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1.
L Recio  A W Hsie 《Mutation research》1987,178(2):257-269
Biologically reactive metabolites of benzo[a]pyrene (BP) and benzo[a]-pyrene 7,8-diol (BP-diol), formed by the mixed-function oxidase (MFO) system, are substrates for conjugation and detoxication by glutathione (GSH) when catalyzed by glutathione S-transferases (GSHT). We have investigated the detoxication of BP- and BP-diol-induced cytotoxicity and mutagenicity with GSH by supplementing the S9 mix used in the Chinese hamster ovary cells/hypoxanthine-guanine phosphoribosyltransferase (CHO/HGPRT) assay with GSH (6.5 mM) or GSH plus GSHT. The addition of GSH to the S9 mix resulted in a reduction of BP- and BP-diol induced cytotoxicity. GSH plus GSHT eliminated BP-induced cytotoxicity and reduced the mutagenicity of BP. GSH inhibited the mutagenicity at low (essentially non-lethal) concentrations of BP-diol, but did not do so at toxic concentrations. GSH plus GSHT inhibited the cytotoxicity and mutagenicity of BP-diol at concentrations not affected by GSH alone. These studies indicate that biochemical mechanisms of detoxication can affect the biological activity of a carcinogen, such as BP or BP-diol as profoundly as bioactivation by the MFO system.  相似文献   

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3.
Liver microsomal enzymes are essential for the detection of benzo[a]pyrene (B[a]P)-mediated mutagenesis in the Salmonella/mammalian microsome mutagenicity test and, furthermore, this mutagenicity is considerably enhanced by induction of hepatic enzymes involved with drug metabolism. Although Aroclor 1254 is most commonly used for induction of S9 enzymes, DDT is also capable of this induction. This paper reports a comparison of liver S9 fraction induced by the two agents: there is a marked difference in their concentration optima for metabolism of B[a]P; greater numbers of revertant colonies are seen with Aroclor-induced S9, which is optimal at a concentration of 10% (v/v), whereas DDT-induced S9 is optimal at 2.5% (v/v); Aroclor induces aryl hydrocarbon hydroxylase (AHH), cytochrome P-450 and epoxide hydrase while DDT induces only AHH, to about half the level detected in the Aroclor-induced S9 fraction. A comparison of metabolite distribution for Aroclor- and DDT-induced hepatic microsomes reveals quantitative differences only. DDT-induced microsomes yield a greater proportion of B[a]P-4,5-oxide and its metabolic product B[a]P-4,5-dihydrodiol than do Aroclor-induced microsomes. Time course studies on the mutagen half-life measured on the agar plate provides good evidence that metabolites responsible for mutagenicity were different for each inducer.  相似文献   

4.
Mechanisms of co-carcinogenicity of particulates, such as iron oxide and asbestos, and benzo[a]pyrene (B[a]P) are not completely understood. Particulates dramatically alter rates of uptake of B[a]P into membranes, a factor which could account for co-carcinogenicity. However, B[a]P must be activated to reactive forms to be carcinogenic and mutagenic so alterations in metabolism of B[a]P by particulates also could result in co-carcinogenesis. To elucidate mechanisms of particulate-B[a]P co-carcinogenesis, we have correlated rates of uptake of B[a]P into microsomes with metabolism of B[a]P and with mutagenicity of B[a]P in the Ames test. In general, aryl hydrocarbon hydroxylase (AHH) activity paralleled rates of uptake of B[a]P, though some inhibition of AHH activity by particulates which was not attributable to availability of B[a]P was evident. This inhibition was studied further by assaying separately mixed function oxidase and epoxide hydrase activities in the presence of particulates. Both chrysotile and iron oxide inhibited O-deethylation of 7-ethoxyresorufin and hydration of B[a]P-4,5-oxide. To determine effects of this inhibition on activation of B[a]P to reactive forms, we studied profiles of metabolites of B[a]P and mutagenicity of B[a]P. The only alteration in profiles of B[a]P metabolites produced by particulates was that due to effects on rates of uptake. Similarly, mutagenicity of B[a]P was positively correlated with rates of uptake into microsomes. We conclude that the predominant effects of chrysotile and iron oxide are in altering rates of uptake of particle-adsorbed B[a]P. Changes in uptake rates then result in alterations of B[a]P metabolism and mutagenicity.  相似文献   

