for PFOA transport in rat kidney, renal mRNA levels of organic anion transporter 1 (OAT1), OAT2, OAT3, organic anion transporting polypeptide 1 (oatp1), oatp2 and kidney specific organic anion transporter (OAT-K) were determined in male and female rats under various hormonal states and compared with the CL(R) of PFOA. The level of OAT2 mRNA in male rats was only 13% that in female rats. Castration or estradiol treatment increased the level of OAT2 mRNA whereas treatment of castrated male rats with testosterone reduced it. In contrast to OAT2, mRNA levels of both oatp1 and OAT-K were significantly higher in male rats compared with female rats. Castration or estradiol treatment caused a reduction in the levels of mRNA of oatp1 and OAT-K in male rats. Ovariectomy of female rats significantly increased the level of OAT3 mRNA. Multiple regression analysis suggests that the change in the CL(R) of PFOA is, at least in part, due to altered expression of OAT2 and OAT3.

Regulation of renal tubular secretion of organic compounds

BACKGROUND

Information on the molecular basis underlying organic anion and cation transport in renal tubules has expanded in recent years with the identification and characterization of numerous transporters. However, little is known about the regulation of this transport.

METHODS

Both English and Russian language studies dealing with the regulation of organic ion transport by the kidney have been reviewed.

RESULTS

This review summarizes the literature on the physiological and pharmacological aspects of the regulation of organic ion transport, linking this information where possible to underlying transport mechanisms. Current models of the tubular secretion of organic anions and cations are reviewed. Factors that inhibit or enhance tubular secretion of xenobiotics are described, and their influence on proximal tubule cell transport and function is discussed. Important roles for substrate stimulation, the adrenergic nervous system, numerous hormones, P-glycoprotein, and protein kinase C activity have been identified.

CONCLUSIONS

Despite considerable advances in the understanding of basic transport pathways and mechanisms involved in the tubular secretion of organic compounds, there is still relatively little information on the regulation of this transport. Studies combining the techniques of integrative and cell physiology and molecular biology will provide significant new insights into the pathways regulating the tubular transport of these compounds.

Metabolism of 2,3,5,6-tetrachloronitrobenzene (tecnazene) in rat

1. The metabolic fate of [U-14C]-2,3,5,6-tetrachloronitrobenzene (tecnazene) has been determined in the male and female rat following a single dose of 1 mg/kg and in surgically prepared, bile-duct-cannulated rats following a single oral dose of 135 mg/kg. 2. Radioactivity in the female rat was excreted mainly in urine (82%). The male rat, however, excreted approximately equal amounts of radioactivity in urine and faeces (the latter via bile). 3. The principal metabolic pathway was conjugation with glutathione (GSH) and concomitant nitro-displacement. The GSH-conjugate and related metabolites were excreted in the bile and ultimately in the urine as the mercapturic acid conjugate. The cysteine conjugate underwent beta-lyase-mediated metabolism to yield a thiol that underwent subsequent methylation to the thioanisole followed by S-oxidation. 4. A novel tetrachloromethyldisulphide metabolite was also formed.

Sex-dependent and independent renal excretion of nilvadipine metabolites in rat: evidence for a sex-dependent active secretion in kidney

1. To clarify the mechanism of sex-dependent and independent kidney secretion of major nilvadipine metabolites (3, 7) in rat, renal clearance corrected for protein binding and glomerular filtration rate (GFR) was measured in both sexes. The effect of probenecid, an inhibitor of organic anion transport, on these measurements was also investigated. 2. Clear sex-dependent active secretion was observed in the renal excretion of 3 (3-carboxylic acid pyridine derivative). In the female rat, 3, clearance was approximately 32-fold greater than GFR and was markedly decreased by probenecid. Conversely, in the male rat, renal clearance of 3 was only a fraction of GFR and was unaffected by probenecid. 3. Sex-independent active secretion was observed in the renal excretion of 7 (5-carboxylic acid pyridine derivative). In both sexes of rat 7 clearance was about 22-fold greater than GFR and was markedly reduced by probenecid. 4. A clear presence of sex-dependent and independent active secretion mechanisms in the kidney has been demonstrated in rat. The female rat is able to eliminate 3 and 7 in urine by an active secretion mechanism that is inhibited by probenecid. In the male rat, a transport mechanism for 7 is present, but either lacks or is apparently inactive for 3.

