Identification of three sulphur-containing urinary metabolites of styrene in the rat

Comparison of urinary mercapturic acid excretions in users of various tobacco/nicotine products

Urinary mercapturic acids (MAs) are detoxification products for electrophiles occurring in the human body. They are suitable biomarkers of exposure to directly acting electrophilic chemicals or to chemicals which generate the electrophile during its metabolism. We determined the urinary excretion of 19 MAs in habitual users of combustible cigarettes (CCs), electronic cigarettes (ECs), heated tobacco products (HTPs), oral tobacco (OT), and nicotine replacement therapy (NRT) products, and nonusers (NUs) of any tobacco/nicotine products. The 19 MAs are assumed to be physiologically formed primarily from 15 toxicants with three of them belonging to IARC Group 1 (human carcinogen), seven to Group 2A (probable human carcinogen), four to Group 2B (possible human carcinogen), and one to Group 3 (not classifiable as carcinogen). Smoking (CC) was found to be associated with significantly elevated exposure to ethylene oxide (or ethylene), 1,3-butadiene, benzene, dimethylformamide, acrolein, acrylamide, styrene, propylene oxide, acrylonitrile, crotonaldehyde, and isoprene compared with the other user groups and NU. Users of HTPs revealed slight elevation in the MAs related to acrolein, acrylamide, and crotonaldehyde compared with the other non-CC groups. Vaping (EC) was not found to be associated with any of the MAs studied. In conclusion, the determination of urinary MAs is a useful tool for assessing the exposure to toxicants (mainly potential carcinogens) in users of various tobacco/nicotine products. Our data also give cause to clarify the role of vaping (EC) in urinary excretion of DHPMA (precursor: glycidol).

Study of urinary 2-{[2-(acetylamino-2-carboxyethyl]sulfanyl}butanedioic acid, a mercapturic acid of rats treated with maleic acid

Maleic anhydride was reported illegally adulterated into starch to prepare traditional foods for decades in Taiwan. Maleic acid (MA), hydrolyzed from maleic anhydride, could cause kidney damages to animals. The potential health effects due to long-term MA exposures through food consumption have been of great concerns. Assessment of the dietary MA exposures could be very difficult and complicated. One of the alternatives is to analyze an MA-specific biomarker to assess the daily total MA intake. Therefore, this paper aimed to study the mercapturic acid of MA, 2-{[2-(acetylamino)-2-carboxyethyl]sulfanyl}butanedioic acid (MAMA), with our newly-developed isotope-dilution online solid-phase extraction liquid chromatography tandem mass spectrometry (ID-SPE-LC-MS/MS) method. MAMA was first synthesized, purified, and characterized with NMR to reveal two diastereomers and used for developing the analytical method. The method was validated to reveal excellent sensitivity with a LOD at 16.3ng/mL and a LOQ at 20.6ng/mL and used to analyze MAMA in urine samples collected from Sprague-Dawley rats treated with a single dose of 0mg/kg, 6mg/kg, and 60mg/kg (n=5) of MA through gavage. Our results show dose-dependent increases in urinary MAMA contents, and 70% MAMA was excreted within 12h with no gender differences (p>0.05). A half life of urinary MAMA was estimated at 6.8h for rat. The formation of urinary MAMA validates it as a chemically-specific biomarker for current MA exposure. Future study of MA metabolism in vivo will elucidate mechanisms of MAMA formation, and analysis of this marker in epidemiology studies could help to shed light on the causal effects of MA on human.

Styrene Metabolism, Genotoxicity, and Potential Carcinogenicity

This report reviews styrene biotransformation, including minor metabolic routes, and relates metabolism to the genotoxic effects and possible styrene-related carcinogenicity. Styrene is shown to require metabolic activation in order to become notably genotoxic and styrene 7,8-oxide is shown to contribute quantitatively by far the most (in humans more than 95%) to the genotoxicity of styrene, while minor ring oxidation products are also shown to contribute to local toxicities, especially in the respiratory system. Individual susceptibility depending on metabolism polymorphisms and individual DNA repair capacity as well as the dependence of the nonlinearity of the dose-response relationships in the species in question and the consequences for risk evaluation are analyzd.

Effects of styrene and styrene oxide on glutathione-related antioxidant enzymes

Styrene is both hepatotoxic and pneumotoxic in mice. Its mode of action is not clear, but it may be related to oxidative stress including a very large decrease in reduced glutathione (GSH). The current studies evaluated if: (1) the more toxic R-styrene oxide had a greater effect on reduced GSH levels than the less toxic S-styrene oxide, (2) the ratio of reduced to oxidized forms of glutathione was altered by styrene or styrene oxide, (3) other enzymes involved in the oxidant status of the cell, namely glutathione reductase, glutathione peroxidase and gamma-glutamylcysteine synthetase were altered, and (4) lipid peroxidation, as measured by the determination of malondialdehyde, increased. R-Styrene oxide (300mg/kg, ip) caused greater decreases in mouse liver and lung GSH than did S-styrene oxide (300mg/kg, ip). Styrene (600mg/kg, ip) caused decreases in both GSH and GSSG in both liver and lung. Styrene and styrene oxide did not cause significant increases in lipid peroxidation in either liver or lung. Styrene and styrene oxide had minimal effects on glutathione reductase and glutathione peroxidase in liver and lung. Styrene increased gamma-glutamylcysteine synthetase activity. The results suggest that while styrene and its metabolite styrene oxide cause significant decreases in GSH levels, they have little effect on the enzymes glutathione reductase and glutathione peroxidase and that in response to decreased glutathione levels there is an increase in its synthesis via induction of gamma-glutamylcysteine synthetase activity.

Mercapturic acids in the biological monitoring of occupational exposure to chemicals

This paper reviews several procedures for determination of mercapturic acids in urine. Special attention was paid to methods useful in relation to human exposure to industrial pollutants, without any description for less sensitive methods used in animal research. Gas chromatographic and liquid chromatographic procedures were considered together with the little information available about thin layer chromatography and immunochemical techniques. After a description of the main industrial pollutants which lead to synthesis of their specific mercapturic acids, the methods for analysing these products are synthetically reported. The comparison among difficulties in sample preparation, complexity of instrumentation and their cost/benefit ratio are discussed.

Liquid chromatography/electrospray tandem mass spectrometry characterization of styrene metabolism in man and in rat

Liquid chromatography with electrospray tandem mass spectrometry was used to characterize the metabolism of styrene in man and in rat. To improve identification and characterization of minor styrene metabolites, rats were co-exposed to styrene and styrene-d(8). In addition to the main styrene metabolites, mandelic acid and phenylglyoxylic acid, and specific mercapturic acids, phenylhydroxyethylmercapturic acids (PHEMAs), other minor metabolites, including phenylglycine, N-acetyl-S-(phenacyl)cysteine, 4-vinylphenol and styreneglycol conjugates (glucuronides and sulfates) were identified and determined both in human and rat urine. Phenylglycine and N-acetyl-S-(phenacyl)cysteine have been hypothesized to occur, but never detected in human or rat urine after styrene exposure. 4-Vinylphenol and styrene glycol had already been recognized as styrene metabolites, but never determined as intact glucuronide and sulfate conjugates. Failure to identify 1- and 2-phenylethanol conjugates suggests that phenylethanol might be an intermediate metabolite, but it is not a conjugated catabolite. A method for the simultaneous determination of mandelic acid, phenylglyoxylic acid, phenyglycine and the four PHEMA diastereoisomers has been developed and validated. For those glucuronide and sulfate conjugates whose standards are not commercially available, a method for semiquantitative analysis, based on the use of structurally similar compounds as standards, has been developed. This approach was found to be valid for the determination of 4-vinylphenol glucuronide and 4-vinylphenol sulfate.