5.
Selenium added to the incubation mix containing rat-liver S9 modified both the metabolism and mutagenicity of benzo[a]pyrene (BaP) and several of its metabolites. Selenium (Na2SeO3) inhibited the S9-dependent mutagenic effects of BaP on Salmonella typhimurium strain TA100 as indicated by the number of histidine-dependent revertants counted. This inhibition was concentration-dependent over a range of 12.5 to 100 ppm. When used as the substrate the BaP metabolites 7,8-dihydrodiol, 9,10-dihydrodiol and 3-hydroxy also produced significantly fewer revertants in TA100 when selenium was included in the incubation mix. High-performance liquid chromatographic analysis of metabolites from S9-dependent metabolism of BaP indicated that selenium inhibited the formation of 3-hydroxy-BaP, 9,10-dihydrodiol, 7,8-dihydrodiol, 1,3- and 3,6-quinone. Eluting samples on an alumina column to isolate the conjugated metabolites showed that selenium caused 12% less binding to glucuronides, no significant differences in binding to sulfate esters or glutathione but the amount of unmetabolized BaP and unconjugated metabolites was increased by 48%. These results suggest that selenium inhibits S9-dependent BaP metabolism therefore reducing the mutagenic effects of this compound.  相似文献   

6.
The inhibitory effects of hemin and related compounds on the mutagenicity of benzo[a]pyrene (BP) were investigated in Chinese hamster V79 cells co-cultivated with X-irradiated hamster embryo cells. Mutant V79 cells were selected by their resistance to ouabain. The mutation frequency induced by BP was substantially inhibited dose dependently by hemin. The mutagenicity of BP (1 microgram/ml) on V79 cells was reduced to 6.5% by hemin, 52% by biliverdin, 73% by protoporphyrin and 85% by chlorophyllin at the highest concentration of the compounds tested (15 microM).  相似文献   

7.
The effect of norharman on the metabolism of benzo[a]pyrene by rat-liver microsomes was studied. Separation of the metabolites into hydrophilic and hydrophobic fractions showed that norharman inhibited the conversion of hydrophobic metabolites to hydrophilic ones.Analysis of the hydrophobic metabolites by high-pressure liquid chromatography showed that norharman also inhibited the disappearance of benzo[a]pyrene itself. However, large amounts of hydrophobic metabolites, such as phenol, quinones and diols, were formed in the presence of norharman, and formation of the strong mutagen 7,8-dihydroxybenzo[a]pyrene was increased 10-fold by norharman. The increase in formation of this compound may be one of the chief reasons why norharman enhances the mutagenicity of benzo[a]pyrene on Salmonella typhimurium.  相似文献   

8.
Benzo[a]pyrene (BP) and two of its major metabolites, the ultimate mutagen BP-4,5-oxide and the proximate mutagen trans-7,8-dihydro-7,8-dihydroxybenzo[a]pyrene (BP-7,8-diol) were investigated for mutagenicity in Salmonella typhimurium TA1538, TA98 and TA100 using an intrasanguineous host-mediated assay. BP and BP-4,5-oxide were not mutagenic under any experimental conditions. BP-7,8-diol was inactive with the strain TA1538 but was mutagenic with the strains TA98 and TA100. The effect was potentiated by pretreatment of the host mice with the cytochrome P-450 inducer 5,6-benzoflavone. We conclude: (i) one of the reasons for the observed insensitivity of the intrasanguineous host-mediated assay towards BP is that BP-4,5-oxide, which contributes to the microsome-mediated mutagenicity of BP, is inactive in the host-mediated assay; (ii) the finding that BP-7,8-diol is mutagenic in the host-mediated assay demonstrates that the lack of mutagenicity of BP is not intrinsic; (iii) the potentiated mutagenicity after treatment of the hosts with 5,6-benzoflavone suggests that cytochrome P-450 is more important in the activation of BP-7,8-diol in this system than other enzymes (e.g. prostaglandin synthase) that can also activate this compound in vitro.  相似文献   

9.
The effect of phenothiazine and 11 of its derivatives on the mutagenicity of benzo[a]pyrene, as measured by the Ames test was investigated. Significant anti-mutagenic activity was detected for 10 phenothiazine derivatives, with the 2-chloro derivative being the most effective inhibitor tested and promazine the only phenothiazine drug tested which has no demonstrable inhibitory activity. It is considered that the anti-mutagenic activity and therefore potentially anticarcinogenic activity of these derivatives should be of interest to epidemiologists.  相似文献   

