Biochemisches Institut für Umweltcarcinogene

5-Hydroxymethylfurfural (HMF) and furfuryl alcohol (FFA) are moderately potent rodent carcinogens that are present in thermally processed foodstuffs. The carcinogenic effects were hypothesized to originate from sulfotransferase (SULT)-mediated bioactivation yielding DNA-reactive and mutagenic sulfate esters, a confirmed metabolic pathway of HMF and FFA in mice. It is known that orthologous SULT forms substantially differ in substrate specificity and tissue distribution. This could influence HMF- and FFA-induced carcinogenic effects. Here, we studied HMF and FFA sulfoconjugation by 30 individual SULT forms of humans, mice and rats. The catalytic efficiencies (k cat/K M) of HMF sulfoconjugation of human SULT1A1 (13.7 s−1 M−1), mouse Sult1a1 (15.8 s−1 M−1) and 1d1 (4.8 s−1 M−1) and rat Sult1a1 (5.3 s−1 M−1) were considerably higher than those of all other SULT forms investigated (≤0.73 s−1 M−1). FFA sulfoconjugation was monitored using adenosine as a nucleophilic scavenger for the reactive 2-sulfoxymethylfuran (t 1/2 = 20 s at 37 °C). The resulting adduct N 6-((furan-2-yl)methyl)-adenosine (N 6-MF-A) was quantified by isotope-dilution UPLC-MS/MS. The rates of N 6-MF-A formation showed that hSULT1A1 and its orthologues in mice and rats were also the most important contributors to FFA sulfoconjugation in each of the species. Taken together, the catalytic capacity of hSULT1A1 is comparable to that of mSult1a1 in mice, the species in which carcinogenic effects of HMF and FFA were detected. This is of primary concern due to the expression of hSULT1A1 in many different tissues.Electronic supplementary materialThe online version of this article (doi:10.1007/s00204-014-1392-6) contains supplementary material, which is available to authorized users.

Stable adducts to serum albumin (SA) from electrophilic and genotoxic compounds/metabolites can be used as biomarkers for quantification of the corresponding in vivo dose. In the present study, conditions for specific analysis of stable adducts to SA formed from carcinogenic polycyclic aromatic hydrocarbons (PAH) were evaluated in order to achieve a sensitive and reproducible quantitative method. Bulky adducts from diolepoxides (DE) of PAH, primarily DE of benzo[a]pyrene (BPDE) and also DE of dibenzo[a,l]pyrene (DBPDE) and dibenzo[a,h]anthracene (DBADE), were used as model compounds. The alkylated peptides obtained after enzymatic hydrolysis of human SA modified with the different PAHDE were principally PAHDE-His-Pro, PAHDE-His-Pro-Tyr and PAHDE-Lys. Alkaline hydrolysis under optimised conditions gave the BPDE-His as the single analyte of alkylated His, but also indicated degradation of this adduct. It was not possible to obtain the BPDE-His as one analyte from BPDE-alkylated SA through modifications of the enzymatic hydrolysis. The BPDE-His adduct was shown to be stable during the weak acidic conditions used in the isolation of SA. Enrichment by HPLC or SPE, but not butanol extraction, gave good recovery, using Protein LoBind tubes. A simple internal standard (IS) approach using SA modified with other PAHDE as IS was shown to be applicable. A robust analytical procedure based on digestion with pronase, enrichment by HPLC or SPE, and analysis with HPLC/MS-MS electrospray ionisation was achieved. A good reproducibility (coefficient of variation (CV) 11%) was obtained, and the achieved limit of detection for the studied PAHDE, using standard instrumentation, was approximately 1fmol adduct/mg SA analysing extract from 5mg SA.