Stereochemistry of styrene biotransformation

Metabolism of styrene, an important industrial monomer, is reviewed. Attention is focused on the stereoselectivity of its oxidation to 7,8-styrene oxide as well as on further stereoselective biotransformation by hydrolytic and mercapturic acid pathway. Toxic effects such as mutagenicity, genotoxicity, hepatotoxicity, and pneumotoxicity may be related to the ratio of styrene oxide enantiomers at the target site. In rats formation of the less mutagenic (S)-styrene oxide and a faster detoxication of the (R)-enantiomer is favored. In mice metabolic activation of styrene favors the formation of (R)-styrene oxide but this more toxic enantiomer is detoxified faster, so that a nearly racemic styrene oxide results. Stereochemistry of biotransformation can contribute to the species differences in toxicity but can hardly be interpreted as a crucial factor. Due to lack of relevant data the stereochemistry of human metabolism cannot be interpreted in relation to the toxic effects.

A new method for the analysis of styrene mercapturic acids by liquid chromatography/electrospray tandem mass spectrometry

A new method based on liquid chromatography/tandem mass spectrometry has been developed for the direct determination of specific urinary mercapturic acids arising from the conjugation of (R)-and (S)-enantiomers of styrene 7,8-oxide with glutathione (GSH), i.e. (R,R)- and (S,R)-N-acetyl-S-(1-phenyl-2-hydroxyethyl)cysteine (R,R-M1 and S,R-M1) and (R,R)- and (S,R)-N-acetyl-S-(2-phenyl-2-hydroxyethyl)-cysteine (R,R-M2 and S,R-M2). The four diastereoisomers were separated on a C18-DB (7.5 cm, 3 microm) column using variable proportions of 20 mM aqueous ammonium formate buffer and methanol at a flow-rate of 0.5 mL/min. The analytes were ionized by electrospray, in negative-ion mode. Operating in selected-reaction monitoring mode, linearity of the MS response versus analyte concentration was established over 4 orders of magnitude, the detection limits being 0.7-1.0 microg/L for all the mercapturates. Precision of the method determined at 50 microg/L (n = 12), expressed as relative standard deviation, was respectively 3.1, 4.8 and 6.9% within the run, intra-day and inter-day. The corresponding figures at 1.0 mg/L (n = 12) were respectively 2.0, 3.6 and 5.5%. The method was applied to the quantitative analysis of conjugated metabolites in urine samples from workers occupationally exposed to styrene. The diastereoisomers R,R-M1 and S,R-M2 accounted respectively for 50 and 40% of total mercapturates, whereas the proportion of R,R-M2 was 7% and only minor amounts of S,R-M1 were detectable. Styrene mercapturates represented a minor fraction of total styrene metabolites, less than 1% on average. The ratio mercapturates/main metabolites (mandelic + phenylglyoxylic acid) showed a bimodal distribution, the medians of the two subgroups being 0.2 and 1%, respectively. Such subgroups are probably characterized by the genetic polymorphisms of the drug-metabolizing enzymes to be identified.

S-[(1 and 2)-phenyl-2-hydroxyethyl]cysteine-induced alterations in renal mitochondrial function in male Fischer-344 rats

Previous studies from our laboratory have shown that mitochondrial dysfunction may be an important early event in S-[(1 and 2)-phenyl-2-hydroxyethyl]cysteine (PHEC)-induced cytotoxicity in isolated rat renal proximal tubules. The present study has therefore examined in more detail PHEC-induced mitochondrial dysfunction, both in vivo and in vitro, using isolated renal cortical mitochondria. Renal cortical mitochondria isolated from PHEC-treated rats in vivo showed depressed effects on the mitochondrial respiration and oxidative phosphorylation in both a dose (0, 250, and 500 micromol/kg iv)- and time (0-24 h)-dependent manner in the presence of both succinate (Site 2) and malate plus alpha-ketoglutarate (Site 1) as respiratory substrates, with initial significant depression occurring as early as 4 h following treatment with 500 micromol PHEC/kg. Similar mitochondrial dysfunctions were observed in vitro in concentration- and time-dependent manners with both respiratory substrates. PHEC also caused a marked dose-dependent inhibition of mitochondrial succinate dehydrogenase and NADH cytochrome c reductase activities both in vivo and in vitro, with initial inhibition occurring as early as 4 h after in vivo administration and 45 min after exposure to PHEC in vitro, while the NADH dehydrogenase activity was not considerably inhibited. The mitochondrial ATPase activity was significantly decreased 4 and 24 h following treatment with PHEC (500 micromol/kg). These results suggest that PHEC exerts its inhibitory effect on the mitochondrial respiration and oxidative phosphorylation through the action on the mitochondrial electron transport chain. PHEC significantly reduced the activity of adenine nucleotide translocase as well as the net uptake of substrates by mitochondria without affecting their efflux within 2-4 h after its injection (500 micromol/kg). On the other hand, significant renal damage, as assessed by morphological study, appeared as early as 24 h following such treatment. The observation of similar effects after both in vivo and in vitro exposures may suggest that the effect on mitochondria may have a pathogenic role in PHEC-induced renal injury in rats. PHEC produces mitochondrial toxicity that results from an inactivation of mitochondrial anionic substrate transporters as well as from an inhibition of activities of adenine nucleotide translocase and dehydrogenases.

Evaluation of genotoxic potential of styrene in furniture workers using unsaturated polyester resins

Styrene is a widely used chemical, mostly in making synthetic rubber, resins, polyesters, plastics and insulators. Increasing attention has been focused on this compound since experiments using cytogenetic end-points have implicated styrene as a potential carcinogen and mutagen. In order to perform biological monitoring of genotoxic exposure to styrene monomer, we evaluated the urinary thioether (UT) excretion, and sister chromatid exchanges (SCEs) and micronuclei (MN) in peripheral lymphocytes from 53 furniture workers employed in small workplaces where polyester resin lamination processings were done and from 41 matched control subjects. The mean air concentration of styrene in the breathing zone of workers was 30.3 ppm. As a metabolic marker for styrene exposure, mandelic acid + phenylglyoxylic acid was measured in the urine and the mean value was 207 mg/g creatinine. The mean +/- SD value of UT excretions of workers was 4.43 +/- 3.42 mmol SH-/mol creatinine and also mean UT for controls was found to be a 2.75 +/- 1.78 mmol SH-/mol creatinine. The mean +/- SD/cell values of SCE frequency in peripheral lymphocytes from the workers and controls were 6.20 +/- 1.56 and 5.23 +/- 1.23, respectively. The mean +/- SD frequencies (%o) of MN in the exposed and control groups were 1.98 +/- 0.50 and 2.09 +/- 0.35, respectively. Significant effects of work-related exposure were detected in the UT excretion and SCEs analyzed in peripheral blood lymphocytes (p < 0.05 and p < 0.01, respectively). The MN frequency in lymphocytes from the styrene-exposed group did not differ from that in the controls (p > 0.05). Effect of smoking, age and duration of exposure on the genotoxicity parameters analyzed were also evaluated. In conclusion, although our data do not demonstrate a dose-response relationship, they do suggest that styrene exposure was evident and that this styrene exposure may contribute to the observed genotoxic damage in furniture workers.

