Igor Linhart

Exposure to various benzene derivatives differently induces cytochromes P450 2B1 and P450 2E1 in rat liver

Benzene (B), toluene (T), ethylbenzene (EB), styrene (S) and xylene isomers (oX, mX, pX) are important environmental pollutants and B is a proved human carcinogen. Their inhalation by male Wistar rats (4 mg/1,20 h/day, 4 days) caused cytochrome P450 (P450) induction. The degree of P450 2B1 induction increased and that of 2E1 decreased in the series B, T, EB, S, oX, mX and pX, as estimated by Western blots, while neither solvent was as effective for 2B1 induction as phenobarbital and B was more effective for 2E1 than ethanol. The levels of several other P450s decreased after exposure to these solvents, B being most effective. Exposure to these solvents increased in vitro hepatic microsomal oxidation of B and aniline (AN) (2E1 substrates) 3 to 6-fold, indicating induction of this P450. T oxidation was increased 2 to 4-fold and chlorobenzene (ClB) oxidation 3-fold. Sodium phenobarbital (PB, 80 mg/kg/day, 4 days, i.p.) did not increase ethylmorphine (EM) and benzphetamine (BZP) demethylation (2B1 substrates), neither of the B derivatives did so, and oX decreased it; however, pentoxyresorufin O-dealkylation was well related to the immunochemically detected 2B1 levels in control, PB and B microsomes. PB did not increase B, but increased T and C1B oxidation 2–4 and 3-fold, respectively, indicating possible 2B1 role in their oxidation. B oxidation after various inducers was related to immunochemical 2E1 levels, T and C1B oxidation to both 2B1 and 2E1 and AN oxidation to 2E1 and 1A2 levels. Very efficient B oxidation by 2E1 at low B levels indicates that induction of 2E1 may contribute to B myelotoxicity in vivo more than any other P450 enzyme tested, especially considering the fact that B is the most efficient inducer of its metabolism.

Stereochemical aspects of styrene biotransformation

Urine of rats dosed with styrene (240 mg/kg), R-, S- and racemic styrene oxide (150 mg/kg) was analysed for mandelic acid enantiomers and for regioisomers and diastereomers of mercapturic acids by NMR spectrometry. Enantiomers of mandelic acid were converted to diastereomeric Moshers derivatives prior to analysis. R- and S-styrene oxide yielded predominantly R- and S-mandelic acid, respectively, racemic styrene oxide gave predominantly the R-enantiomer whereas styrene yielded almost racemic mandelate. The regioselectivity of mercapturic acid formation was very similar for styrene, R- and S-styrene oxide. These three species yielded a 2:1 mixture of N-acetyl-S-(1-phenyl-2-hydroxyethyl)cysteine (MA1) and N-acetyl-S-(2-phenyl-2-hydroxyethyl)cysteine (MA2). R-Styrene oxide gave higher conversion to mercapturic acids (28%) than the S-isomer (19% of the dose). However, R-styrene oxide yielded stereospecifically S,R-MA1 and R,R-MA2 whereas S-styrene oxide gave R,R-MA1 and S,R-MA2. Styrene yielded a mixture of diastereomeric mercapturic acids. The ratios of R,R-/S,R-isomers were 80:20 and 15:85 for MA1 and MA2, respectively. These data suggest that styrene is metabolised stereoselectively to S-styrene oxide as a major enantiomer in rat in vivo. This enantiomer has been reported to be less mutagenic than R-styrene oxide in vitro.

Improved gas chromatographic-mass spectrometric determination of the N-methylcarbamoyl adduct at the N-terminal valine of globin, a metabolic product of the solvent N,N-dimethylformamide.

