Albrecht Seidel

Carbonyl reductase provides the enzymatic basis of quinone detoxication in man.

Enzymes catalyzing the two-electron reduction of quinones to hydroquinones are thought to protect the cell against quinone-induced oxidative stress. Using menadione as a substrate, carbonyl reductase, a cytosolic, monomeric oxidoreductase of broad specificity for carbonyl compounds, was found to be the main NADPH-dependent quinone reductase in human liver, whereas DT-diaphorase, the principal two-electron transferring quinone reductase in rat liver, contributed a very minor part to the quinone reductase activity of human liver. Carbonyl reductase from liver was indistinguishable from carbonyl reductase previously isolated from brain (B. Wermuth, J. biol. Chem. 256, 1206 (1981] on the basis of molecular weight, isoelectric point, immunogenicity, substrate specificity and inhibitor sensitivity. The purified enzyme from liver catalyzed the reduction of a great variety of quinones. The best substrates were benzo- and naphthoquinones with short substituents, and the K-region orthoquinones of phenanthrene, benz(a)anthracene, pyrene and benzo(a)pyrene. A long hydrophobic side chain in the 3-position of the benzo- and naphthoquinones and the vicinity of a bay area or aliphatic substituent (pseudo bay area) to the oxo groups of the polycyclic compounds decreased or abolished the ability of the quinone to serve as a substrate. Non-k-region orthoquinones of polycyclic aromatic hydrocarbons were more slowly reduced than the corresponding K-region derivatives. The broad specificity of carbonyl reductase for quinones is in keeping with a role of the enzyme as a general quinone reductase in the catabolism of these compounds.

Biomonitoring of polycyclic aromatic compounds in the urine of mining workers occupationally exposed to diesel exhaust.

Diesel exhaust is considered a probable human carcinogen by the IARC. Biomonitoring of workers occupationally exposed to diesel exhaust was performed to determine their internal burden of diesel associated aromatic compounds. Personal air sampling also allowed to determine the exposure of the miners at their work place towards several polycyclic aromatic hydrocarbons (PAH) and nitro-arenes, the latter of which are thought to be specific constituents of diesel exhaust. For biomonitoring the urine of 18 underground salt miners was collected during and after their shift for 24-hours. half of the 18 miners were smokers. The urinary levels of 1-hydroxypyrene and hydroxylated phenanthrene metabolites were determined as biomarkers of PAH exposure, whereas urinary levels of some aromatic amines were chosen to monitor exposure towards specific nitro-arenes from diesel exhaust like 1-nitropyrene and 3-nitrobenzanthrone and to monitor the human burden by these compounds from inhaled cigarette smoke. Non-smoking workers exposed to diesel exhaust excrete an average level of about 4 micrograms phenanthrene metabolites, whereas the urinary levels in smokers were up to 3-fold higher. In summary the results indicate that (i) diesel exposure led to an increase of PAH metabolism in the workers examined, most probably by an induction of cytochrome P450 (ii) smokers could be identified in accordance with earlier studies by their increased ratio of phenanthrene metabolites derived from 1,2- and 3,4-oxidation and their higher amounts of excreted 1-naphthylamine, and (iii) the excreted amounts of aromatic amines found as metabolites of the nitro-arenes were about 5- to 10-fold higher as one might expect from the levels determined by personal air sampling at the workplace of the individuals.

Activation of 3-nitrobenzanthrone and its metabolites by human acetyltransferases, sulfotransferases and cytochrome P450 expressed in Chinese hamster V79 cells.

