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Biomedical subjects

D Henschler

Publications and source records attributed to D Henschler.

At least 37 records · Page 2Linked to original sources
PubMed1993

DNA adduct formation in Salmonella typhimurium, cultured liver cells and in Fischer 344 rats treated with o-tolyl phosphates and their metabolites.

2-Phenoxy-4H-1,3,2-benzodioxaphosphorin 2-oxide is an electrophilic and a neurotoxic metabolite of o-tolyl phosphates. In a previous paper we reported that 2-phenoxy-4H-1,3,2-benzodioxaphosphorin 2-oxide is mutagenic in Salmonella typhimurium TA100 and forms DNA adducts in incubations with nucleotides, nucleosides and isolated DNA. In the present study we compare DNA adduct formation using 32P-post-labelling assays in 2-phenoxy-4H-1,3,2-benzodioxaphosphorin 2-oxide-treated bacteria (S.typhimurium TA100) and hepatoma cells with DNA adducts formed in liver, kidney, lung and heart of tri-o-tolyl phosphate-exposed Fischer 344 male rats. In both bacteria and hepatoma cells two DNA adducts could be detected after treatment with 2-phenoxy-4H-1,3,2-benzodioxaphosphorin 2-oxide. The minor adduct co-chromatographed with synthetic N3-(o-hydroxy-benzyl)deoxyuridine 3' monophosphate after postlabelling. The major DNA adduct was a cytidine adduct, most likely N3-(o-hydroxybenzyl)deoxycytidine 3' monophosphate. Male Fischer 344 rats were treated orally for 10 days with tri-o-tolyl phosphate (50 mg/kg/day) and DNA was isolated from liver, kidney, lung, heart, brain and testes 1, 4, 7 and 28 days after giving the last dose. Analysis by 32P-postlabelling revealed that two adducts were present in the DNA isolated from liver, kidney, lung and heart on the first day after giving the last dose; DNA adducts were not detected in the brain and testes. The adduct pattern after in vivo treatment with tri-o-tolyl phosphate was identical with that found in bacteria and hepatoma cells treated with 2-phenoxy-4H-1,3,2-benzo-dioxaphosphorin 2-oxide, the major adduct being N3-(o-hydroxybenzyl)deoxycytidine 3' monophosphate and the minor N3-(o-hydroxybenzyl)deoxyuridine 3' monophosphate. Both DNA adducts persisted in the lungs for the entire observation period, whereas in the kidney only the cytidine adduct could be detected 28 days after the last dose of tri-o-tolyl phosphate. In liver and heart the adducts were detectable only on the first day after completion of the treatment. The results indicate that in addition to the well established neurotoxicity, some o-tolyl phosphates may have a carcinogenic potential.

Animals↗
PubMed1993

Nephrotoxic and genotoxic N-acetyl-S-dichlorovinyl-L-cysteine is a urinary metabolite after occupational 1,1,2-trichloroethene exposure in humans: implications for the risk of trichloroethene exposure.

Excretion of mercapturic acids in the urine is indicative of the formation of electrophiles in the metabolism of xenobiotics. The determination of these mercapturic acids thus may be a useful method to estimate the exposure. We identified the nephrotoxic and mutagenic mercapturic acids N-acetyl-S-(1,2-dichlorovinyl)-L- cysteine and N-acetyl-S-(2,2-dichlorovinyl)-L-cysteine in the urine of workers exposed to 1,1,2-trichloroethene. A method to quantify these mercapturic acids by gas chromatography-mass spectrometry-selected ion monitoring was developed and appreciable amounts (2.8-3.8 mumole/L were found in human urine samples. Because deacetylation determines notably the amount of the excreted mercapturic acids, the formation of the resulting cysteine S-conjugates was comparably measured in subcellular fractions of rodent and human kidneys; significant species differences in acylase activity were found. The formation of mutagenic and nephrotoxic metabolites during 1,1,2-trichloroethene metabolism mandates a revision of the risk assessment of trichloroethene exposure.

Acetylcysteine↗
PubMed1992

A "chemical" concept for the therapy of glyoxylate-induced oxalurias (1).

Glyoxylic acid is the toxic principle of acquired and inherited oxalurias. A "chemical", not enzyme-mediated detoxication concept for the trapping of this aldehyde is described, based on a spontaneous formation of alkaloid-type heterocycles by reaction with biogenic amines or amino acids. 5,5-Dimethylthiazolidine-2(R,S)-4(S)-dicarboxylic acid, prepared by the condensation of D(-)-penicillamine with glyoxylic acid, was found to be formed quickly in vitro, to be stable in vivo and of good physiological compatibility. Renal elimination of the unchanged thiazolidine occurs mainly within 24 h, after administration of its calcium salt to NMRI-mice. Recovery up to 85% of the applied dose was quantitatively monitored by HPLC after derivatization to the corresponding fluorescent dansyl compound, which was unequivocally identified by MS analysis after isolation from mice urine.

