Abstract In this review we discuss the effects of exposure to complex PAH mixtures in vitro and in vivo on mechanisms related to carcinogenesis. Of particular concern regarding exposure to complex ...PAH mixtures is how interactions between different constituents can affect the carcinogenic response and how these might be included in risk assessment. Overall the findings suggest that the responses resulting from exposure to complex PAH mixtures is varied and complicated. More- and less-than additive effects on bioactivation and DNA damage formation have been observed depending on the various mixtures studied, and equally dependent on the different test systems that are used. Furthermore, the findings show that the commonly used biological end-point of DNA damage formation is insufficient for studying mixture effects. At present the assessment of the risk of exposure to complex PAH mixtures involves comparison to individual compounds using either a surrogate or a component-based potency approach. We discuss how future risk assessment strategies for complex PAH mixtures should be based around whole mixture assessment in order to account for interaction effects. Inherent to this is the need to incorporate different experimental approaches using robust and sensitive biological endpoints. Furthermore, the emphasis on future research should be placed on studying real life mixtures that better represent the complex PAH mixtures that humans are exposed to.
Polycyclic aromatic hydrocarbons (PAHs) are formed during incomplete combustion. Domestic wood burning and road traffic are the major sources of PAHs in Sweden. In Stockholm, the sum of 14 different ...PAHs is 100-200 ng/ m3at the street-level site, the most abundant being phenanthrene. Benzoapyrene (BaP) varies between 1 and 2 ng/ m3. Exposure to PAH-containing substances increases the risk of cancer in humans. The carcinogenicity of PAHs is associated with the complexity of the molecule, i.e., increasing number of benzenoid rings, and with metabolic activation to reactive diol epoxide intermediates and their subsequent covalent binding to critical targets in DNA. BaP is the main indicator of carcinogenic PAHs. Fluoranthene is an important volatile PAH because it occurs at high concentrations in ambient air and because it is an experimental carcinogen in certain test systems. Thus, fluoranthene is suggested as a complementary indicator to BaP. The most carcinogenic PAH identified, dibenzoa,lpyrene, is also suggested as an indicator, although it occurs at very low concentrations. Quantitative cancer risk estimates of PAHs as air pollutants are very uncertain because of the lack of useful, good-quality data. According to the World Health Organization Air Quality Guidelines for Europe, the unit risk is 9× 10-5per ng/ m3of BaP as indicator of the total PAH content, namely, lifetime exposure to 0.1 ng/ m3would theoretically lead to one extra cancer case in 100,000 exposed individuals. This concentration of 0.1 ng/ m3of BaP is suggested as a health-based guideline. Because the carcinogenic potency of fluoranthene has been estimated to be approximately 20 times less than that of BaP, a tentative guideline value of 2 ng/ m3is suggested for fluoranthene. Other significant PAHs are phenanthrene, methylated phenanthrenes/anthracenes and pyrene (high air concentrations), and large-molecule PAHs such as dibenza,hanthrancene, benzobfluoranthene, benzokfluoranthene, and indeno1,2,3-cdpyrene (high carcinogenicity). Additional source-specific indicators are benzoghiperylene for gasoline vehicles, retene for wood combustion, and dibenzothiophene and benzonaphthothiophene for sulfur-containing fuels.
Celotno besedilo
Dostopno za:
BFBNIB, DOBA, IZUM, KILJ, NMLJ, NUK, PILJ, PNG, SAZU, SIK, UILJ, UKNU, UL, UM, UPUK
A general description of effects of toxic compounds in mammalian cells is facing several problems. Firstly, most toxic compounds are hydrophobic and partition phenomena strongly influence their ...behaviour. Secondly, cells display considerable heterogeneity regarding the presence, activity and distribution of enzymes participating in the metabolism of foreign compounds i.e. bioactivation/biotransformation. Thirdly, cellular architecture varies greatly. Taken together, complexity at several levels has to be addressed to arrive at efficient in silico modelling based on physicochemical properties, metabolic preferences and cell characteristics. In order to understand the cellular behaviour of toxic foreign compounds we have developed a mathematical model that addresses these issues. In order to make the system numerically treatable, methods motivated by homogenization techniques have been applied. These tools reduce the complexity of mathematical models of cell dynamics considerably thus allowing to solve efficiently the partial differential equations in the model numerically on a personal computer. Compared to a compartment model with well-stirred compartments, our model affords a more realistic representation. Numerical results concerning metabolism and chemical solvolysis of a polycyclic aromatic hydrocarbon carcinogen show good agreement with results from measurements in V79 cell culture. The model can easily be extended and refined to include more reactants, and/or more complex reaction chains, enzyme distribution etc, and is therefore suitable for modelling cellular metabolism involving membrane partitioning also at higher levels of complexity.
Celotno besedilo
Dostopno za:
DOBA, IZUM, KILJ, NUK, PILJ, PNG, SAZU, SIK, UILJ, UKNU, UL, UM, UPUK
The polycyclic aromatic hydrocarbons (PAHs) dibenzoa,lpyrene (DBP) and benzoapyrene (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 μM (−)-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 μM (−)-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 μM (+)-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.