A sensitive method for determination of the N-methylcarbamoyl adduct at the N-terminal valine of globin, a new metabolic product of the industrial solvent N,N-dimethylformamide (DMF), has been developed and validated. The method includes conversion of the adduct by the Edman degradation to 3-methyl-5-isopropylhydantoin (MVH), which is followed by optimized gas chromatographic analysis with mass spectrometric detection at m/z 114. The recovery of MVH from terminal N-methylcarbamoylvaline was determined using a model dipeptide to be 90%. Calibration of the method is done with MVH, employing 3-methyl-5-isobutylhydantoin as the internal standard. The limit of detection is 0.2 nmol MVH/g globin when a 100-mg sample is used. Within- and between-day precision is 4-10%. The method has been used to determine the background levels of MVH in unexposed subjects. Further, toxicokinetic studies in volunteers laid the grounds for setting the reference value for biological monitoring of occupational exposure to DMF.

New Urinary Metabolites Formed from Ring-Oxidized Metabolic Intermediates of Styrene

The urine from mice exposed to styrene vapors (600 and 1200 mg/m(3), 6 h) was analyzed for ring-oxidized metabolites of styrene. To facilitate the identification of metabolites in urine, the following potential metabolites were prepared: 2-, 3-, and 4-vinylphenol (2-, 3-, and 4-VP), 4-vinylpyrocatechol, and 2-, 3-, and 4-vinylphenylmercapturic acid (2-, 3-, and 4-VPMA). For the analysis of vinylphenols beta-glucuronidase-treated urine was extracted and derivatized with acetanhydride/triethylamine before injection into GC/MS. Three isomers, 2-, 3-, and 4-VP, were found in the exposed urine using authentic standards. Additionally, three novel minor urinary metabolites, arylmercapturic acids 2-, 3-, and 4-VPMA, were identified by LC-ESI-MS(2) by comparison with authentic standards. Excretion of the most abundant isomer, 4-VPMA, amounted to 535 +/- 47 nmol/kg and 984 +/- 78 nmol/kg, representing approximately 0.047 and 0.043% of the absorbed dose for the exposure levels of 600 and 1200 mg/m(3), respectively. The ratio of 2-VPMA, 3-VPMA, and 4-VPMA was approximately 2:1:6. In model reactions of styrene 3,4-oxide (3,4-STO) with N-acetylcysteine in aqueous solutions and of its methyl ester in methanol, 4-vinylphenol was always the main product, while 3-vinylphenol has never been detected. No mercapturic acid was found in the reaction of 3,4-STO with N-acetylcysteine in aqueous solution at pH 7.4 or 9.7, but a small amount of 4-VPMA methyl ester was detected by LC-ESI-MS after the reaction of 3,4-STO with N-acetylcysteine methyl ester. In contrast, no mercapturic acid was found in the reaction of 3,4-STO with N-acetylcysteine in aqueous solution at pH 7.4 or 9.7. These findings indicate a capability of 3,4-STO to react with cellular thiol groups despite its rapid isomerization to vinylphenol in an aqueous environment. Moreover, the in vivo formation of 2- and 3-isomers of both VP and VPMA, neither of which was formed from 3,4-STO in vitro, strongly suggests that another arene oxide, styrene 2,3-oxide, might be a minor metabolic intermediate of styrene.

N-ccetyl-S-(1-cyano-2-hydroxyethyl)-l-cysteine, a new urinary metabolite of acrylonitrile and oxiranecarbonitrile

Two mercapturic acids, i. e., N-acetyl-S-(1-cyano-2-hydroxyethyl)-l-cysteine (CHEMA) and N-acetyl-S(2-hydroxyethyl)-l-cysteine (HEMA), were isolated from the urine of rats dosed with four successive doses of oxiranecarbonitrile (glycidonitrile, GN), 5 mg/kg, a reactive metabolic intermediate of acrylonitrile (AN). GC-MS analysis of methylated urine extracts from both AN- and GN-dosed rats showed another mercapturate which was identified as N-acetyl-S-(1-cyanoethenyl)-l-cysteine (1-CEMA) methyl ester using an authentic reference sample. The mass spectrum of this compound was very similar to that of a methylated metabolite of AN tentatively identified by Langvardt et al. (1980) as N-acetyl-3-carboxy-5-cyanothiazane (ACCT). In contrast, no ACCT was found in rats dosed with either GN or AN. Hence, there is no evidence for the formation of ACCT or its isomers in rats dosed with AN or GN. The methyl ester of 1-CEMA is formed artificially by dehydration of CHEMA methyl ester in the injector of the gas chromatograph.

