Mercapturic acids, protein adducts, and DNA adducts as biomarkers of electrophilic chemicals.

The possibilities and limitations of using mercapturic acids and protein and DNA adducts for the assessment of internal and effective doses of electrophilic chemicals are reviewed. Electrophilic chemicals may be considered as potential mutagens and/or carcinogens. Mercapturic acids and protein and DNA adducts are considered as selective biomarkers because they reflect the chemical structure of the parent compounds or the reactive electrophilic metabolites formed during biotransformation. In general, mercapturic acids are used for the assessment of recent exposure, whereas protein and DNA adducts are used for the assessment of semichronic or chronic exposure. 2-Hydroxyethyl mercapturic acid has been shown to be the urinary excretion product of five different reactive electrophilic intermediates. Classification of these electrophiles according to their acid-base properties might provide a tool to predict their preference to conjugate with either glutathione and proteins or with DNA. Constant relationships appear to exist in the cases of 1,2-dibromoethane and ethylene oxide between urinary mercapturic acid excretion and DNA and protein adduct concentrations. This suggests that mercapturic acids in some cases may also play a role as a biomarker of effective dose. It is concluded that simultaneous determination of mercapturic acids, protein and DNA adducts, and other metabolites can greatly increase our knowledge of the specific roles these biomarkers play in internal and effective dose assessment. If the relationship between exposure and effect is known, similar to protein and DNA adducts, mercapturic acids might also be helpful in (individual) health risk assessment.

Thioether excretion in urine of applicators exposed to 1,3-dichloropropene: a comparison with urinary mercapturic acid excretion.

The excretion of thioethers in urine of applicators occupationally exposed to the soil fumigant 1,3-dichloropropene (DCP) was determined by the thioether assay. The mercapturic acid metabolite of E-1,3-dichloropropene, N-acetyl-S-(E-3-chloropropenyl-2-)-L-cysteine (E-DCP-MA), was the reference compound in the thioether assay. The mean recovery of E-DCP-MA was 58.5% (coefficient of variation (CV) 9%, n = 4). In non-exposed men mean background of urinary thioethers was 6.05 mmol SH/mol creatinine (n = 56). In applicators exposed to soil fumigants containing DCP, urinary excretion of thioethers followed first order elimination kinetics. Urinary half lives of elimination of thioethers were 8.0 (SD 2.5) hours based on excretion rates and 9.5 (SD 3.1) hours based on creatinine excretion. The urinary half life of elimination of thioethers was almost twofold higher compared with half lives of elimination of the mercapturic acids of Z- and E-1,3-dichloropropene. The post- minus pre-shift thioether concentrations in urine and the cumulative urinary thioether excretions correlated well with exposure to DCP. In urine samples the mean thioether concentration was 1.38 higher than mean DCP mercapturic acid concentration. This suggests the presence of unidentified thioether metabolite(s) due to exposure to soil fumigants containing DCP. According to the present data, an eight hour time weighted average exposure to the Dutch occupational exposure limit of 5 mg/m(3) DCP results in a post- minus pre-shift thioether concentration of 9.6 mmol SH/mol creatinine (95% confidence interval (95%CI) 7.4-11.8 mmol SH/mon creatinine) and in a cumulative thioether excretion of 139 micromol SH (95% CI 120-157 micromol SH). It is concluded that the thioether assay can be used to assess comparatively high levels of exposure to DCP.

Biological effect monitoring of occupational exposure to 1,3-dichloropropene: effects on liver and renal function and on glutathione conjugation.

A prospective study was performed in the Dutch flower bulb culture to investigate the possible effects of subchronic exposure to the soil fumigant 1,3-dichloropropene (DCP) on liver and kidney function and on glutathione conjugation capacity in blood. Urine spot samples and venous blood samples from 14 workers applying DCP (applicators) were taken at the start of the season in July, and after the season in October. The parameters of liver function measured were: alanine aminotransferase, aspartate aminotransferase, alkaline phosphatase, lactate dehydrogenase, gamma-glutamyltranspeptidase, and total bilirubin (conjugated and unconjugated). Total bilirubin was significantly decreased from 9.5 before to 7.0 mumol/l after the season. In combination with an increase in serum gamma-glutamyltranspeptidase activity from 12.5 to 19.5 U/l this indicates moderate hepatic enzyme induction. To study renal function, creatinine and beta 2-microglobulin in serum, and beta 2-microglobulin, albumin, alanine aminopeptidase, beta-galactosidase, and retinol binding protein in urine were measured. The glomerular function parameters albumin in urine and creatinine in serum changed significantly during the season: albumin concentration increased from 5.2 to 7.6 mg/l, whereas creatinine concentration [corrected] decreased from 93.0 to 87.5 mumol/l. The tubular function parameter retinol binding protein also increased in concentration from 20.0 to 26.9 micrograms/l. Therefore, a subclinical nephrotoxic effect of subchronic exposure to DCP cannot be excluded. Effects on glutathione conjugation capacity were studied by measuring erythrocyte glutathione S-transferase activity and blood glutathione concentrations. The activity of glutathione S-transferase in erythrocytes was significantly decreased from 4.7 before to 3.3 U/g haemoglobin after the season. The same was true for the blood glutathione concentrations, which decreased from 0.93 to 0.82 mM.(ABSTRACT TRUNCATED AT 250 WORDS)