Excretion of N-acetyl-S-(1-phenyl-2-hydroxyethyl)-cysteine and N-acetyl-S-(2-phenyl-2-hydroxyethyl)-cysteine in workers exposed to styrene

Styrene (S) has been shown to be responsible for neurotoxic effects, including behavioural changes and neuroendocrine disturbances. The initial step of S metabolism is conversion to styrene 7,8-epoxide (SO), which is present in two enantiomeric forms [(R)(+)-SO and (S)(-)-SO]; this electrophilic intermediate is considered to be directly responsible for most toxic effects of S. The major urinary metabolites derived from the biotransformation of SO in man are mandelic acid (MA) and phenylglyoxylic acid (PGA). In rats an alternative pathway has been demonstrated, which involves the conjugation of SO to glutathione (GSH), leading to the excretion of two specific mercapturic acids, N-acetyl-S-(-(1-phenyl-2-hydroxyethyl)-cysteine [M1] and N-acetyl-S-(2-phenyl-2-hydroxy-ethyl)-cysteine [M2]; a close relationship has been found between exposure to S and urinary excretion of M1 and M2 in rats. As a consequence of the chiral nature of SO, both M1 and M2 consist of two diastereoisomers (M1-'R', M1-'S', M2-'R' and M2-'S'). Early reports have shown that the conversion of S to mercapturic acids is much lower in man (below 1% of the absorbed dose) than in rats (about 10%). We propose an analytical method for the determination of urinary M1 and M2 in man, which involves a urine clean-up by a chromatographic technique with a short reversed-phase pre-column; purified samples are then deacetylated with porcine acylase and deproteinized by centrifugal ultrafiltration. A derivatization is then performed with o-phthaldialdehyde and 2-mercaptoethanol and the fluorescent derivatives are separated on a reversed-phase analytical column. The mobile phase consists of acetate buffer and methanol mixed at variable proportions, the fluorescence detector is set at 330 nm (exc.) and 440 nm (em.). M1-'S' and M1-'R' are separated (retention times = 52.8 and 73.7 min, respectively) while the diastereoisomers of M2 coelute as a single peak at 70.5 min. The detection limit is about 7 micrograms/l, the coefficients of variation are below 7% and the error percentages are less than 6%. The method was applied to 25 urine samples from workers exposed to S: significant correlations were found between mercapturic acids and MA and PGA, the best correlation being between M2 and PGA (r = 0.79). Urine samples form unexposed subjects showed no detectable amounts of the analytes. A high stereoselectivity is shown by the enzymes involved in the metabolism of S to mercapturic acids: M1-'S', which derives from (S)-SO, is excreted in much higher amounts than M1-'R', which derives from (R)-SO.

The evidence for conjugated mandelic and phenylglyoxylic acids in the urine of rats dosed with styrene

Male Wistar rats were dosed intraperitoneally with styrene (400 mg/kg). Urine samples were collected over phosphate buffer, pH 6.5 for 24 h. Excretion of mandelic (MA) and phenylglyoxylic acid (PGA) amounted to 1.66 +/- 0.62 and 5.21 +/- 2.44% of dose, respectively, as determined by ion-pair HPLC. After acidic hydrolysis, the amount of MA and PGA found in urine increased to 2.10 +/- 0.84 and 6.81 +/- 3.20% (mean +/- S.D.; n = 7), respectively. A similar increase was observed after alkaline hydrolysis of urine samples. Differences between hydrolysed and non-hydrolysed samples were significant in the paired t-test (P < 0.05). Further, urine samples were fractionated by HPLC. Fractions were subjected to acidic hydrolysis and analysed by HPLC and GC/MS. Both MA and PGA were detected in the fraction which did not contain any of these metabolites before hydrolytic treatment. Thus, MA and PGA, which are used as biomarkers of exposure to styrene, form hydrolysable conjugates in the rat. At least a minor part of the total urinary MA and PGA is bound in these conjugates.

Determination of urinary mercapturic acids of styrene in man by high-performance liquid chromatography with fluorescence detection

A method for the determination of urinary N-acetyl-S-(1-phenyl-2-hydroxyethyl)-L-cysteine (M1) and N-acetyl-S-(2-phenyl-2-hydroxyethyl)-L-cysteine (M2) in man was developed. Clean-up of urine samples was obtained by a chromatographic technique, using a short reversed-phase precolumn; purified samples were then deacetylated with porcine acylase I for 16 h at 37 degrees C and deproteinized by centrifugal ultrafiltration. Derivatization was performed with o-phthaldialdehyde and 2-mercaptoethanol and the fluorescent derivatives were separated on a reversed-phase analytical column with a gradient mobile phase consisting of 50 mM acetate buffer (pH 6.5) and methanol. The retention times of the diastereoisomers of M1 (M1-"S" and M1-"R") were 52.8 and 73.7 min, respectively: M2 diastereoisomers eluted as a single peak at 70.5 min. The fluorescence detector was set at 330 nm (excitation) and 440 nm (emission). The detection limit (at a signal-to-noise ratio of three) was about 7 micrograms/1. The method was applied to 25 urine samples from workers exposed to styrene. A relationship was found between urinary mandelic and phenylglyoxylic acids and mercapturic acids specific for styrene. Urine samples from ten non-exposed subjects showed no detectable amounts of analytes.

Biotransformation of diethenylbenzenes, V. Identification of urinary metabolites of 1,2-diethenylbenzene in the rat

1. Biotransformation of 1,2-diethenylbenzene (1) in rat was studied. Five urinary metabolites were isolated by extraction of acid hydrolysed urine and identified by nmr and mass spectroscopy, namely, 1-(2-ethenylphenyl)ethane-1,2-diol (2) 2-ethenylmandelic acid (3), 2-ethenylphenylglyoxylic acid (4), 2-ethenylphenylacetylglycine (5) N-acetyl-S-[1-(2-ethenylphenyl)-2-hydroxyethyl]cysteine (6) and N-acetyl-S-[2-(2-ethenylphenyl)-2-hydroxy-ethyl]cysteine (7). 2. In addition, minor metabolites, namely, 2-ethenylbenzoic acid (8) and 2-ethenylphenyl-acetic acid (9) were identified by glc-mass spectral analysis of the hydrolysed urine extract treated subsequently with diazomethane, hydroxylamine and a trimethyl-silylating reagent. Several compounds, which could arise from biotransformation of both ethenyl groups in the molecule of 1, were detected but not identified unequivocally. 3. A glucuronide was detected by tlc analysis of urine as a blue spot after spraying with naphthoresorcinol. Compounds showing molecular fragments indicating the glucuronide moiety were also detected by glc-mass spectroscopy in non-hydrolysed urine samples. 4. The total thioether excretion amounted to 5.3 +/- 2.4, 5.1 +/- 3.4 and 5.0 +/- 1.9% of the dose at 500, 300 and 100 mg/kg, respectively (mean +/- SD; n = 5). 5. Like styrene and other diethenylbenzene isomers, 1,2-diethenylbenzene is metabolically activated to a reactive epoxide intermediate, 2-ethenylphenyloxirane (10), which is further converted to the urinary metabolites mentioned above. The main detoxification pathways are hydrolysis to the glycol 2 followed by several oxidation steps, and conjugation with glutathione. The latter reaction is both regioselective and stereoselective. 6. The ratio of mercapturic acids 6:7 was 83:17. Each regioisomer consists of two diastereomers which show distinct resonance signals in the 13C-nmr. The diastereomer ratio was 82:28 and 79:21 for 6 and 7 respectively.