Biotransformation of acrylates. Excretion of mercapturic acids and changes in urinary carboxylic acid profile in rat dosed with ethyl and 1-butyl acrylate

1. The excretion of urinary metabolites was studied in rat dosed intraperitoneally with ethyl acrylate and 1-butyl acrylate. 2. Physiological carboxylic acids, namely, 3-hydroxypropanoic acid, lactic acid and acetic acid were determined by hplc and may be derived from the xenobiotic acrylates. 3. A significant increase in the amounts of 3-hydroxypropanoic acid and acetic acid excreted within 24 h after dosing was found in both the ethyl acrylate and 1-butyl acrylate-exposed rats. 4. A slight increase in the excretion of lactic acid (p < 0.10) was also found in animals exposed to ethyl and 1-butyl acrylates. 5. Two mercapturic acids, N-acetyl-S-(2-carboxyethyl)cysteine and the corresponding N-acetyl-S-[(2-alkoxycarbonyl)ethyl]cysteine were formed from both acrylate esters and were determined by glc. For ethyl acrylate the conversion to mercapturic acids amounted to 11% of the administered dose, whereas for 1-butyl acrylate the corresponding conjugates decreased from 3.6% to 0.5 mmol/kg to 1.6% at 3.0 mmol/kg. 6. Mercapturic acids appear to be potential biological markers of exposure to acrylate esters. However, more sensitive methods would be required for their determination than those available at present.

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).

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.

Vinylphenylmercapturic acids in human urine as biomarkers of styrene ring oxidation

New metabolites of styrene, three isomeric vinylphenylmercapturic acids (2-, 3-, and 4-VPMA), were recently identified by LC-ESI-MS in the urine of mice. In this study, 4-VPMA together with traces of 2- and 3-VPMA were found also in the urine of hand-lamination workers, which were exposed to styrene vapours at concentrations ranging from 23 to 244mg/m(3). Concentrations of 4-VPMA in these end-of-shift samples were 4.59±3.64ng/mL (mean±S.D.; n=10), those found next morning after the work-shift were 2.14±2.07ng/mL (mean±S.D.; n=10). Strong correlation (R=0.959) was found in the next-morning samples between concentrations of 4-VPMA and phenylglyoxylic acid, whereas correlations found between 4-VPMA and mandelic acid in both end-of-shift and next-morning samples were much weaker. The excretion of 4-VPMA accounted for only about 3.5×10(-4)% of the absorbed dose of styrene. Despite very low metabolic yield, formation of VPMAs clearly indicates occurrence and extent of styrene ring oxidation considered to be a toxicologically relevant metabolic pathway.

Excretion of urinary N7 guanine and N3 adenine DNA adducts in mice after inhalation of styrene

New urinary adenine adducts, 3-(2-hydroxy-1-phenylethyl)adenine (N3alphaA), 3-(2-hydroxy-2-phenylethyl)adenine (N3betaA), were found in the urine of mice exposed to styrene vapour. These styrene 7,8-oxide derived adenine adducts as well as previously identified guanine adducts, 7-(2-hydroxy-1-phenylethyl)guanine (N7alphaG) and 7-(2-hydroxy-2-phenylethyl)guanine (N7betaG) were quantified by HPLC-ESI-MS(2) and the excretion profile during and after a repeated exposure to 600mg/m(3) or 1200mg/m(3) of styrene for 10 consecutive days (6h/day) was determined. The excretion was dose dependent. Total N3 adenine adducts (N3alphaA+N3betaA) excreted amounted to nearly 0.8x10(-5)% of the absorbed dose while urinary N7 guanine adducts (N7alphaG+N7betaG) amounted to nearly 1.4x10(-5)% of the dose. No accumulation of the adducts was observed. Due to rapid depurination from the DNA, the excretion of both N3 adenine and N7 guanine adducts ceased shortly after finishing the exposure. Both N3 adenine and N7 guanine adducts may be used as non-invasive biomarkers of effective dose reflecting only a short time exposure to styrene.