Modulating effect of tanshinones on mutagenic activity of Trp-P-1 and benzo[a]pyrene in Salmonella typhimurium.

The modulating effects of the Chinese medicinal plant 'Tan-shen', the radix of Salvia miltiorrhiza Bunge, on the mutagenic activities of Trp-P-1 (3-amino-1,4-dimethyl-5H-pyrido[4,3-b]indole) and B(a)P (benzo[a]pyrene) were investigated using Salmonella typhimurium TA98. Ether- and hot water-extracted 'Tan-shen' enhanced both mutagens at low concentrations, but suppressed them at high concentrations. Extracts by ether treatment were more effective than those extracted by hot water. Dihydrotanshinone I, cryptotanshinone, tanshinone I, and tanshinone IIA were isolated from the ether extract by high performance liquid chromatography (HPLC) and were recognized to be the mutagenic modulators. 4 tanshinones enhanced the mutagenicity of Trp-P-1 by 8-24-fold at 20 micrograms/plate and the enhancement was reduced at the higher concentration. Dihydrotanshinone I suppressed Trp-P-1 activity completely at 100 micrograms/plate.     

Mutagenicity of C24H14 PAH in human cells expressing CYP1A1

Relatively little is known about the mutagenicity of C24H14 PAH, a diverse group of five- and six-ring PAH, some of which are present at trace levels in the environment. To better understand the mutagenicity of this class of compounds, 11 C24H14 PAH, including benzo[a]perylene, benzo[b]perylene, dibenzo[a,e]fluoranthene, dibenzo[a,f]fluoranthene, dibenzo[j,l]fluoranthene, dibenzo[a,h]pyrene, dibenzo[a,i]pyrene, dibenzo[e,l]pyrene, naphtho[1,2-b]fluoranthene, naphtho[2,3-a]pyrene, and naphtho[2,3-e]pyrene, were tested in a mutagenicity assay based on human h1A1v2 cells. h1A1v2 cells are a line of human B-lymphoblastoid cells that have been engineered to express cytochrome P4501A1 (CYP1A1), an enzyme capable of metabolizing promutagenic PAH. Mutagenicity was measured at the thymidine kinase (tk) locus following a 72-h exposure period. Our results show that nine of the compounds were mutagenic. Benzo[a]perylene, dibenzo[a,e]fluoranthene, dibenzo[a,i]pyrene, and naphtho[2,3-a]pyrene were the most potent mutagens, having minimum mutagenic concentrations (MMC) (i.e., the dose at which the induced response was twice that of the negative controls) in the 1-5 ng/ml range. Benzo[b]perylene, dibenzo[a,h]pyrene, dibenzo[a,f]fluoranthene, and naphtho[2,3-e]pyrene were somewhat less potent mutagens, having MMC in the 10-30 ng/ml range. Dibenzo[e,l]pyrene, which had an MMC of 280 ng/ml, was the least potent mutagen. Dibenzo[j,l]fluoranthene and naphtho[1,2-b]fluoranthene were not mutagenic at the doses tested (1-3000 ng/ml). The most mutagenic compounds were also quite toxic. At the highest doses tested, benzo[a]perylene, dibenzo[a,e]fluoranthene, dibenzo[a,i]pyrene, dibenzo[a,h]pyrene, and dibenzo[a,f]fluoranthene induced > 60% killing, and naphtho[2,3-a]pyrene and naphtho[2,3-e]pyrene induced > 50% killing. Benzo[b]perylene, dibenzo[e,l]pyrene, dibenzo[j,l]fluoranthene, and naphtho[1,2-b]fluoranthene induced < 50% killing at the highest doses tested. Comparing these results to a previous study in which nine other C24H14 PAH were tested for mutagenicity in this same assay, it was found that dibenzo[a]pyrene isomers were generally more mutagenic than the other groups of C24H14 PAH tested. These observations are discussed with emphasis given to identifying C24H14 PAH that may be important environmental mutagens.     