Review of the metabolic fate of styrene

Styrene and styrene oxide have been implicated as reproductive toxicants, neurotoxicants, or carcinogens in vivo or in vitro. The use of these chemicals in the manufacture of plastics and polymers and in the boat-building industry has raised concerns related to the risk associated with human exposure. This review describes the literature to date on the metabolic fate of styrene and styrene oxide in laboratory animals and in humans. Many studies have been conducted to assess the metabolic fate of styrene in rats, and investigations on the metabolism of styrene in humans have been of considerable interest. Limited research has been done to assess metabolism in the mouse. The metabolism of styrene to styrene oxide and further conversion to styrene glycol (via epoxide hydrolase), mandelic acid, and phenylglyoxylic acid has been given considerable attention, and is considered to be the major pathway of activation and detoxication for humans. While the hydrolysis of styrene oxide to styrene glycol historically has been the favored pathway for the rat, studies in more recent years have indicated that glutathione conjugation also is a viable and significant pathway for both the rat and the mouse. This pathway has not been established in humans. Mandelic acid and phenylglyoxylic acid have been used as urinary markers of exposure in humans exposed to styrene. Extensive investigations have been conducted on the kinetics of styrene and styrene oxide in rodents. In people, the kinetics of styrene and styrene oxide in the blood of occupationally exposed workers and volunteers have been determined. Pharmacokinetic models developed in the last decade have become increasingly complex, with the most recent physiologically based model describing the kinetics of styrene and styrene oxide. This model shows pronounced species differences in sensitivity coefficients for styrene or styrene oxide between mice, rats, and humans, where mice are the more sensitive species to the Vmax for both epoxide hydrolase and monooxygenase. This result is particularly interesting in light of the recent findings of extensive mortality and hepatotoxicity for mice exposed to relatively low levels of styrene (250 to 500 ppm), while rats and humans exhibit only nasal and eye irritations at exposure concentrations well above 500 ppm.

Cytogenotoxicity of N-acetyl-S-(1/2-phenyl-2-hydroxyethyl)-cysteine (NAPEC) in cultured human blood lymphocytes

N-Acetyl-S-(1/2-phenyl-2-hydroxyethyl)-cysteine (NAPEC) is a cysteine conjugate derived from the glutathione conjugate of styrene oxide. The dose- and time-dependent effects of NAPEC on SCEs and cell kinetics were studied in cultured human blood lymphocyte in vitro. Different concentrations of NAPEC (0-1500 microM) were added into the lymphocyte cultures. After 36 h of exposure, both the induction of SCEs and cell-cycle delay were increased with increasing concentrations of NAPEC. When the lymphocyte cultures were exposed to 1000 microM NAPEC for 22, 36 and 72 h during a total of 72-h culture period, no significant differences in the induction of SCEs or cell-cycle delay were noticed due to 3 exposure times. These results suggest that NAPEC possesses the potential to induce SCEs and to inhibit cell-cycle progression and such potential seems to be independent of duration of exposure to NAPEC.

DNA adduct formation by 12 chemicals with populations potentially suitable for molecular epidemiological studies

DNA adduct formation, route of absorption, metabolism and chemistry of 12 hazardous chemicals are reviewed. Methods for adduct detection are also reviewed and approaches to sensitivity and specificity are identified. The selection of these 12 chemicals from the Environmental Protection Agency list of genotoxic chemicals was based on the availability of information and on the availability of populations potentially suitable for molecular epidemiological study. The 12 chemicals include ethylene oxide, styrene, vinyl chloride, epichlorohydrin, propylene oxide, 4,4'-methylenebis-2-chloroaniline, benzidine, benzidine dyes (Direct Blue 6, Direct Black 38 and Direct Brown 95), acrylonitrile and benzyl chloride. While some of these chemicals (styrene and benzyl chloride, possibly Direct Blue 6) give rise to unique DNA adducts, others do not. Potentially confounding factors include mixed exposures in the work place, as well the formation of common DNA adducts. Additional research needs are identified.

Biotransformation of diethenylbenzenes. III: Identification of metabolites of 1,3-diethenylbenzene in rat

1. Biotransformation of 1,3-diethenylbenzene (1) in rat gave four major metabolites, namely, 3-ethenylphenylglyoxylic acid (2), 3-ethenylmandelic acid (3), N-acetyl-S-[2-(3-ethenylphenyl)-2-hydroxyethyl]-L-cysteine (4) and N-acetyl-S-[1-(3-ethenylphenyl)-2-hydroxyethyl]-L-cysteine (5) were isolated from urine and identified by n.m.r. and mass spectrometry. 2. Four minor metabolites, 3-ethenylbenzoic acid (6), 3-ethenylphenylacetic acid (7), 3-ethenylbenzoylglycine (8) and 2-(3-ethenylphenyl)ethanol (9) were identified by g.l.c.-mass spectrometric analysis of urine extract derivatized in two different ways. 3. All identified metabolites are derived from 3-ethenylphenyloxirane (10), a reactive metabolic intermediate. No product of any metabolic transformation of second ethenyl group has been identified. However, several minor unidentified metabolites were detected by g.l.c.-mass spectrometry. 4. Total thioether excretion in 24 h urine after a single i.p. dose of 1 amounted to 28.3 +/- 3.5 dose (mean +/- SD). No significant differences in the thioether fraction were observed in the dose range 100-300 mg/kg. 5. Thioether metabolites consisted mainly of mercapturic acids 4 and 5. The ratio of metabolites 5 to 4 was 62:38. Each mercapturic acid consisted of two diastereomers. Their ratio, as determined by quantitative 13C-n.m.r. measurement was 95:5 and 79:21 for mercapturic acids 4 and 5, respectively.