3‐Nitrobenzanthrone (3‐NBA) is a potent mutagen and suspected human carcinogen identified in diesel exhaust and ambient air pollution. 3‐Aminobenzanthrone (3‐ABA), 3‐acetylaminobenzanthrone (3‐Ac‐ABA) and N‐acetyl‐N‐hydroxy‐3‐aminobenzanthrone (N‐Ac‐N‐OH‐ABA) have been identified as 3‐NBA metabolites. Recently we found that 3‐NBA and its metabolites (3‐ABA, 3‐Ac‐ABA and N‐Ac‐N‐OH‐ABA) form the same DNA adducts in vivo in rats. In order to investigate whether human cytochrome P450 (CYP) enzymes (i.e., CYP1A2), human N,O‐acetyltransferases (NATs) and sulfotransferases (SULTs) contribute to the metabolic activation of 3‐NBA and its metabolites, we developed a panel of Chinese hamster V79MZ‐h1A2 derived cell lines expressing human CYP1A2 in conjunction with human NAT1, NAT2, SULT1A1 or SULT1A2, respectively. Cells were treated with 0.01, 0.1 or 1 μM 3‐NBA, or its metabolites (3‐ABA, 3‐Ac‐ABA and N‐Ac‐N‐OH‐ABA). Using both enrichment versions of the 32P‐postlabeling assay, nuclease P1 digestion and butanol extraction, essentially 4 major and 2 minor DNA adducts were detected in the appropriate cell lines with all 4 compounds. The major ones were identical to those detected in rat tissue; the adducts lack an N‐acetyl group. Human CYP1A2 was required for the metabolic activation of 3‐ABA and 3‐Ac‐ABA (probably via N‐oxidation) and enhanced the activity of 3‐NBA (probably via nitroreduction). The lack of acetylated adducts suggests N‐deacetylation of 3‐Ac‐ABA and N‐Ac‐N‐OH‐ABA. Thus, N‐hydroxy‐3‐aminobenzanthrone (N‐OH‐ABA) appears to be a common intermediate for the formation of the electrophilic arylnitrenium ions capable of reacting with DNA. Human NAT1 and NAT2 as well as human SULT1A1 and SULT1A2 strongly contributed to the high genotoxicity of 3‐NBA and its metabolites. Moreover, N,O‐acetyltransfer reactions catalyzed by human NATs leading to the corresponding N‐acetoxyester may be important in the bioactivation of N‐Ac‐N‐OH‐ABA. As human exposure to 3‐NBA is likely to occur primarily via the respiratory tract, expression of CYPs, NATs and SULTs in respiratory tissues may contribute significantly and specifically to the metabolic activation of 3‐NBA and its metabolites. Consequently, polymorphisms in these genes could be important determinants of lung cancer risk from 3‐NBA.

Detection of DNA effects in human cells with the comet assay and their relevance for mutagenesis

The single cell gel test (SCG-test or comet assay) is a rapid and sensitive method for measuring DNA damage and repair in individual cells. A wide variety of mutagens have been shown to cause DNA alterations detectable with the comet assay, but it is not yet clear whether a relationship exists between the DNA effects and the induction of mutations. We are therefore investigating in a cell culture system with human cells (MRC5CV1) the induction of DNA damage by environmental mutagens and the formation of mutations at the HPRT gene. In the present study we investigated benzo[a]pyrene (BP), an environmental mutagenic and carcinogenic polycyclic aromatic hydrocarbon, and its reactive metabolite (+)-anti-benzo[a]pyrene-7,8-diol 9, 10-oxide ((+)-anti-BPDE). S9 mix activated BP and the direct acting mutagen (+)-anti-BPDE caused a concentration-related increase in DNA migration in the comet assay. Postincubation experiments indicated that induced DNA effects are eliminated by DNA repair within 24 h. BP-treatment caused a strong genotoxic effect in the comet assay but had only a marginal effect on the frequency of gene mutations. When cells were treated with BP in the presence of cadmium sulphate, a clear increase in genotoxicity was observed while the effect on mutations was unchanged. Our results indicate that DNA alterations detected with the comet assay do not necessarily relate to mutagenesis. The absence of a close relationship between DNA migration in the comet assay and mutagenesis may be explained by the fact that some effects seen in the comet assay occur as a consequence of an error free DNA repair process.

Detection of carcinogenic aromatic amines in the urine of non-smokers.