Environmental and biological monitoring of non-occupational exposure to 1,3-dichloropropene.

Voluntary bystanders, simulating a situation of non-occupational exposure to Z- and E-1,3-dichloropropene (Z- and E-DCP), were exposed during field application of this nematocide in the Dutch flower-bulb culture. Environmental monitoring revealed that mean respiratory exposure concentrations of Z- and E-DCP varied from non-detectable levels to 1.12 mg/m3 8-h time-weighted average (TWA) for Z-DCP and to 0.91 mg/m3 8-h TWA for E-DCP. Biological monitoring was executed by determining urinary mercapturic acid metabolites of Z- and E-DCP according to a method recently validated in occupationally exposed applicators. A linear relationship between respiratory exposure to Z- and E-DCP and the urinary excretion of both mercapturic acids was observed in bystanders. Dermal uptake did not contribute significantly to the internal dose of Z- or E-DCP. The urinary mercapturic acid of Z-DCP was a more sensitive parameter for the detection of exposure than was respiratory air monitoring. In future studies it would be worthwhile to determine the extent of exposure of real bystanders to DCP on the basis of urinary mercapturic acid excretion.

Determination of tetrahydrophtalimide and 2-thiothiazolidine-4-carboxylic acid, urinary metabolites of the fungicide captan, in rats and humans.

Capillary gas chromatographic (GC) methods using sulphur and mass selective detection for the qualitative and quantitative determination of tetrahydrophtalimide (THPI) and 2-thiothiazolidine-4-carboxylic acid (TTCA), urinary metabolites of the fungicide captan in rat and humans, were developed. Urinary detection limits were 2.7 micrograms/l for THPI and 110 micrograms/l for TTCA. Intraperitoneal and oral administration of captan to rats resulted in a 48-h cumulative urinary excretion of THPI of 1%-2% and 3%-9% of the dose, respectively. Cumulative urinary excretion of TTCA over 48 h ranged from 2% to 5% of the captan dose for the respective routes of administration. In urine of non-exposed human subjects, neither THPI nor TTCA could be detected. In urine of fruit-growers who were occupationally exposed to captan, both THPI and TTCA could be detected. Based on these results, THPI and TTCA are proposed as promising parameters for the biological monitoring of occupational exposure to captan.

Inhalation exposure to 1,3-dichloropropene in the Dutch flower-bulb culture. Part II. Biological monitoring by measurement of urinary excretion of two mercapturic acid metabolites.

A biological monitoring study was carried out in the Dutch flower-bulb culture to determine the relationship between respiratory occupational exposure to Z- and E-1,3-dichloropropene (Z- and E-DCP) and urinary excretion of two mercapturic acid metabolites, N-acetyl-S-(Z- and E-3-chloropropenyl-2)-L- cysteine (Z- and E-DCP-MA). Urinary excretion of Z- and E-DCP-MA, either based on excretion rates or on creatinine excretion, followed first order elimination kinetics after exposure. Urinary half-lives of elimination were 5.0 +/- 1.2 hr for Z-DCP-MA and 4.7 +/- 1.3 hr for E-DCP-MA and were not statistically significantly different. Calculated coefficients of variation indicated that the half-lives of elimination of Z- and E-DCP-MA were quite consistent inter- and intra-individually. Strong correlations (r greater than or equal to 0.93) were observed between respiratory 8-hr time weighted average (TWA) exposure to Z- and E-DCP and complete cumulative urinary excretion of Z- and E-DCP-MA. Z-DCP yielded three times more mercapturic acid than E-DCP, probably due to differences in metabolism. Z- and E-DCP were excreted 45 and 14% as their respective mercapturic acid metabolites. A respiratory 8-hr TWA exposure to the Dutch occupational exposure limit of 5 mg.m-3 DCP would result in a complete cumulative excretion of 14.4 mg (95% confidence interval: 11.7-17.0 mg) Z-DCP-MA and 3.2 mg (95% confidence interval: 2.3-4.1 mg) E-DCP-MA.