The applicability of the measurement of urinary thioethers. A study of humans exposed to styrene during diet standardization

The excretion of thioethers was measured in the urine of 6 volunteers, who were experimentally exposed to styrene, and 18 styrene workers. In addition, 12 clerks (non-smokers) and 12 sheet-metal workers (smokers) served as control groups. Diet was standardized during the experiments. Thioethers were measured by a spectrophotometric method. The volunteers were exposed to styrene, 210 mg/m3, for 2h at a 50-W workload. An increase in thioether excretion was observed; the largest was in the urine samples collected between 0.5 and 5 h after the end of the exposure. After 43 h the excretion of thioethers was close to the pre-exposure level (3.5 mmol/mol creatinine). About 1% of the styrene absorbed was detected as thioethers in urine, which is only about 1/10 of the conversion reported for rats. From excretion rate curves a half-life of about 11 h was calculated for styrene thioethers. The styrene workers were employed at two plants. The average exposure to styrene (time-weighted average 8 h) was estimated to be about 115 mg/m3 (smokers in plant A), 55 mg/m3 (non-smokers in plant A) and less than or equal to 10 mg/m3 (non-smokers in plant B). The excretion of thioethers in exposed workers at plant A was higher by 2-4 mmol/mol creatinine than that in non-exposed controls. In plant B, where exposure was lower, an increase in that amount of thioethers excreted in the urine by exposed workers was less pronounced, and was statistically significant only when post-shift samples were compared with pre-shift samples.(ABSTRACT TRUNCATED AT 250 WORDS)

In vivo nephrotoxic action of an isomeric mixture of S-(1-phenyl-2-hydroxyethyl)glutathione and S-(2-phenyl-2-hydroxyethyl)glutathione in Fischer-344 rats

An isomeric mixture of S-[(1 and 2)-phenyl-2-hydroxyethyl]glutathione (PHEG), a glutathione conjugate of styrene, is moderately nephrotoxic. Its in vivo nephrotoxicity was characterized by significant elevations in the urinary excretion of glucose, gamma-glutamyl transpeptidase, glutamate dehydrogenase, N-acetyl-beta-D-glucosaminidase and lactic dehydrogenase 24 h after an i.v. administration of PHEG (0.5 mmol/kg) in male Fischer-344 rats. The histologic alterations consisted of moderate tubular damage with proximal tubule vacuolization and accumulation of tubular cast material, indicating an early sign of tubular necrosis. The data suggest that nephrotoxic injury induced by PHEG lies preferentially at the tubular region of the rat kidney involving several subcellular targets. The nephrotoxicity of PHEG was blocked by acivicin, a specific inhibitor of gamma-glutamyl transpeptidase, by phenylalanylglycine, an inhibitor of cysteinylglycine dipeptidase, as well as by probenecid, a competitive inhibitor of renal organic anion transport system. On the other hand, pretreatment with aminooxyacetic acid, a specific inhibitor of renal cysteine conjugate beta-lyase, failed to inhibit the nephrotoxicity of this glutathione conjugate. Similarly, prior administration of alpha-ketobutyrate, an inducer of renal cysteine conjugate beta-lyase, failed to potentiate its nephrotoxicity, suggesting an insignificant role of beta-lyase in such toxicity. A modest decline in renal cellular GSH due to PHEG but without any concomitant oxidation of GSH to GSSG and without any increase in lipid peroxidation indicates that oxidative stress may not be an important mechanism of its nephrotoxicity. Therefore, the following steps at least, are involved in the development of its nephrotoxicity: (1) renal tubular accumulation of PHEG via a probenecid-sensitive transport process; and (2) its renal metabolism via gamma-glutamyl transpeptidase and cysteinylglycine dipeptidase to the corresponding cysteine-S-conjugate.

Glutathione conjugation of styrene 7,8-oxide enantiomers by major glutathione transferase isoenzymes isolated from rat livers

Male Sprague-Dawley rat liver cytosol mediated regioselective conjugation of styrene 7,8-oxide (STO) enantiomers with glutathione in completely trans-ring-opening manner to afford (1S)-S-(1-phenyl-2-hydroxyethyl)glutathione and (2R)-S-(2-phenyl-2-hydroxyethyl)glutathione in the ratio 22:1 for (R)-STO and also to afford (1R)-S-(1-phenyl-2-hydroxyethyl)glutathione and (2S)-S-(2-phenyl-2-hydroxyethyl)glutathione in the ratio 12:1 for (S)-STO. In the above cytosolic reactions, (R)-STO was conjugated 1.8 times faster than (S)-STO, while the (R)- to (S)-ratio in rate of the conjugation was 2.7 when racemic STO was used as a substrate. A kinetic study, carried out by using six major glutathione transferase (GST) isoenzymes isolated from the cytosol, indicated that GSTs 3-3, 3-4 and 4-4 (class mu enzymes) had much higher Kcat/Km values towards both STO enantiomers than the other three major isoenzymes, GSTs 1-1, 1-2 and 2-2 (class alpha enzymes). All the class mu enzymes mediated preferential glutathione conjugation of (R)-STO to (S)-STO. On the contrary, the class alpha enzymes catalysed the conjugation of (S)-STO preferentially to (R)-STO. The kinetic study strongly suggested that GSTs determining the higher enantioselectivity towards (R)-STO in the rat liver cytosol were the class mu enzymes, especially GST 3-3, which had the highest Kcat/Km value towards (R)-STO as well as the highest (R) to (S) ratio in the enantioselectivity among the six isoenzymes examined. GST 7-7, isolated as a major enzyme from the liver cytosol of the animals bearing hepatic hyperplastic nodules which were induced by chemical carcinogens, catalysed preferential GSH conjugation of (S)-STO to (R)-STO.

Metabolism and hepatorenal toxicity due to repeated exposure to styrene in spontaneously hypertensive rats (SHR)

Groups of adult male rats (5 rats per group), either normotensive (WKY) or spontaneously hypertensive (SHR), were exposed by inhalation to 0, 821, and 3018 ppm styrene, 5 h per day for 3 consecutive days. After the exposure, the urines were collected for 24 h and the animals were then sacrificed. The various biochemical parameters of hepatorenal toxicity due to styrene as well as its urinary metabolites were measured. Hepatotoxicity due to styrene was not further increased at any exposure level due to hypertension. However, repeated exposure of SHR rats to 3018 ppm styrene showed significant increases in the urinary excretion of gamma-glutamyl transpeptidase, proteins, and volume of urine, compared to WKY treated rats, whereas no such changes were observed due to repeated exposure to 821 ppm styrene. Studies of in vivo metabolism of styrene at higher exposure level showed significant decrease in the urinary excretion of mandelic, phenylglyoxylic, and hippuric acids in SHR rats compared to WKY-treated rats, suggesting an inhibition of deactivation of styrene reactive intermediate involving the epoxide hydrase pathway due to hypertension. At the same time, a significant increase in the urinary excretion of a potential nephrotoxic metabolite of styrene (e.g., mercapturates or thioethers) was observed in SHR-treated rats when compared to WKY-treated rats. These results demonstrate that spontaneous hypertension has the potential to further increase the nephrotoxicity due to repeated exposure to styrene, and the metabolism of styrene plays an important role in modifying such toxicity in the hypertensive state.