10.
(±)-7β,8α-Dihydroxy-9β,10β-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (diol epoxide-1) and (±)-7β,8α-dihydroxy-9α,10α-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (diol epoxide-2) are highly mutagenic diol epoxide diastereomers that are formed during metabolism of the carcinogen (±)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene. Remarkable stereoselectivity has been observed on metabolism of the optically pure (+)- and (?)-enantiomers of the dihydrodiol which are obtained by separation of the diastereomeric diesters with (?)-α-methoxy-α-trifluoromethylphenylacetic acid. The high stereoselectivity in the formation of diol epoxide-1 relative to diol epoxide-2 was observed with liver microsomes from 3-methylcholanthrene-treated rats and with a purified cytochrome P-448-containing monoxygenase system where the (?)-enantiomer produced a diol epoxide-2 to diol epoxide-1 ratio of 6 : 1 and the (+)-enantiomer produced a ratio of 1 : 22. Microsomes from control and phenobarbital-treated rats were less stereospecific in the metabolism of enantiomers of BP 7,8-dihydrodiol. The ratio of diol epoxide-2 to diol epoxide-1 formed from the (?)- and (+)-enantiomers with microsomes from control rats was 2 : 1 and 1 : 6, respectively. Both enantiomers of BP 7,8-dihydrodiol were also metabolized to a phenolic derivative, tentatively identified as 6,7,8-trihydroxy-7,8-dihydrobenzo[a]pyrene, which accounted for ~30% of the total metabolites formed by microsomes from control and phenobarbital-pretreated rats whereas this metabolite represents ~5% of the total metabolites with microsomes from 3-methylcholanthrene-treated rats. With benzo[a]pyrene as substrate, liver microsomes produced the 4,5-, 7,8- and 9,10-dihydrodiol with high optical purity (>85%), and diol epoxides were also formed. Most of the optical activity in the BP 7,8-dihydrodiol was due to metabolism by the monoxygenase system rather than by epoxide hydrase, since hydration of (±)-benzo[a]pyrene 7,8-oxide by liver microsomes produced dihydrodiol which was only 8% optically pure. Thus, the stereospecificity of both the monoxygenase system and, to a lesser extent, epoxide hydrase plays important roles in the metabolic activation of benzo[a]pyrene to carcinogens and mutagens.  相似文献   

11.
(±)-7β,8α-Dihydroxy-9β,10β-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (BP 7,8-diol-9,10-epoxide) is a suspected metabolite of benzo[a]pyrene that is highly mutagenic and toxic in several strains of Salmonellatyphimurium and in cultured Chinese hamster V79 cells. BP 7,8-diol-9,10-epoxide was approximately 5, 10 and 40 times more mutagenic than benzo[a]pyrene 4,5-oxide (BP 4,5-oxide) in strains TA 98 and TA 100 of S.typhimurium and in V79 cells, respectively. Both compounds were equally mutagenic to strain TA 1538 and non-mutagenic to strain TA 1535 of S.typhimurium. The diol epoxide was toxic to the four bacterial strains at 0.5–2.0 nmole/plate, whereas BP 4,5-oxide was nontoxic at these concentrations. In V79 cells, the diol epoxide was about 60-fold more cytotoxic than BP 4,5-oxide.  相似文献   

12.
Benzo[a]pyrene (BaP), an environmental carcinogen, shows genotoxicity after metabolic transformation into the bay-region diol epoxide, BaP-7,8-diol 9,10-epoxide. 10-Azabenzo[a]pyrene (10-azaBaP), in which a ring nitrogen is located in the bay-region, is also a carcinogen and shows mutagenicity in the Ames test in the presence of the rat liver microsomal enzymes. In order to evaluate the effect of aza-substitution on in vivo genotoxicity, BaP and 10-azaBaP were assayed for their in vivo mutagenicity using the lacZ-transgenic mouse (MutaMouse). BaP was potently mutagenic in all of the organs examined (liver, lung, kidney, spleen, forestomach, stomach, colon, and bone marrow), as described in our previous report, whereas, 10-azaBaP was slightly mutagenic only in the liver and colon. The in vitro mutagenicities of BaP and 10-azaBaP were evaluated by the Ames test using liver homogenates prepared from several sources, i.e. CYP1A-inducer-treated rats, CYP1A-inducer-treated and non-treated mice, and humans. BaP showed greater mutagenicities than 10-azaBaP in the presence of a liver homogenate prepared from CYP1A-inducer-treated rodents. However, 10-azaBaP showed mutagenicities similar to or more potent than BaP in the presence of a liver homogenate or S9 from non-treated mice and humans. These results indicate that 10-aza-substitution markedly modifies the nature of mutagenicity of benzo[a]pyrene in both in vivo and in vitro mutagenesis assays.  相似文献   