Smoking is thought to be one of the most important anthropogenic risk factors involved in the development of urinary bladder cancer in humans. Tobacco smoke contains a complex mixture of chemicals including potent carcinogens such as aromatic amines. In the present study the amounts of several freebase aromatic amines including the potent carcinogens 2-aminonaphthalene and 4-aminobiphenyl have been analyzed in the urine of 48 German urban living smokers and non-smokers. The results indicate that (i) both groups excrete the identical set of four aromatic amines; (ii) smokers excrete approximately twice the total amount of these amines, but similar amounts of 2-aminonaphthalene and 4-aminobiphenyl are found in non-smokers; and (iii) the excreted aromatic amines are decomposed in the urine within a few hours thus, explaining why aromatic amines are difficult to detect in this matrix. Their decomposition could be prevented by adding small amounts of p-toluidine to the freshly collected urine. Unlike smokers the origin of aromatic amines detected in the urine of non-smokers is at present unknown. Based on the cotinine levels found in the urine of non-smokers environmental tobacco smoke can be excluded as a major source of aromatic amines. In addition, neither diesel exhaust-related nitroarenes nor the corresponding amino-derivatives, to which they may be metabolically converted, were found. The detected urinary levels of aromatic amines arising from sources other than tobacco smoke or diesel exhaust may play a role in the bladder cancer etiology of non-smokers.

Conversion of the common food constituent 5-hydroxymethylfurfural into a mutagenic and carcinogenic sulfuric acid ester in the mouse in vivo.

5-Hydroxymethylfurfural (HMF), formed by acid-catalyzed dehydration and in the Maillard reaction from reducing sugars, is found at high levels in numerous foods. It was shown to initiate colon aberrant crypt foci in rats and skin papillomas and hepatocellular adenomas in mice. HMF is inactive in in vitro genotoxicity tests using standard activating systems but is activated to a mutagen by sulfotransferases. The product, 5-sulfoxymethylfurfural (SMF), is a stronger carcinogen than HMF. SMF has not been detected in the biotransfomation experiments conducted on HMF in humans and animals in vivo up to date. Here, we report pharmacokinetic properties of HMF and SMF in FVB/N mice. Sensitive assays for the quantification of HMF and SMF by LC-MS/MS multiple reaction monitoring were devised. SMF, intravenously injected (4.4 micromol/kg body mass), showed first-order elimination kinetics in blood plasma (t(1/2) = 7.9 min). HMF, injected intravenously (793 micromol/kg body mass), demonstrated biphasic kinetics in plasma (t(1/2) = 1.7 and 28 min for the initial and terminal elimination phases, respectively); the volume of distribution of the central compartment corresponded approximately to the total body water. The maximum SMF plasma level was observed at the first sampling time, 2.5 min after HMF administration. On the basis of these kinetic data, it was estimated that between 452 and 551 ppm of the initial HMF dose was converted to SMF and reached the circulation. It is likely that additional SMF reacted with cellular structures at the site of generation and thus is ignored in this balance. Our work supports the hypothesis that HMF-related carcinogenicity may be mediated by its reactive metabolite SMF.

Stable expression of human cytochrome P450 1A1 cDNA in V79 Chinese hamster cells and metabolic activation of benzo[a]pyrene

A V79 Chinese hamster cell line stably expressing human cytochrome P450 1A1 (CYP1A1) was obtained by chromosomal integration of the human CYP1A1 cDNA under the control of the SV40 early promoter. Chromosomal integration was verified by Southern analysis, and effective transcription of the human CYP1A1 cDNA was demonstrated by Northern analysis. The CYP1A1 cDNA-encoded protein was characterized by Western analysis using anti-rat CYP1A1. Intracellular association of CYP1A1 with the endoplasmic reticulum could be visualized by in situ immunofluorescence. Crude cell lysates of the V79 derived cell line was able to catalyze 7-ethoxyresorufin-O-deethylation (EROD) with an activity of about 50 pmol min-1 mg-1 total protein, and an aryl hydrocarbon hydroxylase activity (AHH) of 25 pmol min-1 mg-1. CYP1A1 dependent cytotoxicity, measured by neutral red uptake, and genotoxicity, determined by the frequency of micronucleus formation, of benzo[a]pyrene (B[a]P) and trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene (B[a]P-7,8-diol) could be demonstrated at substrate concentrations as low as 10 nM. Thus, this cell line presents a sensitive tool for studying CYP1A1 mediated metabolism of polycyclic aromatic hydrocarbons (PAH). B[a]P and the purified (+)- and (-)-enantiomers of B[a]P-7,8-diol were compared for their mutagenicity. The (-)-enantiomer was found to be 3-5-fold more mutagenic than the (+)-enantiomer.