Biotransformation of diethenylbenzenes. I. Identification of the main urinary metabolites of 1,4-diethenylbenzene in the rat

1. Biotransformation of 1,4-diethenylbenzene (1) in rat was studied. Six urinary metabolites, namely, N-acetyl-S-[2-(4-ethenylphenyl)-2-hydroxyethyl]-L-cysteine (3), N-acetyl-S-[1-(4-ethenylphenyl)-2-hydroxyethyl]-L-cysteine (4), N-acetyl-S-[1-(4-formylphenyl)-2-hydroxyethyl]-L-cysteine (5), 1-(4-ethenylphenyl)ethane-1,2-diol (6), 4-ethenylbenzoic acid (9) and 4-ethenylbenzoyl-glycine (12) were isolated and identified by n.m.r. and mass spectrometry. 2. G.l.c.-mass spectral analysis of the methylated urine extract allowed the identification of four other metabolites, as 4-ethenylphenylacetic acid (11), 4-ethenylphenylacetylglycine (13), 4-ethenylmandelic acid (7), and 4-ethenylphenylglyoxylic acid (8). 3. The structures of the identified metabolites indicate that the main reactive intermediate in the metabolism of 1 is 4-ethenylphenyloxirane (2). The first step in the biotransformation of 1, formation of an oxirane, is very similar to the metabolic activation of styrene. However, subsequent steps lead not only to analogues of styrene metabolites but also to oxidation of the second ethenyl group leading to compound(s) which may contribute to the toxicity of 1, e.g. to the aldehyde 5. 4. Rats dosed with a single i.p. dose of 1 excreted nearly 5.6% of the dose as the glycine conjugate 12, irrespective of the dose. 5. In contrast, the total thioether fraction decreased significantly with increasing dose, being 23 +/- 3, 17 +/- 5 and 12 +/- 1% of dose at 100, 200 and 300 mg/kg, respectively (mean +/- SD).

Review of the toxicology of styrene

Styrene is used in the production of plastics and resins, which include polystyrene resins, acrylonitrile-butadiene-styrene resins, styrene-acrylonitrile resins, styrene-butadiene copolymer resins, styrene-butadiene rubber, and unsaturated polyester resins. In 1985, styrene ranked in the top ten of synthetic organic chemicals produced in the U.S. This review focuses on various aspects of styrene toxicology including acute and chronic toxicity, carcinogenicity, genotoxicity, pharmacokinetics, effects on hepatic and extrahepatic xenobiotic-metabolizing enzymes, pharmacokinetic modeling, and covalent interactions with macromolecules. There appear to be many similarities between the toxicity and metabolism of styrene in rodents and humans. Needed areas of future research on styrene include studies on the molecular dosimetry of styrene in terms of both hemoglobin and DNA adducts. The results of such research should improve our ability to assess the relationship between exposure to styrene and surrogate measures of "effective dose", thereby improving our ability to estimate the effects of low-level human exposures.

Unusual conjugates in biological profiles originating from consumption of onions and garlic

After consumption of onions or garlic, biological profiles of human urine samples show, in the methylated conjugate fraction, peaks corresponding to the methylates of N-acetyl-S-(2-carboxypropyl) cysteine (1), N-acetyl-S-allylcysteine (2) and hexahydrohippuric acid (3). The compounds 1 and 2 are metabolites of peptides introduced with onions or garlic into the body.

Determination of metabolites (including thioethers) of mutagens and/or carcinogens as exposure indicators

Biological assessment of exposure to environmental hazards offers the potential for: (1) evaluation of exposure to prevent health impairment and (2) early detection of health effects. Two main methods of assessment can be used: (1) evaluation of the biological specimen for the exposed chemical or its metabolites and (2) measurement of the biological or clinical effects. There has been rapid improvement in the sensitivity of analytical techniques in the last decade and biological specimens of trace quantity can now be used for routine determinations. In this paper the current practice for monitoring populations exposed to benzene, styrene trichloroethylene, tetrachloroethylene and to some mutagens/ carcinogens are described. The practical concerns associated with routine urinary analyses, such as sample collection, sample preparation and interpretation of results are also discussed.

Metabolism of vinyltoluene in the rat: effect of induction and inhibition of the cytochrome

Metabolism of vinyltoluene was studied in rats after injecting different doses of vinyltoluene. The main metabolites excreted in urine of rats after vinyltoluene treatment were: thioethers, p- methylmandelic acid, p- methylphenylglyoxylic acid, p- methylbenzoyl glycine, p- methylphenylacetyl glycine and p- vinylbenzoyl glycine. The highest excretion rate was obtained with doses of 50, 250 and 500 mg/kg already within the first six ours. However, the dose of 500 mg/kg did not increase the excretion rates of these metabolites compared to the dose of 250 mg/kg suggesting that the metabolic pathways begin to be saturated with the amount of 250 mg/kg. At the dose of 50 mg/kg 55% of the dose was detected as urinary metabolites within 23 hr, mainly within the first 6 hr. The amounts of the excreted metabolites expressed as per cent of the injected dose (250 mg/kg or 500 mg/kg) were lower than that caused by 50 mg/kg, and a noticeable amount of the total sums were excreted within 11-23 hr suggesting that the excretion was still continued with the doses of 250 and 500 mg/kg 23 hr after the injection. The excretion of all analyzed metabolites of vinyltoluene was prevented by the pretreatment of the rats with 1- phenylimidazole , an inhibitor of cytochrome P-450 monoxygenases. This indicates that these metabolites were formed as catalyzed by cytochrome P-450. The structures of the analyzed metabolites suggest that the main reactive intermediate of vinyltoluene is vinyltoluene-7,8-oxide. Furthermore, the amounts of the excreted metabolites showed that the main detoxification pathways of v inyltoluene -7,8-oxide were the conjugation with reduced glutathione and hydration to diols. Pre-treatment of the rats with PCBs increased the excretion rates of the metabolites. However, the PCB-pretreated rats excreted less thioethers (62%) compared to the rats treated only with the same amount of vinyltoluene whereas the total sum of the other metabolites was about the same in these both groups. This result suggests that PCBs change the metabolism of vinyltoluene to some other pathway which could be glucuronide conjugation because PCBs increased the activity of UDP glucuronosyltransferase in a dose-dependent manner.

Mercapturic acid metabolites from 2-, 3-, and 4-ethenyl-methylbenzenes in the rat

N-Acetyl-L-cysteine was reacted with 2-(2-, 3-, or 4-methylphenyl)-oxiranes to give mixtures of the two possible regio isomers N-acetyl-S-[1-(2-, 3-, or 4-methylphenyl)-2-hydroxyethyl]-L-cysteine and N-acetyl-S-[2-(2-, 3-, or 4-methylphenyl)-2-hydroxyethyl]-L-cysteine, respectively. These were isolated in pure form by h.p.l.c.. The diastereomers were characterized by n.m.r. and mass spectrometry. The 2-, 3- and 4-ethenyl-methylbenzenes and the 2-(2-, 3-, and 4-methylphenyl)-oxiranes were injected i.p. into rats. G.l.c.-mass spectrometry showed similar patterns of acidic metabolites in the urine. Comparison with authentic mass spectra showed that the N-acetyl-S-[1-(methylphenyl)-2-hydroxyethyl]-L-cysteines accounted for over 80% of the mercapturic acids.

Bone marrow cell chromosomal aberrations and styrene biotransformation in mice given styrene on a repeated oral schedule

Styrene's capacity to induce chromosomal aberrations was studied in bone marrow cells of CD1 male mice. No mutagenic effect could be detected after either a 4-day treatment course with daily oral doses of 500 mg/kg or a 70-day course with daily oral doses of 200 mg/kg. Urinary elimination of styrene metabolites related to styrene-7,8-oxide formation (i.e. phenylethylene glycol, mandelic acid, benzoic acid, phenylglyoxylic acid and total mercapturic acids) was quantitatively evaluated in the group of mice given the 200 mg/kg dose. In parallel, kinetic studies were made on styrene and styrene-7,8-oxide blood concentrations in the same group of animals. These determinations were carried out on days 1 and 70 of treatment by spectrophotometric, gas chromatographic and mass fragmentographic procedures. Not even nanograms of styrene-7,8-oxide were found in the blood of styrene-treated mice. This suggests that the metabolite does not migrate from the cellular compartment where it is formed being immediately metabolized or irreversibly bound to cellular structures. This observation could well explain the lack of mutagenic effects observed.