13.
14.
Ellagic acid, a common plant phenol, was shown to be a potent inhibitor of epidermal microsomal aryl hydrocarbon hydroxylase (AHH) activity in vitro, and of benzo[a]pyrene (BP)-binding to both calf thymus DNA in vitro and to epidermal DNA in vivo. The in vitro addition of ellagic acid (0.25-2.0 microM) resulted in a dose-dependent inhibition of AHH activity in epidermal microsomes prepared from control or carcinogen-treated animals. The I50 of ellagic acid for epidermal AHH was 1.0 microM making it the most potent inhibitor of epidermal AHH yet identified. In vitro addition of ellagic acid to microsomal suspensions prepared from control or coal tar-treated animals resulted in 90% inhibition of BP-binding to calf thymus DNA. Application of ellagic acid to the skin (0.5-10.0 mumol/10 gm body wt) caused a dose-dependent inhibition of BP-binding to epidermal DNA. Our results suggest that phenolic compounds such as ellagic acid may prove useful in modulating the risk of cutaneous cancer from environmental chemicals.  相似文献   

15.
16.
The effect of norharman on the metabolism of benzo[alpha]pyrene by rat-liver microsomes was studied. Separation of the metabolites into hydrophilic and hydrophobic fractions showed that norharman inhibited the conversion of hydrophobic metabolites to hydrophilic ones. Analysis of the hydrophobic metabolites by high-pressure liquid chromatography showed that norharman also inhibited the disappearance of benzo[alpha]pyrene itself. However, large amounts of hydrophobic metabolites, such as phenol, quinones and diols, were formed in the presence of norharman, and formation of the strong mutagen 7,8-dihydroxybenzo[alpha]pyrene was increased 10-fold by norharman. The increase in formation of this compound may be one of the chief reasons why norharman enhances the mutagenicity of benzo[alpha]pyrene on Salmonella typhimurium.  相似文献   

17.
18.
Benzo[a]pyrene (BaP), an environmental carcinogen, shows genotoxicity after metabolic transformation into the bay-region diol epoxide, BaP-7,8-diol 9,10-epoxide. 10-Azabenzo[a]pyrene (10-azaBaP), in which a ring nitrogen is located in the bay-region, is also a carcinogen and shows mutagenicity in the Ames test in the presence of the rat liver microsomal enzymes. In order to evaluate the effect of aza-substitution on in vivo genotoxicity, BaP and 10-azaBaP were assayed for their in vivo mutagenicity using the lacZ-transgenic mouse (Muta™Mouse). BaP was potently mutagenic in all of the organs examined (liver, lung, kidney, spleen, forestomach, stomach, colon, and bone marrow), as described in our previous report, whereas, 10-azaBaP was slightly mutagenic only in the liver and colon. The in vitro mutagenicities of BaP and 10-azaBaP were evaluated by the Ames test using liver homogenates prepared from several sources, i.e. CYP1A-inducer-treated rats, CYP1A-inducer-treated and non-treated mice, and humans. BaP showed greater mutagenicities than 10-azaBaP in the presence of a liver homogenate prepared from CYP1A-inducer-treated rodents. However, 10-azaBaP showed mutagenicities similar to or more potent than BaP in the presence of a liver homogenate or S9 from non-treated mice and humans. These results indicate that 10-aza-substitution markedly modifies the nature of mutagenicity of benzo[a]pyrene in both in vivo and in vitro mutagenesis assays.  相似文献   

19.
Antioxidants inhibit the rat liver microsomal mixed-function-oxidase-catalysed hydroxylation of benzo[a]pyrene. These antioxidants also decrease the formation of mutagenic products from benzo[a]pyrene as judged by the Ames bacterial-mutagenicity assay [B.N. Ames, J. McCann & E. Yamazaki (1975) Mutat. Res. 31, 347-364]. It is suggested that antioxidants exert their protective effect against cancer by inhibiting the formation of carcinogenic metabolites.  相似文献   

20.
We have investigated the effect of benzo[a]pyrene (B[a]P), a carcinogen of tobacco smoke and an agonist for the aryl hydrocarbon receptor (AHR), on hypoxia-induced angiogenesis. Ischemia was induced by femoral artery ligation in wild-type and AHR-null mice, and the animals were subjected to oral administration of B[a]P (125 mg/kg) once a week. Exposure to B[a]P up-regulated the expression of metallothionein in the ischemic hindlimb and markedly inhibited ischemia-induced angiogenesis in wild-type mice. The amounts of interleukin-6 and of vascular endothelial growth factor (VEGF) mRNA in the ischemic hindlimb of wild-type mice were reduced by exposure to B[a]P. These various effects of B[a]P were markedly attenuated in AHR-null mice. Our observations suggest that the loss of the inhibitory effect of B[a]P on ischemia-induced angiogenesis apparent in AHR-null mice may be attributable to maintenance of interleukin-6 expression and consequent promotion of angiogenesis through up-regulation of VEGF expression.  相似文献   

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