Glutathione conjugation and conversion to mercapturic acids can occur as an intrahepatic process

By catalyzing the reaction of electrophilic compounds with the sulfhydryl group of glutathione, the glutathione S-transferases play physiologically important roles in the detoxication of potential alkylating agents. The glutathione S-conjugates thus formed are transported out of cells for further metabolism by gamma-glutamyltransferase and dipeptidases, ectoproteins that catalyze the sequential removal of the glutamyl and glycyl moieties, respectively. These ectoproteins are not found in all cells, but are localized predominantly to the apical surface of epithelial tissues. The resulting cysteine S-conjugates can be reabsorbed by specific cell types, and acetylated on the amino group of the cysteinyl residue by intracellular N-acetyl-transferases, to form the corresponding mercapturic acids (N-acetylcysteine S-conjugates). Mercapturic acids are then released into the circulation and delivered to the kidney for excretion in urine, or they may undergo further metabolism. Mercapturic acid biosynthesis is generally considered to be an interorgan process, with the liver serving as the major site of glutathione conjugation, and the kidney as the primary site for conversion of glutathione conjugates to cysteine conjugates. Cysteine conjugates formed in the kidney appear to be transported back to the liver for acetylation. This interorgan model of mercapturic acid synthesis is based largely on the interorgan distribution of the enzymes involved in their formation, and in particular of the enzyme gamma-glutamyltransferase. Rats have relatively low hepatic and high renal activities of gamma-glutamyltransferase, the only protein known to initiate the breakdown of glutathione S-conjugates. The low gamma-glutamyltransferase activity in rat liver limits the hepatic degradation of glutathione S-conjugates, particularly after large doses of xenobiotic. In contrast, hepatic gamma-glutamyltransferase is significantly higher in species such as rabbit, guinea pig, and dog, and as a consequence, nearly all of the glutathione and glutathione S-conjugates released by liver cells of these species is degraded within the liver. Recent studies demonstrate that glutathione S-conjugates synthesized within hepatocytes are secreted preferentially across the canalicular membrane into bile, and are broken down within biliary spaces to form cysteine S-conjugates. The latter are then reabsorbed by the liver, N-acetylated to form mercapturic acids, and reexcreted into bile, completing an intrahepatic pathway for mercapturic acid biosynthesis. The contribution of this intrahepatic pathway to overall mercapturate formation is dependent on dose of the electrophile, route of exposure, and the physicochemical properties of the glutathione S-conjugate formed, as well as the tissue distribution and activity of gamma-glutamyltransferase.(ABSTRACT TRUNCATED AT 400 WORDS)

Studies on sex differences in excretion of sulphur derivatives of hexachlorobenzene and pentachloronitrobenzene by rats

The appearance of sex-related differences in the excretion of sulphur derivatives of hexachlorobenzene (HCB) and pentachloronitrobenzene (PCNB) was studied in vitro and in vivo. Sexually immature rats given HCB showed initially no differences in the excretion of N-acetyl-S-(pentachlorophenyl)cysteine, but 5-8 days after weaning the urinary levels of the sulphur derivative began to increase in females until a 10-fold difference between both sexes was established. The studies in vitro and the analysis of tissues after in vivo administration of PCNB showed that conjugation with glutathione and hydrolysis of the conjugates to yield free pentachlorothiophenol do not present sex-related differences. These data tend to reinforce the view that an active renal secretory mechanism probably induced by estrogens during sexual maturation is responsible for the highly efficient excretion of sulphur derivatives of HCB and PCNB by female rats.

Contraluminal para-aminohippurate (PAH) transport in the proximal tubule of the rat kidney. VI. Specificity: amino acids, their N-methyl-, N-acetyl- and N-benzoylderivatives; glutathione- and cysteine conjugates, di- and oligopeptides

In order to evaluate the specificity of the renal contraluminal PAH transport system for amino acids, oligopeptides and their conjugates, the inhibitory potency of these substances against contraluminal [3H] PAH influx has been determined. For this, inhibition of 3H-PAH flux from the interstitium into cortical tubular cells of the rat kidney in situ has been measured. Apparent Ki values were evaluated by a computer program assuming competitive inhibition. Unconjugated amino acids (glycine, cysteine, alanine, leucine, phenylalanine, tyrosine, aspartate, glutamate, arginine, ornithine and lysine) do not inhibit [3H] PAH influx. The very hydrophobic tryptophan, however, does. N-alpha-methylation does not change this behaviour. N-alpha-acetylation does not evoke interaction with the PAH transporter when it occurs with glycine, cysteine (to yield mercapturic acid), arginine, ornithine and lysine. However, it renders alanine, leucine, phenylalanine, tryptophan, L-aspartate moderately, and L-glutamate strongly, inhibitory. The acetylated D-isomers of alanine, leucine and phenylalanine exert a higher inhibitory potency compared with the respective L-isomers. N-alpha-benzoylation of L-lysine is ineffective. N-alpha-benzoylation, however, evokes interaction with the PAH transporter, when it occurs with ornithine less than arginine less than histidine less than glycine = leucine less than alanine = phenylalanine = aspartate = glutamate. Dipeptides interact with the PAH transporter according to their hydrophobicity (Nozaki scale down to 0.9, Fauchère scale up to 1.0). N-acetylation does not change this behaviour. Hydrophobicity also renders oligopeptides, as angiotensin II, inhibitory against PAH transport. Similarly the anionic angiotensin I converting enzyme inhibitors Captopril, Enalapril and Ramipril inhibit contraluminal PAH influx.