Studies on metabolism and toxicity of styrene--VI. Regioselectivity in glutathione S-conjugation and hydrolysis of racemic, R- and S-phenyloxiranes in rat liver

Rat liver cytosol converted phenyloxirane enantiomers regioselectively to glutathione S-conjugates. R-(+)-Phenyloxirane was converted to S-(1-phenyl-2-hydroxyethyl)glutathione (conjugate 1) and S-(2-phenyl-2-hydroxyethyl)glutathione (conjugate 2) (ratio 6.1:1), and S-(-)-phenyloxirane to conjugates 1 and 2 (ratio 1:32). Racemic phenyloxirane was converted to conjugates 1 and 2 (ratio 1.8:1). The conjugates were separated by HPLC on an octadecylsilicone column and identified with synthetic specimens whose structures were assigned by 13C NMR spectrometry. R-(+)-, S-(-)- and racemic phenyloxiranes were hydrolyzed to R-(-)-, S-(+)- and racemic phenylethanediols by microsomal epoxide hydrolase without inversion of absolute configurations of their benzylic carbons. R-(+)-Phenyloxirane had much smaller Km and Vmax than the S-(-)-oxirane did. The R-(+)-oxirane potentially inhibited the microsomal hydrolysis of the S-(-)-oxirane and was preferentially hydrolyzed when the racemic oxirane was used as the substrate. Microsomal monooxygenase oxidized styrene to R-(+)- and S-(-)-phenyloxiranes (ratio 1.3:1), and the ratio was little changed by the pretreatment of the animal with phenobarbital, 3-methylcholanthrene and polychlorinated biphenyls.

Mechanism of formation of mercapturic acids from aromatic aldehydes in vivo

Male adult Wistar rats dosed i.p. with o-substituted benzaldehydes (o-F, o-Cl, and o-Br = V, VI, and VII) excreted mercapturic acids in urine. These acids were identified as N-acetyl-S-(ortho-substituted benzyl)cysteines (I, II, III). The total mercapturic acid excretion as % dose (2.0 mmol/kg, n = 4) was 1.2 +/- 0.4, 6.8 +/- 0.9, and 10.4 +/- 2.0 for V, VI, and VII. p-Cl-benzaldehyde administered in the same dose showed a non-significant urinary thioether excretion. The aim of the investigation was to prove in vivo a postulated metabolic pathway of substituted benzaldehydes via sulphate esters to mercapturic acids. After a single administration of the sodium salts of o- and p-Cl-benzylsulfuric acid a significant increase in mercapturic acid excretion of 21.2 +/- 1.8% and 14.5 +/- 1.2% of dose (2.0 mmol/kg, n = 4) was found. By pretreatment with pyrazole the mercapturic acid excretion increased after administration of o-Cl-benzyl alcohol (IX) whereas a significant decrease was found after administration of o-Cl-benzaldehyde (VI). After simultaneous administration of ethanol with IX and VI an increase in mercapturic acid excretion was observed. After previous administration of pentachlorophenol a significant decrease in urinary mercapturic acid excretion for IX and VI was found. These findings are in accordance with a metabolic pathway of substituted benzaldehydes via benzyl alcohols, subsequently sulphate esters to the corresponding benzylmercapturic acids.

High-performance liquid chromatographic assay of cytosolic glutathione S-transferase activity with styrene oxide

A high-performance liquid chromatographic (HPLC) assay for measuring cytosolic glutathione S-transferase activity with styrene oxide is described. After incubating lung or liver cytosol with reduced glutathione and styrene oxide, unreacted styrene oxide is extracted into ethyl acetate. An aliquot of the aqueous phase is evaporated to dryness and reconstituted in the mobile phase for HPLC analysis. The two glutathione conjugates of styrene oxide [S-(1-phenyl-2-hydroxyethyl)glutathione and S-(2-phenyl-2-hydroxyethyl)glutathione] are separated in less than 10 min; quantitation of transferase activity is based on the comparison of the UV absorbance of the two conjugates at 254 nm with synthetic conjugate standards. As little as 1 nmole of either conjugate can be quantitated with good precision. This assay has advantages over previously published methods for measuring styrene oxide glutathione S-transferase activity as it does not depend on the use of relatively unstable and expensive radiolabelled substrates.

Advances in methods and techniques for the identification of xenobiotic conjugates

This review discusses recent advances in methods and instrumentation that are potentially useful for the characterization of polar xenobiotic conjugates. Topics that are discussed include: fast atom bombardment, secondary ion, 252Cf-plasma desorption, field desorption and direct chemical ionization mass spectrometry and, proton and carbon-13 nuclear magnetic resonance spectrometry.

Isolation and identification of mercapturic acid metabolites of phenyl substituted acrylate esters from urine of female rats

The urinary mercapturic acid excretion by female rats of methyl atropate (alpha-phenyl methyl acrylate) and methyl cinnamate (beta-phenyl methyl acrylate) has been studied. On the basis of the structures of these mercapturic acids the conclusion can be drawn that these compounds arise from a conjugation of glutathione with the acrylic esters in a Michael fashion. Previous administration of (tri-orthotolyl) phosphate (TOTP), a carboxy esterase inhibitor, enhances the capacity of the acrylate esters to alkylate glutathione in vivo. The amount increased from 1.5 to 22.8% of dose (1.0 mmol/kg) for methyl cinnamate and from 10.4 to 14.8% of dose (0.2 mmol/kg) for methyl atropate. Upon inhibition of the esterase activity the major actual mercapturic acid is a conjugate of the acrylate in which the ester function is retained. In the absence of an esterase inhibition the excreted mercapturic acid is a formal conjugate of the free acrylic acid (Fig. 1). No mercapturic acids could be detected which might arise from glutathione conjugation of a, beta-epoxyesters. Such epoxides are potential primary metabolites of unsaturated esters. They were not detected by in vitro experiments. Therefore, the intermediacy of glycidic esters in the biotransformation of these acrylic esters may be considered as highly unlikely.

Mercapturic acids as metabolites of aromatic aldehydes and alcohols

After administration of substituted (CH3, OH, OCH3, F, CL, Br, NO2) benzaldehyde or benzyl alcohols in the rat an enhanced urinary thioether excretion was found in some cases. With p-substituted benzaldehyde only occasionally a slight increase could be shown, but with o-substituted aldehydes and alcohols thioether excretions amounted up to 13% of the dose. Mercapturic acids were isolated and identified by synthesis, mass-, and n.m.r.-spectrometry as the arylmethyl thioethers of N-acetylcysteine. Steric hindrance by o-substituents must be the main cause of a relative decrease in oxidation to the carboxylic acid and an increase of the importance of both the reduction of the aldehydes and the reaction of the alcohols, presumably to sulphuric acid esters, as intermediates for the alkylation of glutathione. Consequently, previous administration of pyrazole, an inhibitor of alcohol dehydrogenase, caused an even larger thioether excretion after injection of o-chlorobenzyl alcohol.