Human embryonic stem cells (hESC) offer a potential unlimited source for functional human hepatocytes, since they can differentiate into hepatocyte-like cells displaying a characteristic hepatic ...morphology and expressing several hepatic markers. Such cells could be used for, e.g. studies of drug metabolism and hepatotoxicity, which however would require a significant expression of drug metabolising enzymes. Thus, we have investigated the expression of cytochrome P450s (CYPs), UDP-glucuronosyltransferases (UGTs), drug transporters, transcription factors and other liver specific genes in hepatocyte-like cells derived from hESC using a simple direct differentiation protocol. The mRNA and protein expression of several important CYPs were determined using low density arrays, real time PCR and Western blotting. Significant CYP expression on the mRNA level was detected in hepatocyte-like cells derived from one out of two different hESC lines tested, which was much higher than in undifferentiated hESC and generally higher than in HepG2 cells. CYP1A2, CYP3A4/7 and low levels of CYP1A1 and CYP2C8/9/19 protein were detected in both lines. The mRNAs for a variety of CYPs and liver specific factors were shown to be inducible in both cell lines, and this was reflected in induced levels of CYP1A2 and CYP3A4/7 protein. This first report on expression of all major CYPs in hepatocyte-like cells derived from hESC represents an important step towards functional hepatocytes, but efforts to further differentiate the cells using optimized protocols are needed before they exhibit similar levels of drug metabolizing enzymes as primary human hepatocytes and liver.
Early events in the cellular response to DNA damage, such as double strand breaks, rely on lesion recognition and activation of proteins involved in maintenance of genomic stability. One important ...component of this process is the phosphorylation of the histone variant H2AX. To investigate factors explaining the variation in carcinogenic potency between different categories of polycyclic aromatic hydrocarbons (PAHs), we have studied the phosphorylation of H2AX (H2AXγ). A549 cells were exposed to benzo
apyrene diol epoxide (+)-
anti-BPDE (a bay-region PAH) and dibenzo
a,
lpyrene diol epoxide (−)-
anti-DBPDE (a fjord-region PAH) and H2AXγ was studied using immunocytochemistry and Western blot. Hydrogen peroxide (H
2O
2) was used to induce oxidative DNA damage and strand breaks. As showed with single cell gel electrophoresis, neither of the diol epoxides resulted in DNA strand breaks relative to H
2O
2. Visualisation of H2AXγ formation demonstrated that the proportion of cells exhibiting H2AXγ staining at 1
h differed between BPDE, 40% followed by a decline, and DBPDE, <10% followed by an increase. With H
2O
2 treatment, almost all cells demonstrated H2AXγ at 1
h. Western blot analysis of the H2AXγ formation also showed concentration and time-dependent response patterns. The kinetics of H2AXγ formation correlated with the previously observed kinetics of elimination of BPDE and DBPDE adducts. Thus, the extent of H2AXγ formation and persistence was related to both the number of adducts and their structural features.
► Differences in repair efficiency of four polycyclic aromatic hydrocarbons could not be related to bay or fjord region structures. ► DBPDE was found to be the most reactive of the four polycyclic ...aromatic hydrocarbon diolepoxides tested here. ► Regarding DNA repair and mutagenicity, DNA adducts of DBPDE behave differently than adducts derived from the other tested PAH–DE.
Polycyclic aromatic hydrocarbons (PAH) are an important class of environmental contaminants many of which require metabolic activation to DNA-reactive bay or fjord region diolepoxides (DE) in order to exert their mutagenic and carcinogenic effects. In this study, the mutagenicity of the bay region diolepoxides (+)-anti-7,8-dihydroxy-9,10-epoxy-7,8,9,10-tetrahydrobenzoapyrene (BPDE) and (±)-anti-1,2-dihydroxy-3,4-epoxy-1,2,3,4-tetrahydrodibenzoa,hanthracene (DBADE) and the fjord region diolepoxides (±)-anti-11,12-dihydroxy-13,14-epoxy-11,12,13,14-tetrahydrodibenzoa,l-pyrene (DBPDE) and (±)-anti-3,4-dihydroxy-1,2-epoxy-1,2,3,4-tetrahydrobenzoc-phenanthrene (BPhDE) was compared in nucleotide excision repair (NER) proficient and deficient hamster cell lines. The 32P-postlabelling assay was applied to analyze DNA adduct levels and the Hprt gene mutation assay for monitoring mutations. Previously, we found that the mutagenicity per adduct was four times higher for DBPDE compared to BPDE in NER proficient cells. In these same cells, the mutagenicity of DBADE and BPhDE adducts was now found to be significantly lower compared to that of BPDE. In NER deficient cells the highest mutagenicity per adduct was found for BPDE and there was a tenfold and fivefold difference when comparing the BPDE data with the DBADE and BPhDE data, respectively. In order to investigate to what extent the mutagenicity of the different adducts in NER proficient cells was influenced by repair or replication bypass, we measured the overall NER incision rate, the rate of adduct removal, the rate of replication bypass and the frequency of induced recombination in the Hprt gene. Since NER turned out to be an important pathway for the yield of mutations, we further analyzed the role of transcription coupled NER versus global genome NER. However, our data demonstrate that neither of these pathways seems to be the sole factor determining the mutation frequency of the four PAH–DE and that the differences in the repair efficiency of these compounds could not be related to the presence of a bay or fjord region in the parent PAH.