Sex differences in the metabolism and excretion of nilvadipine, a new dihydropyridine calcium antagonist, in rats

1. The metabolic profiles of nilvadipine in the urine and bile of male and female rats were studied after i.v. dosing with 1 mg/kg of the 14C-labelled compound. 2. Excretion rates of the dosed radioactivity in male and female rats, respectively, in the first 48 h were 84.1% and 59.1% in bile, 12.0% and 36.9% in urine, and 2.5% and 3.6% in faeces. 3. Comparison of biliary and urinary excretion for each radioactive metabolite after dosing with 14C-nilvadipine, showed marked sex-related differences in the excretion routes of several metabolites. In male rats, metabolite M3, having a free 3-carboxyl group on the pyridine ring, was not excreted in urine, but in female rats urinary excretion of M3 accounted for 4.7% of the dose. One reason for the lower urinary excretion of radioactivity by males than by females was that the main metabolite, M3, was not excreted in the urine of the male rats. 4. To clarify the sex difference in the route of excretion of M3, this metabolite (M3) was given i.v. to rats. No excretion of the metabolite was observed in urine of male rats within 24 h but, in marked contrast, 41.5% of the dose was excreted in urine of females in the same period.

Stimulation by oestradiol of the urinary excretion of perfluorooctanoic acid in the male rat

The urinary excretion of perfluorooctanoic acid (PFOA) was studied in male Wistar rats after castration and oestradiol administration as well as in intact females and males. During the first 24 hr females excreted 72 +/- 5% (N = 6) of a single intraperitoneal dose of PFOA (50 mg/kg) in urine whereas the intact males excreted only 9 +/- 4% (N = 6). After castration followed by oestradiol administration (500 micrograms/kg every 2nd day for 14 days), the males excreted PFOA in urine in similar amounts as the females (68 +/- 14% at 24 hr, N = 10). Oestradiol treatment of non-castrated males produced similar results (61 +/- 19% at 24 hr, N = 10). Also castration without oestradiol administration significantly enhanced the renal PFOA excretion, but not as effectively as oestradiol treatment. After 96 hr, the concentration of PFOA in serum of intact males was 17-40 times higher than in the serum of other groups. PFOA was similarly bound by the proteins in the serum of females and males. Phase II metabolism of PFOA was not shown either in males or females.

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.

Metabolism of hexachloro-1,3-butadiene in mice: in vivo and in vitro evidence for activation by glutathione conjugation

1. The metabolism of 14C-hexachloro-1,3-butadiene (HCBD) was studied in mice and in subcellular fractions from mouse liver and kidney. 2. In the presence of glutathione (GSH), liver microsomes and cytosol transformed HCBD to S-(pentachlorobutadienyl)glutathione (PCBG). PCBG formation in subcellular fractions from mouse kidney was very limited. Oxidative metabolism of HCBD by cytochrome P-450 could not be demonstrated. 3. Cysteine conjugate beta-lyase was present in mitochondria and cytosol from mouse liver and kidney. 4. After an oral dose of 30 mg/kg 14C-HCBD, mice eliminated 67.5-76.7% of dose in faeces; urinary elimination accounted for 6.6-7.6%. 5. Metabolites of HCBD identified are: S-(pentachlorobutadienyl)glutathione in faeces; S-(pentachlorobutadienyl)-L-cysteine, N-acetyl-S-(pentachlorobutadienyl)-L-cysteine and 1,1,2,3-tetrachlorobutenoic acid in urine. 6. The results suggest that conjugation of HCBD with GSH in liver, followed by renal processing of the glutathione S-conjugates and beta-lyase-catalysed formation of reactive intermediates, accounts for the organ specific toxicity of HCBD in mice.

