Mechanism of peroxidase-mediated oxidation of carcinogenic o-anisidine and its binding to DNA
Language English Country Netherlands Media print
Document type Journal Article, Research Support, Non-U.S. Gov't
PubMed
11890934
DOI
10.1016/s0027-5107(01)00295-0
PII: S0027510701002950
Knihovny.cz E-resources
- MeSH
- Aniline Compounds pharmacokinetics toxicity MeSH
- DNA metabolism MeSH
- Glutathione metabolism MeSH
- Spectrometry, Mass, Electrospray Ionization MeSH
- Indomethacin pharmacology MeSH
- Carcinogens pharmacokinetics toxicity MeSH
- Horseradish Peroxidase metabolism MeSH
- Rats MeSH
- Lactoperoxidase metabolism MeSH
- Microsomes drug effects metabolism MeSH
- Mice MeSH
- NAD metabolism MeSH
- Urinary Bladder Neoplasms chemically induced MeSH
- Sheep MeSH
- Oxidation-Reduction MeSH
- Seminal Vesicles drug effects metabolism MeSH
- Binding Sites MeSH
- Animals MeSH
- Check Tag
- Rats MeSH
- Male MeSH
- Mice MeSH
- Animals MeSH
- Publication type
- Journal Article MeSH
- Research Support, Non-U.S. Gov't MeSH
- Names of Substances
- 2-anisidine MeSH Browser
- Aniline Compounds MeSH
- DNA MeSH
- Glutathione MeSH
- Indomethacin MeSH
- Carcinogens MeSH
- Horseradish Peroxidase MeSH
- Lactoperoxidase MeSH
- NAD MeSH
2-Methoxyaniline (o-anisidine) is a urinary bladder carcinogen in both mice and rats. Since the urinary bladder contains substantial peroxidase activity, we investigated the metabolism of this carcinogen by prostaglandin H synthase (PHS), a prominent enzyme in the urinary bladder, and lactoperoxidase as model mammalian peroxidases. Horseradish peroxidase (HRP)-mediated oxidation of o-anisidine was also determined and compared with the reactions catalyzed by mammalian peroxidases. All three peroxidases oxidized o-anisidine via a radical mechanism. Using HPLC combined with electrospray tandem mass spectrometry, we determined that peroxidases oxidized o-anisidine to a diimine metabolite, which subsequently hydrolyzed to form a quinone imine. Two additional metabolites were identified as a dimer linked by an azo bond and another metabolite consisting of three methoxybenzene rings, which exact structure has not been identified as yet. Using [14C]-labeled o-anisidine, we observed substantial peroxidase-dependent covalent binding of o-anisidine to DNA, tRNA and polydeoxynucleotides [poly(dX)]. The 32P-postlabeling assay (a standard procedure and enrichment of adducts by digestion with nuclease P1 or by extraction into 1-butanol prior to 32P-labeling) was employed as the second method to detect and quantitate binding of o-anisidine to DNA. Using these versions of the 32P-postlabeling technique we did not observe any DNA adducts derived from o-anisidine. The o-anisidine-DNA adducts became detectable only when DNA modified by o-anisidine was digested using three times higher concentrations of micrococcal nuclease and spleen phosphodiesterase (MN/SPD). We found deoxyguanosine to be the target for o-anisidine binding in DNA using poly(dX) and deoxyguanosine 3'-monophosphate (dGp). A diimine metabolite of o-anisidine is the reactive species forming adducts in dGp. The results strongly indicate that peroxidases play an important role in o-anisidine metabolism to reactive species, which might be responsible for its genotoxicity, and its carcinogenicity to the urinary bladder in rodents. The limitation of the 32P-postlabeling technique to analyze DNA adducts derived from o-anisidine as a means to estimate its genotoxicity is discussed.
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