242 research outputs found

    Genotoxicity: damage to DNA and its consequences

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    A genotoxin is a chemical or agent that can cause DNA or chromosomal damage. Such damage in a germ cell has the potential to cause a heritable altered trait (germline mutation). DNA damage in a somatic cell may result in a somatic mutation, which may lead to malignant transformation (cancer). Many in vitro and in vivo tests for genotoxicity have been developed that, with a range of endpoints, detect DNA damage or its biological consequences in prokaryotic (e.g. bacterial) or eukaryotic (e.g. mammalian, avian or yeast) cells. These assays are used to evaluate the safety of environmental chemicals and consumer products and to explore the mechanism of action of known or suspected carcinogens. Many chemical carcinogens/ mutagens undergo metabolic activation to reactive species that bind covalently to DNA, and the DNA adducts thus formed can be detected in cells and in human tissues by a variety of sensitive techniques. The detection and characterisation of DNA adducts in human tissues provides clues to the aetiology of human cancer. Characterisation of gene mutations in human tumours, in common with the known mutagenic profiles of genotoxins in experimental systems, may provide further insight into the role of environmental mutagens in human cancer

    Benzo[a]pyrene-induced DNA adducts and gene expression profiles in target and non-target organs for carcinogenesis in mice

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    Background: Gene expression changes induced by carcinogens may identify differences in molecular function between target and non-target organs. Target organs for benzo[a]pyrene (BaP) carcinogenicity in mice (lung, spleen and forestomach) and three non-target organs (liver, colon and glandular stomach) were investigated for DNA adducts by 32P-postlabelling, for gene expression changes by cDNA microarray and for miRNA expression changes by miRNA microarray after exposure of animals to BaP. Results: BaP-DNA adduct formation occurred in all six organs at levels that did not distinguish between target and non-target. cDNA microarray analysis showed a variety of genes modulated significantly by BaP in the six organs and the overall gene expression patterns were tissue specific. Gene ontology analysis also revealed that BaP-induced bioactivities were tissue specific; eight genes (Tubb5, Fos, Cdh1, Cyp1a1, Apc, Myc, Ctnnb1 and Cav) showed significant expression difference between three target and three non-target organs. Additionally, several gene expression changes, such as in Trp53 activation and Stat3 activity suggested some similarities in molecular mechanisms in two target organs (lung and spleen), which were not found in the other four organs. Changes in miRNA expression were generally tissue specific, involving, in total, 21/54 miRNAs significantly up- or down-regulated. Conclusions: Altogether, these findings showed that DNA adduct levels and early gene expression changes did not fully distinguish target from non-target organs. However, mechanisms related to early changes in p53, Stat3 and Wnt/β-catenin pathways may play roles in defining BaP organotropism

    Chemical and molecular basis of the carcinogenicity of Aristolochia plants

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    The herbal drug aristolochic acid (AA), which is derived from the Aristolochia species, has been associated with the development of a novel nephropathy, designated as aristolochic acid nephropathy (AAN), and with human urothelial cancer. The major components of the plant extract AA are nitrophenanthrene carboxylic acids, which, after metabolic activation, are genotoxic mutagens. The major activation pathway of AA involves reduction of the nitro group, primarily catalyzed by NAD(P) H: quinone oxidoreductase (NQO1), to an electrophilic cyclic N-acylnitrenium ion that reacts preferentially with purine bases to form covalent DNA adducts. These specific AA-DNA adducts have been identified and detected in experimental animals exposed to AA or botanical products containing AA, and in urothelial tissues from AAN patients. In rodent tumors induced by AA the predominantly formed DNA adduct 7-(deoxyadenosin-N-6-yl) aristolactam I has been associated with the activation of ras oncogenes through the characteristic transversion mutation AT -> TA. This mutation has been identified in the p53 gene of urothelial tumors of a patient with AAN (induced by use of a herbal product) and in several patients suffering from Balkan endemic nephropathy (BEN) with specific AA-DNA adducts. This is a rare example of a human cancer causally linked to a distinct environmental exposure (ie, use of a herbal product), where the carcinogenic process of initiation is well established, linking formation of carcinogen-specific exposure (specific DNA adduct formation) with the presence of characteristic human tumor mutations

    Linking environmental carcinogen exposure to TP53 mutations in human tumours using the human TP53 knock-in (Hupki) mouse model