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

The cysteine conjugate beta-lyase mediated metabolism and the mutagenicity of the synthetic cysteine conjugates S-(2-chloroethyl)-L-cysteine (CEC), S-(2-chlorovinyl)-L-cysteine (CVC), S-(1,2,3,3,3-pentachloroprop-1-enyl)-L-cysteine (PCPC), S-(pentachlorophenyl)-L-cysteine (PCPhC), S-(chloro-1,2,2-trifluoroethyl)-L-cysteine (CTFEC), S-benzyl-L-cysteine (SBC) and S-methyl-L-cysteine (SMC) were investigated in Salmonella typhimurium strains TA100, TA2638, TA102 and TA98 to establish structure/activity relationships. Bacterial 100,000 X g supernatants cleaved CTFEC, PCPC, CVC, PCPhC and SBC to pyruvate; pyruvate formation was inhibited by the beta-lyase inhibitor aminooxyacetic acid (AOAA) in all cases. Of the compounds tested, CEC, PCPC and CVC were mutagenic in the Ames-test. CTFEC, PCPhC and SBC failed to increase the number of revertants above control levels. The mutagenicity of PCPC and CVC could be inhibited by AOAA. CEC exerted a potent mutagenic effect in the Ames-test which was not affected by AOAA; CEC was not transformed to pyruvate by bacterial beta-lyase. Neither pyruvate formation nor mutagenicity were observed with SMC. These results indicate that the structure of the substituent on the sulfur atom is an important determinant for the biological activity of cysteine S-conjugates. Electronegative and/or unsaturated substituents are required for beta-lyase catalysed beta-elimination reactions. The formation of chemically unstable thiols, which may be converted to thioacylating intermediates, seems to be a prerequisite for beta-lyase dependent mutagenicity of S-conjugates.

Metabolism of the "mixed" cytochrome P-450 inducer hexachlorobenzene by rat liver microsomes

Hexachlorobenzene (HCB) was metabolised by phenobarbital-induced liver microsomes from male rats to pentachlorobenzene, pentachlorophenol, tetrachloro-1,2-benzenediol and tetrachloro-1,4-benzenediol (1:88:2:9). Metabolites were identified and quantified by electron capture g.l.c. Structures were confirmed by selective ion monitoring g.l.c.-m.s. The formation of pentachlorophenol was dependent on the presence of NADPH and O2 and inhibited by CO, SKF 525A and metyrapone. Conversion of HCB to pentachlorophenol was stimulated by pretreatment of rats with phenobarbital (PB) but not by 3-methylcholanthrene (3-MC), or 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). In contrast, the conversion of pentachlorophenol to tetrachloro-1,4-benzenediol was markedly induced by 3-MC but poorly by PB. HCB, Aroclor 1254 and isosafrole stimulated both hydroxylations. The cytochrome P-450c inhibitor 9-hydroxyellipticine inhibited conversion of pentachlorophenol to tetrachlorobenzenediols by HCB and beta-naphthoflavone induced micromes. In addition to hydroxylation reactions, evidence was obtained for the conjugation of HCB with glutathione catalysed by a microsomal glutathione transferase. Radioactivity from [14C]HCB was bound to microsomal protein during aerobic incubations. Binding was inhibited by GSH and N-acetyl-cysteine. Preliminary studies suggested that the reactive species was derived from tetrachloro-1,4-benzoquinone. No correlation was found between levels of metabolites or covalent binding produced by the two sexes and the marked sex dependent hepatic porphyrogenic and carcinogenic effects of HCB.

Transport of N-acetyl-S-pentachloro-1,3-butadienylcysteine by rat renal cortex

N-acetyl-S-pentachloro-1,3-butadienyl-L-cysteine (PCBD-NAC) is a postulated metabolite derived from glutathione conjugation of hexachloro-1,3-butadiene and is nephrotoxic in the rat. Because PCBD-NAC causes selective necrosis to the pars recta of the proximal tubule, and is an organic anion it might be expected to be transported by the renal organic anion transport system. Rat renal cortical slices were used to characterise the transport. 14C-PCBD-NAC uptake was temperature dependent and reduced by the metabolic inhibitors cyanide and iodoacetate. Probenecid and sulphinpyrazone, specific competitive inhibitors of the anion transport system, and dinitrophenol, a metabolic inhibitor as well as a competitive inhibitor of anion transport, reduced PCBD-NAC transport. Organic cations or uric acid transport inhibitors did not alter PCBD-NAC accumulation by the slices. These data are consistent with the transport of PCBD-NAC by the renal organic anion secretory system.

Fate of hexachlorobenzene in C57BL/10 mice with iron overload

The distribution of radioactivity in male C57BL/10 mice dosed with [14C]hexachlorobenzene (HCB) was followed over 21 days and found to be high in adipose tissue and adrenals, moderate in thymus whereas liver was relatively poorly labelled. A predose of iron (500 mg/kg), which greatly promotes the porphyrogenic action of HCB in this strain, had only a small effect on the distribution of radioactivity in tissues and excreta. Iron induced excretion of urinary metabolites from HCB by C57BL/10 mice but not by the insensitive DBA/2 strain. However, there was no such difference in faecal metabolites, total metabolism was only slightly increased and there was no correlation between liver porphyrin levels and urinary excretion of metabolites by individual mice. At the end of 4 weeks exposure of iron-treated C57BL/10 mice to HCB urinary metabolites fell while porphyrin excretion continued to rise. Thus the considerable sensitisation of the C57BL/10 strain after iron overload to the induction of porphyria by HCB cannot be ascribed simply to enhancement of total metabolism but must be caused either by the formation of a specific undetected metabolite or induction of some other toxic process.