Animals↗
PubMed1992

Evaluation of adverse effects in the standard-setting process.

Occupational exposure limits (OELs) were first introduced more than a century ago in Germany [1]. They were based on observations of people exposed at the workplace, and on experimental exposures of humans and animals, all accompanied by analytical determination of airborne occupational toxicants. The "acceptable concentrations for short-term and long-term exposure" were derived using crude subjective criteria (humans), or gross pathological alterations (animals). Over the years considerable refinement of these criteria has been achieved, both in their type and number, starting from overt histological derangements, going on to the physiological and biochemical level, and even to subtle psychological parameters. This development has taken place in parallel with, and has been considerably influenced by changes in the definition of health and the perception of effects detrimental to health. Differences in the elementary philosophy of health and in the activities aimed at preventing damage to health in different societies have complicated all the efforts to harmonize standard-setting processes at the international level.

Humans↗
PubMed1991

The concept of occupational exposure limits.

Germany was the first country to introduce occupational exposure limits (OEL) in 1886. A theoretical consideration for the existence of toxicological thresholds has been provided. Prerequisites for OELs are seen in: reversibility, existence of a threshold, deviation of (physiological) functions from normal to be regarded as "safe", knowledge about mechanism of toxic effect; and for the decision process: complete transparency of decision making, and combination with intensive health surveillance in the workplace. A variety of additional provisions has been introduced into the German MAK-list: a system for limitation of peak exposures; notification of sensitization and skin absorption, and of reproductive hazards; no satisfactory regulation of exposure to mixtures has been established. Occupational carcinogens constitute a special case because of identification of a threshold and the establishment of health-based standards has not yet been demonstrated justifiably. At present, strategies are elaborated for the quantification of cancer risk from a given compound. Despite many shortcomings and criticism. OELs continue to be an important and valid instrument for the protection of workers' health.

Environmental Health↗
PubMed1991

Genotoxic and cell-transforming properties of (trans,trans)-muconaldehyde.

(trans,trans)-Muconaldehyde, a putative metabolite of benzene, should be expected to have mutagenic properties by virtue of its twin alpha,beta-unsaturated carbonylic function. It displayed definitely mutagenic properties in S. typhimurium TA100 without metabolic activation and with a 5-fold concentration of tester organisms in the preincubation assay and induced SOS response in E. coli. It induced micronucleus formation and morphological transformation in a dose-dependent manner in Syrian hamster embryofibroblasts. No DNA single-strand breaks or interstrand cross-links could be detected using the alkaline elution technique; however, strand-break generation by subsequent gamma-irradiation was found to be increased.

Aldehydes↗
PubMed1991

Mutagenicity of 2-methylacrolein, 2-ethylacrolein and 2-propylacrolein in Salmonella typhimurium TA100. A comparative study.

The C2-alkylated acrolein derivatives 2-methylacrolein, 2-ethylacrolein and 2-propylacrolein are mutagenic in Salmonella typhimurium TA100. They are direct mutagens, their mutagenic potency being inversely proportional to the size of the alkylating substituent in the C2 position. In the presence of S9 mix, the mutagenicity of all these substances is considerably reduced; the reduction in mutagenicity is inversely proportional to the direct mutagenic potential of the substance. As shown for 2-methylacrolein, the reduction in mutagenicity is dependent on the concentration of S9 in the S9 mix and is not significantly influenced by heat inactivation of the S9 mix or by addition of TCPO, an inhibitor of epoxide hydrolase, to the testing system. There are no indications of enzymatic activation by the metabolizing microsomal system.

Acrolein↗
PubMed1991

Metabolism of 14C-dichloroethyne in rats.