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    TP53 is one of the most commonly mutated genes in human tumours. Variations in the types and frequencies of mutations at different tumour sites suggest that they may provide clues to the identity of the causative mutagenic agent. A useful model for studying human TP53 mutagenesis is the partial human TP53 knock-in (Hupki) mouse containing exons 4-9 of human TP53 in place of the corresponding mouse exons. For an in vitro assay, embryo fibroblasts from the Hupki mouse can be examined for the generation and selection of TP53 mutations because mouse cells can be immortalized by mutation of Tp53 alone. Thus far, four environmental carcinogens have been examined using the Hupki embryo fibroblast immortalization assay: (a) UV light, which is linked to human skin cancer; (b) benzo[a] pyrene, which is associated with tobacco smoke-induced lung cancer; (c) 3-nitrobenzanthrone, a suspected human lung carcinogen linked to diesel exposure; and (d) aristolochic acid, which is linked to Balkan endemic nephropathy-associated urothelial cancer. In each case, a unique TP53 mutation pattern was generated that corresponded to the pattern found in human tumours where exposure to these agents has been documented. Therefore, the Hupki embryo fibroblast immortalization assay has sufficient specificity to make it applicable to other environmental mutagens that putatively play a role in cancer aetiology. Despite the utility of the current Hupki embryo fibroblast immortalization assay, it has several limitations that could be addressed by future developments, in order to improve its sensitivity and selectivity

    Metabolic activation of carcinogenic aristolochic acid, a risk factor for Balkan endemic nephropathy

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    Aristolochic acid (AA), a naturally occurring nephrotoxin and carcinogen, is associated with tumor development in patients suffering from Chinese herbs nephropathy (now termed aristolochic acid nephropathy, AAN) and may also be a cause for the development of a similar type of nephropathy, the Balkan endemic nephropathy (BEN). Major DNA adducts [7-(deoxyadenosin-N-6-yl)-aristolactam and 7-(deoxyguanosin-N-2-yl)aristolactam] formed from AA after reductive metabolic activation were found in renal tissues of patients with both diseases. Understanding which human enzymes are involved in AA activation and/or detoxication is important in the assessment of an individual's susceptibility to this plant carcinogen. This paper reviews major hepatic and renal enzymes responsible for AA-DNA adduct formation in humans. Phase I biotransformation enzymes play a crucial role in the metabolic activation of AA to species forming DNA adducts, while a role of phase II enzymes in this process is questionable. Most of the activation of AA in human hepatic microsomes is mediated by cytochrome P450 (CYP) 1A2 and, to a lower extent, by CYP1A1; NADPH:CYP reductase plays a minor role. In human renal microsomes NADPH:CYP reductase is more effective in AA activation. Prostaglandin H synthase (cyclooxygenase, COX) is another enzyme activating AA in human renal microsomes. Among the cytosolic reductases, NAD(P)H:quinone oxidoreductase (NQO I) is the most efficient in the activation of AA in human liver and kidney. Studies with purified enzymes confirmed the importance of CYPs, NADPH:CYP reductase, COX and NQO1 in the AA activation. The orientation of AA in the active sites of human CYP1A1, -1A2 and NQO1 was predicted from molecular modeling and explains the strong reductive potential of these enzymes for AA detected experimentally. We hypothesized that inter-individual variations in expressions and activities of enzymes activating AA may be one of the causes responsible for the different susceptibilities to this carcinogen reflected in the development of AA-induced nephropathies and associated urothelial cancer. (c) 2007 Elsevier B.V. All rights reserved