Effect of vitamins A, C and glutathione on the mutagenicity of benzo[a]pyrene mediated by S9 from vitamin A-deficient rats

Vitamin A deficiency has been shown to enhance the mutagenicity of benzo[a]pyrene (Narbonne et al., 1985). Here we report that this is not a result of increased benzo[a]pyrene metabolism but might be a consequence of either a lack of vitamin A or a decreased level of scavengers (ascorbic acid and glutathione) in the liver. However, the addition of vitamin A in vitro in the form of retinyl palmitate strongly inhibits the benzo[a]pyrene mutagenicity. An enhancing effect on the mutagenicity of benzo[a]pyrene is observed with addition of ascorbic acid when incubated with high amounts of the precarcinogen. In vivo addition of high levels of glutathione also reduces the mutagenicity of benzo[a]pyrene.     

Use of nitrous acid-dependent decrease in mutagenicity as an indication of the presence of mutagenic primary aromatic amines. Non-specific reactions with phenols and benzo[alpha]pyrene

Treatment of mutagenic primary aromatic amines with nitrous acid is known to decrease their mutagenicity. We examined some factors concerning the validity of using decreases in mutagenicity due to nitrous acid treatment as an indication of the presence of mutagenic primary aromatic amines in complex mixtures. We found that treatment of benzo[alpha]pyrene with nitrous acid for the extended periods of time previously employed leads to formation of three nitrobenzo[alpha]pyrene isomers. Some of the isomers are direct-acting mutagens for S. typhimurium with considerably greater mutagenicity than benzo[alpha]pyrene isomers. In attempts to minimize reaction of chemicals other than aromatic amines, we found that only very brief reaction periods are required for complete reaction of nitrous acid with representative aromatic amines, essentially eliminating their mutagenicity. During such brief reaction periods modification of benzo[alpha]pyrene is negligible, but phenols react readily. Chromatographic analysis indicated that reaction of nitrous acid with aromatic amines leads to the formation of families of products, thereby increasing the complexity of the mixtures in which the amines may occur. Thus, experiments examining the effects of nitrous acid on the mutagenic activity of complex mixtures must be carefully designed, and the results must be interpreted cautiously.     

Mutagenicity of some methylated benzo[a]pyrene derivatives

The mutagenicity of benzo[a]pyrene (BP) and a number of methylated derivatives towards Salmonella typhimurium has been tested. The most mutagenic derivative tested was 6-methylbenzo[a]pyrene which produced about twice the number of revertants as did BP, 11-Methylbenzo[a]pyrene was slightly more mutagenic than BP. All the other compounds tested (7-, 8-, 9- and 10-methylbenzo[a]pyrene and 7,8- and 7,10-dimethylbenzo[a]pyrene) were significantly less active than benzo[a]pyrene. With the exception of 6-methylbenzo[a]pyrene, these results closely parallel the known carcinogenicity of the methylated benzo[a]pyrenes, and support the view that metabolic activation of BP may involve the 7-10 positions which are blocked in the methylated compounds.     

Use of recombinant DNA techniques in cloning DNA repair genes and in the study of metagenesis in mammalian cells

18 polycyclic aromatic hydrocarbons (PAHs) and 7 quinones were tested for mutagenicity using Salmonella typhimurium TA97, TA98 and TA100 with or without metabolic activation. In the presence of metabolic activation, TA97 was more susceptible to mutation than either TA98 or TA100 by many of PAHs tested. PAHs such as 1-methylphenanthrene, fluoranthene, pyrene, benzo[a]pyrene, benzo[e]pyrene and perylene had high mutagenic effects on TA97 in the presence of metabolic activation. 1,6- and 1,8-pyrenequinones were also highly mutagenic on TA97 in the presence or absence of metabolic activation. It appears that pyrene is mutagenic through its metabolic conversion to pyrenequinones.     

Photomutagenicity of 16 polycyclic aromatic hydrocarbons from the US EPA priority pollutant list