1. The metabolism of 14C-dichloroethyne was studied in rats by inhalation in a dynamic nose-only exposure system. 14C-Dichloroethyne was generated in 95-99% yield from 14C-trichloroethene by alkaline dehydrochlorination. 2. After inhalation of 20 ppm and 40 ppm dichloroethyne for 1 h, the retention rates were 17.6% and 15.6% of the radioactivity introduced into the exposure system, respectively. During the period of observation (96 h), almost quantitative elimination of the dose was observed. Elimination with urine accounted for 60.0% (40 ppm) and 67.8% (20 ppm) of absorbed radioactivity and elimination with faeces for 27% (40 ppm) and 27.7% (20 ppm), 3.4-3.5% remained in the carcasses. 3. Metabolites of dichloroethyne identified are: N-acetyl-S-(1,2-dichlorovinyl)-L-cysteine, dichloroethanol, dichloroacetic acid, oxalic acid and chloroacetic acid in urine; N-acetyl-S-(1,2-dichlorovinyl-L-cysteine in faeces. 4. In bile of rats exposed to 40 ppm of dichloroethyne, S-(1,2-dichlorovinyl)glutathione was the only metabolite identified. Biliary cannulation did not influence the renal excretion of N-acetyl-S-(1,2-dichlorovinyl)-L-cysteine, indicating that glutathione conjugate formation occurs in the kidney. 5. The results suggest that two metabolic pathways are operative in dichloroethyne metabolism in vivo. Cytochrome P450-dependent oxidation represents a minor pathway accounting for the formation of 1,1-dichloro compounds after chlorine migration. The major pathway is the biosynthesis of toxic glutathione conjugates. Organ-specific toxicity and carcinogenicity of dichloroethyne is due most likely to the topographical distribution of gamma-glutamyl transpeptidase which is concentrated mainly in the kidney in rats.

Acetylene↗
PubMed1991

[Genetic injuries caused by radiation and other harmful environmental pollutants].

Cancer may be induced by chemicals, ionizing radiation and certain viruses. The first causal relationships between occupation and increase in cancer have been reported two and half centuries ago. In the meantime, many other occupational toxicants have been identified as cancer inducing agents. However, quantitative risk estimates can be established in a few cases only. On the other hand, modern epidemiological investigations have brought about the main causes of cancer in highly civilized populations as certain life-styles; approximately 35% are attributed to inadequate diet and nutrition, 30% to tobacco, 7% are hormone-related in context with human reproduction, 4% due to occupational exposures, 3% may be caused by alcohol consumption, 1,5% by UV radiation and 1% by medicines (cytostatics included). Cancer risks from radiation exposure are comparatively very low. Although radiation can be measured precisely and reliably as physical units, cancers induced by nuclear weapon fallout and precipitation from the accident of Chernobyl will never be detected by epidemiological methods due to their minimal proportions. The attribution of causes obtained in this way allows for the conclusion: human cancers are mostly due to chemically definable factors, and thus are avoidable.

Carcinogens, Environmental↗
PubMed1990

Metabolism of trichloroethene--in vivo and in vitro evidence for activation by glutathione conjugation.

The metabolism of trichloroethene by glutathione conjugation was investigated in rat liver subcellular fractions and in male rats in vivo. In the presence of glutathione, rat liver microsomes transformed [14C]trichloroethene to S-(1,2-dichlorovinyl)glutathione (DCVG) identified by gas chromatography mass spectrometry after hydrolysis to the corresponding cysteine S-conjugate and chemical derivatisation. In bile of rats given 2.2 g/kg trichloroethene. DCVG was present in concentrations of 5 nmol (7 ml bile collected over 9 h) and identified by thermospray mass spectrometry after HPLC-purification. E- and Z-N-acetyl-dichlorovinyl-L-cysteine (3.1 nmol present in the pooled 24-h urine) were identified by GC/MS after methylation and butylation as urinary metabolites of trichloroethene (2.2 g/kg, orally). The presented results demonstrate that glutathione-dependent metabolism of trichloroethene is a minor route in the biotransformation of this haloalkene in rats. Formation of S-(1,2-dichlorovinyl)-glutathione, processing to S-(1,2-dichlorovinyl)-L-cysteine and metabolism of this S-conjugate by cysteine beta-lyase in the kidney to reactive and genotoxic intermediates may account for the nephrocarcinogenicity observed after long time administration of trichloroethene in male rats.

Acetylcysteine↗
PubMed1990

A mechanism of haloalkene-induced renal carcinogenesis.