Metabolism and genotoxicity of styrene

An overview on the metabolism and genotoxicity of styrene is given in this article. The mutagenic potency of styrene has been confirmed in a number of test systems providing the metabolic activation of styrene. Styrene is converted to styrene-7,8-oxide as catalyzed by cytochrome P-450 cored enzyme complex. Styrene-7,8-oxide is mutagenic in prokaryotic and eukaryotic test systems without metabolic activation. It reacts with nucleic acid bases, especially with deoxyguanosine producing 7-alkylguanine and deoxycytidine producing N-3 alkylcytosine. Quite recently, styrene-7,8-oxide has been found to be a potent carcinogen in rats. In human whole blood cultures, styrene is metabolized into styrene-7,8-oxide. Styrene is able to induce both SCEs and chromosomal aberrations in cultured lymphocytes. The clastogenic action of styrene can be explained by the metabolism of styrene into styrene-7,8-oxide in cultured human blood cells. Although also an arene oxide, styrene-3,4-oxide, has been suggested in the biotransformation of styrene, the evidence so far supports the view that the vinyl group oxidation and oxirane formation plays a predominant role in the genotoxicity of styrene.

Isolation and identification of mercapturic acids of cinnamic aldehyde and cinnamyl alcohol from urine of female rats

Rats dosed with cinnamic aldehyde (I) excreted two mercapturic acids in the urine. The major one was identified as N-acetyl-S-(1-phenyl-3-hydroxypropyl)cysteine (V). The minor one was identified as N-acetyl-S-(1-phenyl-2-carboxy ethyl)cysteine (VI). The ratio appeared to be V : VI = 4 : 1. The hydroxy mercapturic acid (V) was also isolated from urine of rats dosed with cinnamyl alcohol (II). The total mercapturic acid excretion as percentage of the dose was 14.8 +/- 1.9% for cinnamic aldehyde (250 mg/kg) (n = 4) and 8.8 +/- 1.7% for cinnamyl alcohol (n = 4) (125 mg/kg). Inhibition of the alcohol dehydrogenase by pyrazole (206 mg/kg) diminished the thioether excretion of cinnamyl alcohol to 3.3 +/- 1.4% of the dose (n = 8). Cinnamic aldehyde has been proposed to be an intermediate in the mercapturic acid formation of cinnamyl alcohol.

Stereoselective oxidation of styrene to styrene oxide in rats as measured by mercapturic acid excretion

1. Administration of styrene (I) and styrene oxide (II) to rats resulted in the excretion of 2-hydroxymercapturic acids, N-acetyl-S-(1-phenyl-2-hydroxyethyl)cysteine (III) and N-acetyl-S-(2-phenyl-2-hydrosyethyl)cysteine (IV). Each appeared to be a mixture of diastereoisomers. 2. Administration of optically pure styrene oxide resulted in formation of one set of diastereoisomers. Racemic styrene oxide gave equal amounts of diastereoisomers. Thus the opening of the epoxide ring by glutathione S-transferases was stereospecific and the transferases showed no preference for one of the isomers of styrene oxide. 3. After administration of styrene the observed ratio of the diastereoisomers for both hydroxymercapturic acids was about 1:4. This leads to the conclusion that there is a stereoselective oxidation of styrene to styrene oxide, with a preference for the R-isomer.

Whole-body autoradiography after systemic and topical administration of methyl acrylate in the guinea pig

Whole-body autoradiography was performed in the guinea pig with methyl (2,3-14C)-acrylate. Radioactive material quickly disappeared from the body after oral and, somewhat slower, after i.p. administration for the greater part. After administration in a closed cup on the skin a slow penetration in the dermis occurred preceded by the toxic effect, mainly a strong edema. In the first 16 h metabolism was primarily restricted to the skin, internal organs showed a slow rise in radioactivity. A large part of the labeled material was retained in the dermis. The detoxification was screened by estimating the urinary thioether content and respiratory carbon dioxide. This showed that in addition to oxidation to carbon dioxide the binding to SH-groups was the principal way of metabolism.

Identification or urinary mercapturic acids formed from acrylate, methacrylate and crotonate in the rat

1. After administration to rats of methyl acrylate (I), methyl methacrylate (II) and methyl crotonate (III), urinary mercapturic acids were isolated and identified as the dicarboxylic acids N-acetyl-S-(2-carboxyethyl)cysteine (IV, R = H), N-acetyl-S-(2-carboxypropyl)cysteine (V, R = H) and N-acetyl-S-(1-methyl-2-carboxyethyl)cysteine (VI, R = H) and for a minor part as their monomethyl esters IV (R = CH3) and VI (R = CH3). 2. After a single dose of the acrylates (I), (II) and (III) (0.14 mmol/kg), the excretion of the thioethers amounted to 6.6 +/- 0.6, 0.0, and 2.0 +/- 0.6% dose respectively. 3. After 18 h previous administration of the carboxylesterase inhibitor tri-o-tolyl phosphate (0.34 mmol/kg) the excretion of the thioethers amounted to 40.6 +/- 2.1, 11.0 +/- 3.3, and 16.0 +/- 2.0% dose. 4. For methyl acrylate (I) the ratio of the excreted dicarboxylic acid and monomethyl ester was 20:1. After previous administration of tri-o-tolyl phosphate this ratio was 1:2.

Synthesis and relative stereochemistry of the four mercapturic acids derived from styrene oxide and N-acetylcysteine

The chemical reaction between (+/-)-styrene oxide and N-acetylcysteine produces both positional isomers (1 and 2) as a mixture of diastereoisomers with a preference for the benzylic thioether isomer 1 (2 : 1). Synthesis of the mercapturic acid conjugates from either (+)- or (-)-styrene oxide produces only two of the four possible stereoisomers. The single diastereoisomers of 1 and 2 were separated by high pressure liquid chromatography (HPLC) and identified by 1H- and 13C-nuclear magnetic resonance (NMR). The relative stereochemistry at the benzylic carbon center of the mercapturic acid conjugates was assigned on the basis of the established chemical correlation between optically pure styrene oxide and its precursor mandelic acid, and considerations on the mechanism of ring opening of epoxides by sulfur nucleophiles. The stereochemical definition of the isomers 3-6 should prove useful in investigations of the biotransformation of the glutathione (GSH) conjugates of styrene oxide.

Some biochemical and pharmacological properties of an epoxide metabolite of alclofenac

The properties of an epoxide metabolite of alclofenac have been investigated in a number of in vitro and in vivo tests. Alclofenac epoxide was shown to inhibit the activity of yeast alcohol dehydrogenase and form a conjugate with cysteine. The epoxide, but not alclofenac itself, showed mutagenic effects on strains of Salmonella typhimurium sensitive to alkylating agents, but had no effect on strains sensitive to intercalating agents. In addition the epoxide was active in a cell transformation assay using as a target Syrian hamster cells. No acute toxic reactions were observed in mice treated with alclofenac epoxide and the compound was devoid of analgesic and acute antiinflammatory activity. Alclofenac epoxide was found to be a sensitising agent in the guinea-pig when administered either by injection with complete Freud's adjuvant or topically as an ethanolic solution. It is postulated that the formation of the epoxide may explain some of the therapeutic and toxicological properties of alclofenac in man.