The photomutagenicity of 16 polycyclic aromatic hydrocarbons (PAHs), all on the United States Environmental Protection Agency (US EPA) priority pollutant list, was studied. Concomitant exposing the Salmonella typhimurium bacteria strain TA102 to one of the PAHs and light (1.1 J/cm2 UVA+2.1 J/cm2 visible) without the activation enzyme S9, strong photomutagenic response is observed for anthracene, benz[a]anthracene, benzo[ghi]perylene, benzo[a]pyrene, indeno[1,2,3-cd]pyrene, and pyrene. Under the same conditions, acenaphthene, acenaphthylene, benzo[k]fluoranthene, chrysene, and fluorene are weakly photomutagenic. Benzo[b]fluoranthene, fluoranthene, naphthalene, phenanthrene, and dibenz[a,h]anthracene are not photomutagenic. These results indicate that PAHs can be activated by light and become mutagenic in Salmonella TA102 bacteria. At the same time, the mutagenicity for all the 16 PAHs was examined with the standard mutagenicity test with 10% S9 as the activation system. Benzo[b]fluoranthene, benzo[k]fluoranthene, chrysene, acenaphthylene, and fluorene are weakly mutagenic, while the rest of the PAHs are not. In general, the photomutagenicity of PAHs in TA102 does not correlate with their S9-activated mutagenicity in either TA102 or TA98/TA100 since they involve different activation mechanisms.     

Mutagenicity of benzylic acetates, sulfates and bromides of polycyclic aromatic hydrocarbons

Studies were performed to determine the direct mutagenicity of the acetates and some bromides and sulfates of hydroxymethyl polycyclic aromatic hydrocarbons in S. typhimurium strains TA98 and TA100. Benzylic acetates, bromides and sulfates were synthesized and characterized. The compounds tested were benzyl alcohol, 5-hydroxymethylchrysene, 1-hydroxymethylpyrene, 6-hydroxymethylbenzo[a]pyrene, 6-(2-hydroxyethyl)benzo[a]pyrene, 6-hydroxymethylanthanthrene, 9-hydroxymethylanthracene, 9-hydroxymethyl-10-methylanthracene, 7-hydroxymethylbenz[a]anthracene, 7-(2-hydroxyethyl)benz[a]anthracene, 12-hydroxymethylbenz[a]anthracene, 7-hydroxymethyl-12-methylbenz[a]anthracene, 12-hydroxymethyl-7-methylbenz[a]anthracene, 1-hydroxy-3-methylcholanthrene, 2-hydroxy-3-methylcholanthrene, 3-hydroxy-3, 4-dihydrocyclopental[cd]pyrene and 4-hydroxy-3, 4-dihydrocyclopental[cd]pyrene. The benzylic sulfate esters of 6-hydroxymethylbenzo[a]pyrene and 7-hydroxymethylbenz[a]anthracene were the most mutagenic compounds, whereas the aliphatic sulfate ester of 7-hydroxyethylbenz[a]anthracene did not cause an increase in mutations above background. All meso-anthracenic benzylic acetate esters were mutagenic in both strains with various degrees of activity, whereas the corresponding non-benzylic esters were inactive, as expected. Of the non-meso-benzylic acetate esters, only the 3-acetoxy-3, 4-dihydrocyclopenta[cd]pyrene was mutagenic. In the benzylic bromide series, only the eight mesoanthracenic were mutagenic, whereas benzyl bromide and 5-bromomethylchrysene were inactive. The aliphatic bromides, 6-(2-bromoethyl)benzo[a]pyrene and 7-(2-bromoethyl)benz[a]anthracene did not display significant activity. The potencies of the acetate esters more accurately reflect the mutagenicity because the rate of solvolysis did not compete with the reactivity of the esters with bacterial DNA. In the case of benzylic sulfates and bromides, the rate of solvolysis was very rapid and could have diminished the level of mutagenicity, depending on the assay conditions. These results demonstrate that meso-anthracenic benzylic acetates, sulfates and bromides are mutagenic, whereas benzylic acetate esters attached to other carbon atoms are inactive.     

Ataxia-telangiectasia cells are not uniformly deficient in poly(ADP-ribose) synthesis following X-irradiation

Inducibility of 6-thioguanine-resistant (6TGr) mutants and single-strand scission of DNA by cadmium chloride (CdCl2) was investigated in cultured Chinese hamster V79 cells. Frequency of 6TGr mutants increased concentration dependently by 24-h treatment with CdCl2 up to 3 X 10(-6) M but decreased beyond 3 X 10(-6) M. Mutagenic potency of cadmium in the absence of S9 was about half that of benzo[a]pyrene in the presence of S9 at equitoxic concentrations. Treatment of the cultured cells with cadmium after benzo[a]pyrene treatment was not synergistic but additive to the mutagenicity of benzo[a]pyrene. Single-strand scission of DNA by alkaline elution techniques was observed in the cells treated with CdCl2 for 2 h in a concentration-dependent manner. The single-strand scission by cadmium was detected only in combination with proteinase K digestion of the cell lysates, indicating formation of DNA--protein cross-linking by the metal. These biological and biochemical findings indicate that cadmium is mutagenic in mammalian cells, and its mutagenic effect seems to be accompanied by single-strand scission of DNA.     