Several halogenated alkenes are nephrotoxic; some others induce renal tubular adenocarcinomas in rodents after lifelong administration. A bioactivation mechanism accounting for the organ-selective tumor induction has been elucidated: conjugation of the parent compounds with glutathione (GSH), catalyzed by hepatic GSH S-transferases, results in the formation of haloalkyl and halovinyl glutathione S-conjugates. Formation of S-conjugates (identified by NMR and mass spectrometry) could be demonstrated with trichloroethene, tetrachloroethene, hexachlorobutadiene, perfluoropropene, trichlorotrifluoropropene, and dichloroacetylene in incubations with rat liver microsomes and in the isolated perfused rat liver. The GSH conjugates formed are eliminated from the rat liver with the bile and may be translocated to the kidney, intact or after metabolism to the corresponding cysteine S-conjugates that are metabolized in the kidney by renal tubular cysteine conjugate beta-lyase (beta-lyase) to reactive intermediates, most likely thioacylchlorides and thioketenes. Interaction of these potent electrophiles with DNA [demonstrated for intermediates formed from S-(1,2,3,4,4-pentachlorobutadienyl)-L-cysteine] causes mutagenicity in bacteria, genotoxicity in cultured renal cells, and cytotoxicity in kidney cells. As an alternative to beta-lyase-catalyzed cleavage, the cysteine S-conjugates may be acetylated to the corresponding mercapturic acids, which have been identified in urine. The ability of the kidney to concentrate GSH and cysteine S-conjugates and the intensive metabolism of GSH S-conjugates to cysteine S-conjugates in this organ are evidently responsible for the organotropic carcinogenicity.

Acetylcysteine↗
PubMed1989

Crotonaldehyde is mutagenic in Salmonella typhimurium TA100.

The mutagenicity of crotonaldehyde in Salmonella typhimurium TA100 cannot be demonstrated in the standard plate incorporation assay. However, as reported earlier by our group, this alpha, beta-unsaturated aldehyde is clearly mutagenic in the liquid assay modification of this testing procedure. Carried out because of the doubts recently expressed by Cooper et al. (Environ Mutagen 9:289-295, 1987) concerning the observed mutagenicity of crotonaldehyde in S. typhimurium TA100, this study confirms that this compound is clearly a direct (without activation by mammalian microsomes)-acting mutagen in S. typhimurium TA100 under appropriate conditions in the preincubation assay. The observed mutagenicity is increased by extended preincubation time and increased bacterial cell densities.

Aldehydes↗
PubMed1989

Mutagenicity of tetrachloroethene in the Ames test--metabolic activation by conjugation with glutathione.

The mutagenicity of tetrachloroethene (tetra) and its S conjugate, S-(1,2,2-trichlorovinyl)glutathione (TCVG) was investigated using a modified Ames preincubation assay. TCVG was a potent mutagen in presence of rat kidney particulate fractions containing high concentrations of gamma-glutamyl transpeptidase (GGT) and dipeptidases. Purified tetra was not mutagenic without exogenous metabolic activation or under conditions favoring oxidative metabolism. Preincubation of tetra with purified rat liver glutathione (GSH) S-transferases in presence of GSH and rat kidney fractions resulted in a time-dependent formation of TCVG as determined by (HPLC) analysis and in an unequivocal mutagenic response in the Ames test. Experiments with tetra in the isolated perfused rat liver demonstrated TCVG formation and its excretion with the bile; bile collected after the addition of tetra to the isolated perfused liver was unequivocally mutagenic in bacteria in the presence of kidney particulate fractions. The mutagenicity was reduced in all cases by the GGT inhibitor serine borate or the beta-lyase inhibitor aminooxyacetic acid. These results support the suggestion that cleavage of the GSH S conjugate formed from tetra by the enzymes of the mercapturic acid pathway and by beta-lyase may be involved in the nephrocarcinogenic effects of this haloalkene in rats.

Animals↗
PubMed1989

Non-genotoxicity of acrylic acid and n-butyl acrylate in a mammalian cell system (SHE cells).

Acrylic acid (AA), ethyl acrylate (EA) and n-butyl acrylate (BA) are widely used in the production of plastics, coatings and acrylic fibres. Occupational exposure occurs primarily via inhalation and/or skin contact. In chronic inhalation experiments EA and BA did not induce neoplastic changes in rats and mice (Klimisch and Reininghaus 1984; Miller et al. 1985). Additional investigations showed that AA and BA were not carcinogenic in mice after chronic dermal application (De Pass et al. 1984). However, recently other authors reported a weak carcinogenic potential of AA and BA after chronic dermal administration to mice (Cote et al. 1986). The conditions of the latter study lead to the suggestion that the observed tumours had developed secondarily due to the local irritating and corrosive properties of AA and BA. This view is supported by the negative results of AA, EA and BA in the conventional Ames test (Waegemaekers and Bensink 1984). Mutagenicity data in mammalian cell systems of EA were equivocal (Henschler 1986) and were lacking for AA and BA. For this reason the mutagenic potential of AA and BA was investigated in Syrian hamster embryo fibroblasts (SHE cells). DNA repair (UDS assay), chromosomal changes (micronucleus assay) and morphological transformation were chosen as biological end-points.

Acrylates↗
PubMed1989

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

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

Animals↗