Genetic deficiency of human class mu glutathione S-transferase isoenzymes in relation to the urinary excretion of the mercapturic acids of Z- and E-1,3-dichloropropene.

Mononuclear lymphocytes were isolated from the blood of 12 individuals, who had been exposed to the vapour of the soil fumigant 1,3-dichloropropene (DCP). Western blot experiments were performed on the crude lymphocyte homogenates, using a monoclonal antibody against human hepatic glutathione S-transferase (GST) isoenzyme mu, to determine the presence or absence of mu-class isoenzymes mu and/or psi. Nine of the individuals were found to be positive for mu and/or psi, the remaining three individuals being negative. In addition, all individuals showed a positive staining on immunoblot of a protein of somewhat lower molecular mass than the hepatic standard. This protein was bound by the S-hexylglutathione affinity column, and presumably constitutes a new mu-class isoenzyme, which is not subject to genetic polymorphism. Determination of the specific activities of individual human GST isoenzymes towards Z-(cis-) and E-(trans-)-DCP demonstrated that mu-class isoenzymes show a considerably higher specific activity with Z-DCP than alpha-class or pi-class isoenzymes. In addition, mu-class isoenzymes were found to be 2- to 3-fold more active with Z-DCP than with E-DCP. Their activity towards E-DCP was similar to the specific activity of alpha-class isoenzymes. Genetic polymorphism for mu-class isoenzymes could thus be a determinant in the extent of excretion of mercapturic acids from Z- and E-DCP. The urinary excretion of Z- and E-DCP mercapturic acids and the respiratory exposure to Z- and E-DCP were determined for nine and eight phenotyped individuals, respectively.(ABSTRACT TRUNCATED AT 250 WORDS)

Identification and quantitative determination of a carboxylic and a mercapturic acid metabolite of etridiazole in urine of rat and man. Potential tools for biological monitoring.

Etridiazole, 5-ethoxy-3-trichloromethyl-1,2,4-thiadiazole, was orally administered to rats and human volunteers. Two metabolites of etridiazole were synthesized: 5-ethoxy-1,2,4-thiadiazole-3-carboxylic acid (ET-CA) and N-acetyl-S-(5-ethoxy-1,2,4-thiadiazol-3-yl-methyl)-L-cysteine (ET-MA). Selective and sensitive analytical procedures to determine etridiazole, the carboxylic acid ET-CA and the mercapturic acid ET-MA in urine were developed. The detection limit of etridiazole, applying GC with nitrogen selective detection (GC-NPD), was 36 micrograms/l urine (CV = 15.4%, n = 3). The detection limit of ET-CA, applying GC with sulphur selective detection (GC-FPD), was 100 micrograms/l urine (CV = 9.8%, n = 3). In urine of rats orally treated with etridiazole, ET-CA and ET-MA were identified as metabolites of etridiazole, whereas in urine of humans given oral etridiazole, only ET-CA was identified. Unmetabolized etridiazole was excreted for less than 0.1% of the administered dose in rats. ET-CA, however, accounted for 22 +/- 9% of the administered dose of etridiazole in rats and for 13 +/- 6% in humans. ET-MA appeared to be a minor urinary metabolite of etridiazole. ET-CA is proposed as a possible biomarker for the biological monitoring of etridiazole.

N-acetyl-S-(2-hydroxyethyl)-L-cysteine as a potential tool in biological monitoring studies? A critical evaluation of possibilities and limitations.

In mammalian species, including man, N-acetyl-S-(2-hydroxyethyl)-L-cysteine (2-HEMA) is a common urinary metabolite of a large number of structurally different xenobiotic chemicals. It is a common urinary end product of glutathione pathway metabolism of a variety of chemicals possessing electrophilic properties and, in most cases, also a genotoxic potential. Five different chemically reactive intermediates, with different electrophilic properties, may be involved in the formation of 2-HEMA. An inventory of chemicals known to lead to the formation of 2-HEMA, or based on their chemical structure expected to do so, is presented. Furthermore, an attempt is made to evaluate the possibilities and limitations in terms of the potential use of urinary 2-HEMA as a tool in biomonitoring studies. Two other related, sulfur-containing urinary metabolites, i.e. N-acetyl-(S-carboxymethyl)-L-cysteine and thio-diacetic acid, are proposed as possible alternatives to urinary 2-HEMA. It is suggested that 2-HEMA might be seen as a potentially useful and sensitive signal parameter for the assessment of exposure of animals and man to a variety of electrophilic and therefore potentially toxic xenobiotic chemicals.