Mutagenicity of smoked, dried bonito products

Mutagens have been found in smoked, dried bonito products, popular items in Japanese foods. The mutagens were isolated by means of blue cotton, an absorbent cotton preparation with covalently bound trisulfo-copper-phthalocyanine residues, and by means of XAD-2 resin. The mutagenicity was positive in Salmonella typhimurium strain TA98 with metabolic activation. The mutagens are produced during the process of smoking-and-drying bonito (a process called baikan). The activity was much higher than that expected from the content of benzo[a]pyrene. In contrast to benzo[a]pyrene, the mutagens were not inhibited by ellagic acid. The mutagenicity was not abolished by treatment with nitrite. Thin-layer and high-performance liquid chromatographic analysis gave two mutagenic fractions, both of which were distinguishable from benzo[a]pyrene and from the pyrolysis products Trp-P-1, Trp-P-2, Glu-P-1, Glu-P-2, A alpha C and MeA alpha C. The major mutagenic component was not chromatographically distinguishable from IQ and MeIQx, and the minor one was very similar to MeIQ. The smoked, dried bonito products contained free fatty acids, which were inhibitory to the mutagenicity of the bonito products.     

Relationship between mutagenicity and DNA adduct formation in mammalian cells for fjord- and bay-region diol-epoxides of polycyclic aromatic hydrocarbons

Chinese hamster V79 cells were treated with the anti- and syn-diastereomers of the bay- or fjord-region diol-epoxides of four polycyclic aromatic hydrocarbons, namely benzo[a]pyrene (BP), benzo[c]chrysene (BcC), benzo[g]chrysene (BgC) and benzo[c]phenanthrene (BcPh). The frequency of induction of 6-thioguanine-resistant mutations was determined, and the extent of formation of DNA adducts was measured by 32P-postlabelling. When expressed as mutation frequency per nanomoles compound per millilitre incubation medium, this group of chemicals expressed a 160-fold range in potency. In agreement with previous experimental studies, the anti-diol-epoxide of BcC was highly mutagenic, inducing in excess of 3 x 10(4) mutations/10(6) cells per nmol compound/ml. The mutagenic activities of the anti- and syn-diol-epoxides of BP were 10- and 100-fold lower, respectively. Both diol-epoxides of BgC, the syn-BcC and the anti-BcPh derivatives were also highly mutagenic, and only the syn-BcPh diol-epoxide was less mutagenic than the anti-diol-epoxide of BP. Determination of the levels of DNA adducts formed by the diol-epoxides indicated that the most mutagenic compounds were the most DNA reactive, although the fjord-region diol-epoxides gave rise to more complex patterns of adducts than those of the BP diol-epoxides. When the mutagenicity results were expressed as mutations per femtomoles total adducts formed, all compounds showed similar activities. Thus the potent mutagenicity of the fjord region diol-epoxides appears to be due to the high frequency with which they form DNA adducts in V79 cells, rather than to formation of adducts with greater mutagenic potential.     

Enzymatic characterization of the polynuclear aromatic hydrocarbons activating rat-liver preparations used in the mutagenicity test of Ames

Stability studies were performed on the mono-oxygenase system involved, in particular, in the activation of polynuclear aromatic hydrocarbons (PAHs) present in rat-liver preparations used in the Ames mutagenicity test. The results indicated a good stability of the spectral response of the cytochrome-P-450 system, but a much lower stability of its enzymatic activities measured with various substrates, thus showing the inadequacy of the spectral response to characterize the PAH mono-oxygenase activity of the preparations. Epoxide hydrolase activity was found to be stable. Various mono-oxygenase activities were measured in preparations induced with phenobarbital, 3-methylcholanthrene or Aroclor 1254. The activities of two enzymes, benzo[a]pyrene hydroxylase and ethoxyresorufin-O-dealkylase, were found suitable to characterize the capacity of the preparations to metabolize PAH to mutagens. The efficiency of the same preparations to promote the mutagenicity of benzo[a]pyrene and aflatoxin B1 in the Ames test was determined. There was an excellent general correlation between the efficiencies for mutagenic activation of the preparations and the two enzymatic activities mentioned above. Determination of ethoxyresorufin-O-dealkylase (or benzo[a]pyrene hydroxylase) and benzo[a]pyrene 4,5-oxide hydrolase activities is proposed for characterizing the rat-liver preparations used in the Ames test.     