A wide variety of contaminants are ingested through food, among them the pro-carcinogenic polycyclic aromatic hydrocarbon benzo[a]pyrene (BP) that is resorbed and partially metabolized in the enterocytes of the small intestine. Previous in vitro studies have revealed that BP phenols are excreted as Phase II metabolites including glucuronides and sulfates. This export is mediated by the breast cancer resistance protein (ABCG2). The ultimate carcinogenic Phase I BP metabolite anti-BP-7,8-dihydrodiol-9,10-epoxide (BPDE) can be detoxified by glutathione conjugate formation catalyzed by glutathione S-transferases. In the present study, differentiated human intestinal Caco-2 cells were used as a model for the human small intestine to investigate the detoxification of BPDE and excretion of stereoisomeric glutathione conjugates in the presence of an inhibitor of the glutathione-cleaving enzyme γ-glutamyl transpeptidase at the cell surface. The results indicate that the glutathione conjugates of BPDE are formed and excreted mainly to the apical and to a minor extent to the basolateral side of polarized Caco-2 monolayers. Inhibition studies revealed that the multidrug resistance-associated proteins (ABCCs) are involved in the transport of BPDE glutathione conjugates. Stable ABCC1, ABCC2 and ABCC3 knockdown cell lines were generated, thus making it possible to demonstrate that ABCC1 mediates the basolateral and ABCC2 the apical excretion of BPDE glutathione conjugates. In conclusion, the ultimate carcinogen BPDE is detoxified via glutathione conjugation and subsequently excreted by Caco-2 cells in both apical and basolateral directions. This finding is equivalent to a transport into feces as well as blood system in the in vivo situation.

The alkylated polycyclic aromatic hydrocarbon 1-methylpyrene is a carcinogen in rodents and has been detected in various environmental matrices and foodstuffs. It is activated metabolically by benzylic hydroxylation to 1-hydroxymethylpyrene followed by sulfoconjugation to yield electrophilic 1-sulfooxymethylpyrene (1-SMP) that is prone to form DNA adducts. An LC-MS/MS method using multiple reaction monitoring (MRM) of fragment ions has been developed for specific detection and quantification of N (2)-(1-methylpyrenyl)-2'-deoxyguanosine (MP-dGuo) and N (6)-(1-methylpyrenyl)-2'-deoxyadenosine (MP-dAdo) formed in DNA in the presence of 1-SMP. DNA samples were spiked with stable isotope internal standards, [ (15)N 5, (13)C 10]MP-dGuo and [ (15)N 5]MP-dAdo, followed by enzymatic digestion to 2'-deoxynucleosides and solid-phase extraction to remove unmodified 2'-deoxynucleosides prior to analysis by LC-MS/MS. The limits of detection were 10 fmol of MP-dGuo and 2 fmol of MP-dAdo or three molecules of MP-dGuo and 0.6 molecules of MP-dAdo per 10 (8) 2'-deoxynucleosides using 100 mug of herring sperm DNA as the sample matrix. The method was validated with herring sperm DNA reacted with 1-SMP in vitro. Hepatic DNA was analyzed from rats that were dosed intraperitoneally with 9.3 mg 1-SMP per kg body weight and killed after various time periods. Levels of MP-dGuo and MP-dAdo in rat liver were found to increase, reaching their maxima at approximately 3 h, and then decrease over time. A good correlation was observed between the results obtained using LC-MS/MS and MRM and those from (32)P-postlabeling. MRM allowed the more precise quantification of specific 1-MP adducts, in addition to a time reduction of the analysis when compared with (32)P-postlabeling.

The polycyclic aromatic hydrocarbons (PAHs) dibenzo[a,l]pyrene (DBP) and benzo[a]pyrene (BP) are environmental contaminants and potent carcinogens. DBP is several orders of magnitude more mutagenic/carcinogenic than BP. This can be ascribed to differences in DNA binding efficiency of their ultimate carcinogenic bay- and fjord-region diol epoxide (DE) intermediates, differences in structural features of the DNA adducts and differences in DNA adduct recognition and the subsequent downstream signaling. In this study, we have characterized the effect of the ultimate carcinogenic DEs, (+)-anti-BPDE and (-)-anti-DBPDE following short exposure times, on Mdm2 and p53 pathway in A549 human lung epithelial carcinoma cells. In contrast to (-)-anti-DBPDE, (+)-anti-BPDE induces stabilization of phosphorylated Mdm2. (+)-anti-BPDE-induced effects on Mdm2 were transient and correlated with transient p53 Ser15 phosphorylation. DNA adducts of (-)-anti-DBPDE are more refractory to removal by nucleotide excision repair (NER) than adducts of (+)-anti-BPDE and do not induce Mdm2 phosphorylation. This suggests a role of phosphorylated Mdm2 in the repair process. In addition, (-)-anti-DBPDE, in contrast to (+)-anti-BPDE, induced prolonged p53 Ser15 phosphorylation as well as phosphorylation of p53 at Ser46, a phosphorylation site associated with apoptosis. It is also concluded that p53 Ser15 phosphorylation and antibody 2A10-site specific Mdm2 alterations are induced by nonidentical signaling pathways by the bay- and fjord-region DE. These differences may reflect the different carcinogenic potential of these compounds.