    Influence of cell cycle on responses of MCF-7 cells to benzo[a]pyrene

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    <p>Abstract</p> <p>Background</p> <p>Benzo[a]pyrene (BaP) is a widespread environmental genotoxic carcinogen that damages DNA by forming adducts. This damage along with activation of the aryl hydrocarbon receptor (AHR) induces complex transcriptional responses in cells. To investigate whether human cells are more susceptible to BaP in a particular phase of the cell cycle, synchronised breast carcinoma MCF-7 cells were exposed to BaP. Cell cycle progression was analysed by flow cytometry, DNA adduct formation was assessed by <sup>32</sup>P-postlabeling analysis, microarrays of 44K human genome-wide oligos and RT-PCR were used to detect gene expression (mRNA) changes and Western blotting was performed to determine the expression of some proteins, including cytochrome P450 (CYP) 1A1 and CYP1B1, which are involved in BaP metabolism.</p> <p>Results</p> <p>Following BaP exposure, cells evaded <it>G1 </it>arrest and accumulated in <it>S</it>-phase. Higher levels of DNA damage occurred in <it>S</it>- and <it>G2/M</it>- compared with <it>G0/G1-</it>enriched cultures. Genes that were found to have altered expression included those involved in xenobiotic metabolism, apoptosis, cell cycle regulation and DNA repair. Gene ontology and pathway analysis showed the involvement of various signalling pathways in response to BaP exposure, such as the Catenin/Wnt pathway in <it>G1</it>, the ERK pathway in <it>G1 </it>and <it>S</it>, the Nrf2 pathway in <it>S </it>and <it>G2/M </it>and the Akt pathway in <it>G2/M</it>. An important finding was that higher levels of DNA damage in <it>S- </it>and <it>G2/M</it>-enriched cultures correlated with higher levels of <it>CYP1A1 </it>and <it>CYP1B1 </it>mRNA and proteins. Moreover, exposure of synchronised MCF-7 cells to BaP-7,8-diol-9,10-epoxide (BPDE), the ultimate carcinogenic metabolite of BaP, did not result in significant changes in DNA adduct levels at different phases of the cell cycle.</p> <p>Conclusions</p> <p>This study characterised the complex gene response to BaP in MCF-7 cells and revealed a strong correlation between the varying efficiency of BaP metabolism and DNA damage in different phases of the cell cycle. Our results suggest that growth kinetics within a target-cell population may be important determinants of susceptibility and response to a genotoxic agent.</p

    Mechanisms of Enzyme-Catalyzed Reduction of Two Carcinogenic Nitro-Aromatics, 3-Nitrobenzanthrone and Aristolochic Acid I: Experimental and Theoretical Approaches

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    Abstract: This review summarizes the results found in studies investigating the enzymatic activation of two genotoxic nitro-aromatics, an environmental pollutant and carcinogen 3-nitrobenzanthrone (3-NBA) and a natural plant nephrotoxin and carcinogen aristolochic acid I (AAI), to reactive species forming covalent DNA adducts. Experimental and theoretical approaches determined the reasons why human NAD(P)H:quinone oxidoreductase (NQO1) and cytochromes P450 (CYP) 1A1 and 1A2 have the potential to reductively activate both nitro-aromatics. The results also contributed to the elucidation of the molecular mechanisms of these reactions. The contribution of conjugation enzymes such as N,O-acetyltransferases (NATs) and sulfotransferases (SULTs) to the activation of 3-NBA and AAI was also examined. The results indicated differences in the abilities of 3-NBA and AAI metabolites to be further activated by these conjugation enzymes. The formation of DNA adducts generated by both carcinogens during their reductive activation by the NOQ1 and CYP1A1/

    Tissue-specific in vivo genetic toxicity of nine polycyclic aromatic hydrocarbons assessed using the Muta™Mouse transgenic rodent assay

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    Test batteries to screen chemicals for mutagenic hazard include several endpoints regarded as effective for detecting genotoxic carcinogens. Traditional in vivo methods primarily examine clastogenic endpoints in haematopoietic tissues. Although this approach is effective for identifying systemically distributed clastogens, some mutagens may not induce clastogenic effects; moreover, genotoxic effects may be restricted to the site of contact and/or related tissues. An OECD test guideline for transgenic rodent (TGR) gene mutation assays was released in 2011, and the TGR assays permit assessment of mutagenicity in any tissue. This study assessed the responses of two genotoxicity endpoints following sub-chronic oral exposures of male Muta™Mouse to 9 carcinogenic polycyclic aromatic hydrocarbons (PAHs). Clastogenicity was assessed via induction of micronuclei in peripheral blood, and mutagenicity via induction of lacZ transgene mutations in bone marrow, glandular stomach, small intestine, liver, and lung. Additionally, the presence of bulky PAH-DNA adducts was examined. Five of the 9 PAHs elicited positive results across all endpoints in at least one tissue, and no PAHs were negative or equivocal across all endpoints. All PAHs were positive for lacZ mutations in at least one tissue (sensitivity = 100%), and for 8 PAHs, one or more initial sites of chemical contact (i.e., glandular stomach, liver, small intestine) yielded a greater response than bone marrow. Five PAHs were positive in the micronucleus assay (sensitivity = 56%). Furthermore, all PAHs produced DNA adducts in at least one tissue. The results demonstrate the utility of the TGR assay for mutagenicity assessment, especially for compounds that may not be systemically distributed.</p
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