Effects of harman and norharman on the mutagenicity and binding to DNA of benzo[a]pyrene metabolites in vitro and on aryl hydrocarbon hydroxylase induction in cell culture

Harman and norharman, two β-carboline derivatives known to exist in certain foods and to be formed during pyrolysis of tobacco and meat, were tested for mutagenic activity in the presence of benzo[a]pyrene, mouse liver enzymes, and Salmonella typhimurium TA98 in vitro. Both harman and norharman inhibit benzo[a]pyrene mutagenicity, benzo[a]pyrene metabolism (as measured by aryl hydrocarbon hydroxylase activity), and the binding of all benzo[a]pyrene metabolites to DNA in vitro. Moreover, harman and norharman are quite toxic to cultures of hepatoma-derived H-4-II-E and Hepa-1 established cell lines and therefore were found to be very weak inducers of aryl hydrocarbon hydroxylase activity.     

Preliminary studies on the ability of Drosophila microsomal preparations to activate mutagens and carcinogens

Subcellular fractions from Drosophila melanogaster, known to have several xenobiotic-metabolizing enzymatic activities, were investigated with respect to their ability to biotransform compounds that require metabolic activation before exerting mutagenic effects. Nitrofurazone, dimethylnitrosamine, cyclophosphamide and 2-acetylaminofluorene were activated to mutagens upon incubation with Drosophila microsomes or 20000 x g supernatant: mutagenicity was observed in Chinese hamster ovary cells, Escherichia coli strains 343/113/R-9 and 343/113/uvrB, and Salmonella typhimurium TA1538. Under the conditions used, microsomal preparations of Drosophila were not able to activate benzo[a]pyrene to a mutagen for Salmonella typhimurium TA98. The spectrum of mutagenic effects observed shows some correlation with the known mutagenicity of these compounds in vivo in Drosophila melanogaster. Drosophila microsomes appeared to be at least as active as rat-liver microsomes when compared in this type of mutagenicity testing.     

The presence of the mutagenic polycyclic aromatic hydrocarbons benzo[a]pyrene and benz[a]anthracene in creosote P1

Several fractions of creosote P1 separated by TLC showed mutagenicity towards Salmonella typhimurium TA98. Thus mutagenicity is probably caused by the presence of mutagenic aromatic hydrocarbons. The mutagenic polycyclic aromatic hydrocarbons, benzo[a]pyrene and benz[a]anthracene, were detected in concentrations of 0.18 and 1.1% respectively. Because these compounds are probably not essential for the wood-preserving properties of creosote , a more selective composition of the product should be considered.     

Aryl hydrocarbon receptor-mediated activity of mutagenic polycyclic aromatic hydrocarbons determined using in vitro reporter gene assay