Mammalian V79 cells stably expressing human glutathione transferase (GST) A1-1, M1-1, and P1-1 (the allelic variant with Val105 and Ala114) have been constructed and characterized. The cells have ...been used to study the capacity of individual GST isoenzymes in conjunction with GSH to detoxify diol epoxides from dibenzoa,lpyrene (DBPDE), the most carcinogenic polycyclic aromatic hydrocarbon (PAH) identified so far, and diol epoxides from benzoapyrene (BPDE). The relationship between GSH-conjugation and DNA adduct-formation has been investigated as well as factors governing the accessibility of lipophilic diol epoxide substrates for the soluble GSTs in the cells. Relative to control cells, those expressing GSTA1-1 showed the highest rate (about 50-fold increase) to perform GSH-conjugation of (−)-anti-DBPDE (R-absolute configuration at the benzylic oxirane carbon in the fjord-region) followed by GSTM1-1 (25-fold increase) and GSTP1-1 (10-fold increase). GSTA1-1 was found to be strongly inhibited when expressed in cells (10% of fully functional protein). Taking this factor into account, the rates of conjugation found in the cells fairly well reflected the order of catalytic efficiencies (k cat/K m) obtained with the pure enzymes. Increased GSH conjugation of (−)-anti-DBPDE was associated with a reduction in DNA adduct formation. GSTA1-1 inhibited the formation of adducts more than 6-fold and GSTM1-1 and GSTP1-1 about 2-fold. With (+)-anti-BPDE, GSTP1-1-expressing cells demonstrated a substantially higher rate of GSH-conjugate formation than cells with GSTA1-1 and GSTM1-1 cells (33- and 10-fold increase, respectively). Relative to control cells, GSTM1-1 was found to inhibit DNA adduct formation of (+)-anti-BPDE most effectively followed by GSTP1-1 and GSTA1-1 (12-, 4-, and 3-fold, respectively). Values of k cat/K m and estimated oil/water partition coefficients of DBPDE and BPDE were used to calculate the concentration of free diol epoxides in solution and expected rates of GSH conjugate formation in cells, and these theoretical results were compared with the observed ones. With the highly reactive (+)-anti-BPDE, 1−2% of the expected activity was observed, whereas the corresponding values for the less reactive (−)-anti-DBPDE were up to 13%. The most obvious explanations for the low observed rate with (+)-anti-BPDE are rapid and competing reactions such as hydrolysis and/or more unspecific chemical and physical reactions with cellular constituents (proteins, lipids, nucleic acids, etc.). In addition, the difference between the theoretical and observed rates may also reflect participation of factors such as macromolecular crowding and reduced rates of diffusion, factors expected to further restrict the accessibility of GST and the diol epoxides in the intact cell.
Mutations induced by polycyclic aromatic hydrocarbons (PAH) are expected to be produced when error-prone DNA replication occurs across unrepaired DNA lesions formed by reactive PAH metabolites such ...as diol epoxides. The mutagenicity of the two PAH-diol epoxides (+)-anti-7,8-dihydroxy-9,10-epoxy-7,8,9,10-tetrahydrobenzoapyrene (BPDE) and (±)-anti-11,12-dihydroxy-13,14-epoxy-11,12,13,14-tetrahydrodibenzoa,lpyrene (DBPDE) was compared in nucleotide excision repair (NER) proficient and deficient hamster cell lines. We applied the 32P-postlabelling assay to analyze adduct levels and the hprt gene mutation assay for monitoring mutations. It was found that the mutagenicity per target dose was 4 times higher for DBPDE compared to BPDE in NER proficient cells while in NER deficient cells, the mutagenicity per target dose was 1.4 times higher for BPDE. In order to investigate to what extent the mutagenicity of the different adducts in NER proficient cells was influenced by repair or replication bypass, we measured the overall NER incision rate, the rate of adduct removal, the rate of replication bypass and the frequency of induced recombination in the hprt gene. The results suggest that NER of BPDE lesions are 5 times more efficient than for DBPDE lesions, in NER proficient cells. However, DBPDE adducts block replication more efficiently and also induce 6 times more recombination events in the hprt gene than adducts of BPDE, suggesting that DBPDE adducts are, to a larger extent, bypassed by homologous recombination. The results obtained here indicate that the mutagenicity of PAH is influenced not only by NER, but also by replication bypass fidelity. This has been postulated earlier based on results using in vitro enzyme assays, but is now also being recognized in terms of forward mutations in intact mammalian cells.
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