The equivocal experimental and epidemiological evidence of bitumen fumes and the possible mechanisms of toxicity remain uncertain. This study therefore aimed at investigating the genotoxicity of bitumen fumes, the biotransformation and urinary excretion of PAHs, and altered expression of a selected number of genes in lung, nasal epithelium, and white blood cells of rats. Animals were exposed to three different concentrations (low: 4 mg/m 3 ; medium: 20 mg/m 3 ; high: 100 mg/m 3 ) of bitumen fume condensate for 5 days, 30 days, and 12 months (6 hours per day) or ambient air. Notably, no dose-related signs of intolerance were observed throughout the inhalation period but dose dependent uptake of bitumen fumes was observed based on urinary excretion of PAHs and metabolites. At best, measurements of naphthols enabled an estimate of dose-dependent body burden. Excretion of 1-hydroxy- and 2-hydroxyphenanthrene was dose dependent and their production is catalyzed by the CYP1A1 monooxygenase which we found to be strongly induced upon exposure to bitumen fumes. Furthermore, pyrene, a minor component in bitumen fumes, produced hydroxypyrene levels close to the detection limit in rat urine. We additionally determined DNA adduct formation by the 32 P-postlabelling assay and observed a dose and time dependent increase of 3 to 4 stable DNA adducts in lung, nasal, and alveolar epithelium. DNA adduct levels were highest in nasal epithelium, the relative adduct level (RAL) being 450 adducts per 10 9 nucleotides. For lung and alveolar epithelium the RAL was 114 and 76 adducts per 10 9 nucleotides, respectively. However, we did not observe micronucleated red blood cells of the peripheral blood or with polychromatic erythrocytes of the bone marrow (after 12 months). It is important to note that erythrocyte cell count in bone marrow smears was reduced in four out of six animals after 12 months of exposure, clearly demonstrating that components of bitumen fume had reached the bone marrow. Finally, we investigated by reverse transcription polymerase chain reaction regulation of genes with known functions in inflammation, asthma and other pulmonary diseases. Gene expression changed during the time of exposure. With the monooxygenases CYP1A1 and CYP2G1 we observed dose dependent regulation in nasal and lung tissue. We also observed significant, but dose independent, regulation of cathepsin K and D, cadherin 22, platelet activating factor acetylhydrolase isoform 1b alpha subunit and the regulator of G-protein signalling in nasal epithelium of male rats after exposure to bitumen fumes. We found bitumen fumes to be genotoxic in target tissue of exposure and observed altered regulation of genes involved in the metabolic activation of polycyclic aromatic hydrocarbons and cellular inflammatory processes. These findings are consistent with the histopathology observed in the respiratory tract of rats chronically exposed to bitumen fume. An understanding of the regulation of suspected disease candidate genes in target tissues of exposure will be an interesting objective for further research into the mechanisms of toxicity.