DNA adduct formation by the ubiquitous environmental pollutant 3-nitrobenzanthrone and its metabolites in rats.

Diesel exhaust is known to induce tumours in animals and is suspected of being carcinogenic in humans. Of the compounds found in diesel exhaust, 3-nitrobenzanthrone (3-NBA) is an extremely potent mutagen and suspected human carcinogen forming multiple DNA adducts in vitro. 3-Aminobenzanthrone (3-ABA), 3-acetylaminobenzanthrone (3-Ac-ABA), and N-acetyl-N-hydroxy-3-aminobenzanthrone (N-Ac-N-OH-ABA) were identified as 3-NBA metabolites. In order to gain insight into the pathways of metabolic activation leading to 3-NBA-derived DNA adducts we treated Wistar rats intraperitoneally with 2mg/kg body weight of 3-NBA, 3-ABA, 3-Ac-ABA, or N-Ac-N-OH-ABA and compared DNA adducts present in different organs. With each compound either four or five DNA adduct spots were detected by TLC in all tissues examined (lung, liver, kidney, heart, pancreas, and colon) using the nuclease P1 or butanol enrichment version of the 32P-postlabelling method, respectively. Using HPLC co-chromatographic analysis we showed that all major 3-NBA-DNA adducts produced in vivo in rats are derived from reductive metabolites bound to purine bases and lack an N-acetyl group. Our results indicate that 3-NBA metabolites (3-ABA, 3-Ac-ABA and N-Ac-N-OH-ABA) undergo several biotransformations and that N-hydroxy-3-aminobenzanthrone (N-OH-ABA) appears to be the common intermediate in 3-NBA-derived DNA adduct formation. Therefore, 3-NBA-DNA adducts are useful biomarkers for exposure to 3-NBA and its metabolites and may help to identify enzymes involved in their metabolic activation.

Detoxication of carcinogenic fjord-region diol epoxides of polycyclic aromatic hydrocarbons by glutathione transferase P1-1 variants and glutathione

Epidemiological studies suggest that individuals differing in the expression of allelic variants of the human glutathione transferase (GST) Pi gene differ in susceptibility to chemical carcinogens such as polycyclic aromatic hydrocarbons (PAH). This study reports the catalytic efficiencies (k cat/K m) of two naturally occurring variants, GSTP1‐1/I‐105 and GSTP1‐1/V‐105, towards a series of fjord‐region diol epoxides representing potent biologically active PAH metabolites, and two GSTP1‐1 mutants with Ala105 and Trp105 in the active site. The results indicate that individuals who are homozygous for the allele encoding GSTP1‐1/V‐105 might be more susceptible to PAH carcinogenesis due to other reasons than a reduced capacity for detoxifying diol epoxides.

Human intestinal Caco-2 cells display active transport of benzo[a]pyrene metabolites

Epithelial cells of the gastrointestinal tract are challenged by exposure to many potentially toxic agents including the well-known food contaminant benzo[a]pyrene (B[a]P). They are equipped with a variety of Phase 1- and Phase 2-enzymes that are able to metabolize B[a]P. Furthermore, transmembranous ABC-transport proteins are expressed at the apical pole of these cells. The aim of this study was to investigate whether [14C]B[a]P or products of the metabolism are transported by intestinal cells back into the gut lumen. The intestinal Caco-2 cell line was used as a metabolism and transport model. Experiments with Caco-2 monolayers in the Transwell-system revealed that radiolabeled substance is transported towards the apical (luminal) region. This transport was characterized as active and increased after induction of cytochromes P450 1A1 and 1B1 by beta-naphthoflavone. On the other hand, transport was decreased with the concomitant inhibition of Phase 1-metabolism. TLC-analysis revealed that the primary metabolites of B[a]P found in the supernatant were very polar; other metabolites of less polarity could only be detected in trace amounts. These results indicate that B[a]P is metabolized by Caco-2 cells to highly polar metabolites resulting from biphasic metabolism and that these polar metabolites are subject to an apically directed transport. Chemical inhibition studies showed that P-glycoprotein and MRP1 or 2 were not involved in this polarized B[a]P-metabolite secretion.