The procarcinogen 1-methylpyrene is activated by hepatic enzymes via 1-hydroxymethylpyrene to 1-sulfooxymethylpyrene (1-SMP), a highly reactive and mutagenic metabolite. Previously, high levels of 1-SMP DNA adducts were observed in rat kidneys after intraperitoneal administration of 1-hydroxymethylpyrene or 1-SMP. This study examined whether organic anion transporters (OAT) that are expressed at the basolateral membrane of proximal tubule cells are involved in uptake of SMP. Human epithelial kidney (HEK293) cells that stably express human OAT1 (hOAT1) and hOAT3 were used. Stable isomers of 1-SMP, (2-SMP and 4-SMP) competitively inhibited the uptake of characteristic substrates p-aminohippurate for hOAT1 and estrone sulfate for hOAT3. Both inhibitors exhibited high affinity for hOAT1 (K(i) = 4.4 microM for 2-SMP; K(i) = 5.1 microM for 4-SMP) as well as hOAT3 (K(i) = 1.9 microM for 2-SMP; K(i) = 2.1 microM for 4-SMP). The uptake rate of 4-SMP (at a concentration of 10 microM) by hOAT1- and hOAT3-expressing cells was 3.0 and 1.6 times higher, respectively, than in control cells. Uptake of the reactive isomer 1-SMP was investigated using as the end point the level of DNA adducts that were formed in the cells. After exposure to 1-SMP (10 microM), the DNA adduct level was 4.6 and 3.0 times higher in hOAT1- and hOAT3-expressing cells, respectively, than in control cells. The enhanced DNA adduct formation in hOAT-expressing cells was abolished in the presence of the OAT inhibitor probenecid. This study indicates that OAT can mediate the basolateral uptake of reactive sulfuric acid esters into proximal tubule cells and thereby participate in kidney cell damage by these compounds.

The polycyclic aromatic hydrocarbons (PAHs) dibenzo[a,l]pyrene (DBP) and benzo[a]pyrene (BP) are widespread environmental contaminants and potent carcinogens. The fjord-region DBP is considerably more carcinogenic than the bay-region BP. This fact can be ascribed to differences in DNA binding efficiency of their ultimate carcinogenic diol epoxide (DE) intermediates, differences in structural features of the DNA adducts, and differences in DNA adduct recognition and the subsequent lesion removal by nucleotide excision repair (NER). We have compared the formation and removal of adducts as a function of time formed by the carcinogenic metabolites (-)-anti-DBPDE and (+)-anti-BPDE in A549 human epithelial lung carcinoma cells. Cells were exposed to 0.1 or 1.0 microM (-)-anti-DBPDE and (+)-anti-BPDE, respectively. Adducts were measured at various post-treatment times (up to 6 h) by enzymatic DNA hydrolysis and a HPLC procedure that allows monitoring of all cis- and trans-nucleoside adducts of dA and dG. Treatment with 0.1 microM (-)-anti-DBPDE resulted in an initial increase of adducts to a maximal level of 144 pmol adducts/mg of DNA after 1 h of incubation. This was followed by an apparent, although not statistically significant, slow removal of adducts. After 6 h of incubation, at least 80% seems to remain. In cells treated with 1.0 microM (+)-anti-BPDE, the maximal level of 140 pmol adducts/mg of DNA was reached within 20 min of exposure. The formation was followed by an initial rapid decline in the adduct level (1.54 pmol adducts/mg of DNA/min) and a later statistically significant slower rate (0.14 pmol adducts/mg of DNA/min) of adduct removal. After 1 h of incubation, about 45% of the adducts are removed followed by 75% at 6 h. The biphasic pattern of BPDE removal has been observed previously in mammalian cells and, at least in part, may reflect the action of transcription-coupled repair (TCR) and the subsequent global genomic repair (GGR). Comparing the rate of removal of adducts derived from BPDE with those of DBPDE, the latter are obviously more refractory to the NER-coupled repair than the former. Furthermore, the apparent resistance of adducts from DBPDE to be eliminated may reflect the ability of such adducts to escape recognition and/or the subsequent removal by the NER machinery. Further analysis of DNA adduct distribution as a function of incubation time reveals that the dA/dG adduct ratio for BPDE was independent of time (4% dA, 96% dG), whereas the corresponding ratio for DBPDE was significantly increased from 2.9 (74% dA, 26% dG) at 20 min to 4.0 (80% dA, 20% dG) after 6 h of incubation. The results presented here on DNA adduct removal in mammalian cells are in part consistent with recent results on NER-coupled activity on bay- and fjord-region DE-modified oligonucleotides in vitro and further substantiate the hypothesis that the high carcinogenicity of the nonplanar PAHs arise from the ability of the preferentially formed dA adducts to escape recognition by surveillance systems and the subsequent NER-coupled lesion removal.