Activation of aryl hydrocarbon receptor (AhR) by 30 polycyclic aromatic hydrocarbons (PAHs) was determined in the chemical-activated luciferase expression (CALUX) assay, using two exposure times (6 and 24h), in order to reflect the metabolization of PAHs. AhR-inducing potencies of PAHs were expressed as induction equivalency factors (IEFs) relative to benzo[a]pyrene and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). In 24h exposure assay, the highest IEFs were found for benzo[k]fluoranthene, dibenzo[a,h]anthracene and dibenzo[a,k]fluoranthene (approximately three orders of magnitude lower than TCDD) followed by dibenzo[a,j]anthracene, benzo[j]fluoranthene, indeno[1,2,3-cd]pyrene, and naphtho[2,3-a]pyrene. The 6h exposure to PAHs led to a significantly higher AhR-mediated activity than the 24h exposure (generally by two orders of magnitude), probably due to the high rate of PAH metabolism. The strongest AhR inducers showed IEFs approaching that of TCDD. Several PAHs, including some strong mutagens, such as dibenzo[a,l]pyrene, cyclopenta[cd]pyrene, and benzo[a]perylene, elicited only partial agonist activity. Calculation of IEFs based on EC25 values and/or 6h exposure data is suggested as an alternative approach to estimation of toxic potencies of PAHs with high metabolic rates and/or the weak AhR agonists. The IEFs, together with the recently reported relative mutagenic potencies of PAHs [Mutat. Res. 371 (1996) 123; Mutat. Res. 446 (1999) 1] were combined with data on concentrations of PAHs in extracts of model environmental samples (river sediments) to calculate AhR-mediated induction equivalents and mutagenic equivalents. The highest AhR-mediated induction equivalents were found for benzo[k]fluoranthene and benzo[j]fluoranthene, followed by indeno[1,2,3-cd]pyrene, dibenzo[a,h]anthracene, benzo[a]pyrene, dibenzo[a,j]anthracene, chrysene, and benzo[b]fluoranthene. High mutagenic equivalents in the river sediments were found for benzo[a]pyrene, dibenzo[a,e]pyrene, and naphtho[2,3-a]pyrene and to a lesser extent also for benzo[a]anthracene, benzo[b]fluoranthene, indeno[1,2,3-cd]pyrene, benzo[j]fluoranthene, dibenzo[a,e]fluoranthene and dibenzo[a,i]pyrene. These data illustrate that AhR-mediated activity of PAHs, including the highly mutagenic compounds, occurring in the environment but not routinely monitored, could significantly contribute to their adverse effects.     

Mutagenicity testing of seminal fluid: seminal fluid increases the mutagenicity of the precursor mutagen benzo[a]pyrene in the presence of S9 mix

Small amounts of seminal fluid strongly enhanced the mutagenicity of the precursor mutagen benzo[a]pyrene (BP) in the Salmonella/microsome test. This previously unreported effect was found only in the presence of S9 mix for metabolic activation. The increase far exceeded the additive effect expected from experiments where seminal fluid and BP were tested separately with S9 mix. Testing of the direct-acting mutagen 4-nitro-o-phenylene-diamine (NPD) together with seminal fluid resulted in a lower mutagenic activity than that of NPD alone. Seminal fluid had a bactericidal effect on the Salmonella bacteria, thus only volumes up to 40 microliter could be used per plate. The mutagenic effect of only seminal fluid and S9 mix was slightly increased over controls in a standard Ames test, but was equal to the spontaneous mutation rate with a preincubation test modified according to Kado and coworkers. There were no significant differences between seminal plasma from smokers and non-smokers in any experimental series. Seminal fluid concentrated 20-fold by extraction with the mutagen-removing adsorbant Mutasorb did not have any enhancing effect on the mutagenicity of BP, nor did it exhibit any mutagenic activity in itself with or without S9 mix.     

Benz[j]aceanthrylene: a novel polycyclic aromatic hydrocarbon with bacterial mutagenic activity

Initial studies on the mutagenicity and metabolism of a novel cyclopenta-PAH, benz[j]aceanthrylene, are reported in the Salmonella bacterial system. The spectrum of activity of benz[j]aceanthrylene over the 5 Ames tester strains is similar to that of benzo[a]pyrene, and the dose-response curves for strain TA98 are comparable. Like other biologically active PAH, benz[j]aceanthrylene is a frame-shift mutagen requiring metabolic activation. An interesting feature of the S9 dependence of activity is the low concentration (congruent to 10-fold smaller than for benzo[a]pyrene) at which optimal activity is observed. The 1,2-dihydro-1,2-diol (product of metabolism of the cyclopenta-ring) appears to be the predominant metabolite, and implicates the 1,2-oxide as the ultimate mutagenic species.     

The effect of caffeine on cytotoxicity, mutagenesis, and sister-chromatid exchanges in Chinese hamster cells treated with dihydrodiol epoxide derivatives of benzo[a]pyrene

The effect of caffeine on Chinese hamster V79 cells after treatment with the highly mutagenic (+/-)-7 beta,8 alpha-dihydroxy-9 alpha, 10 alpha-7,8,9,10-tetrahydrobenzo[a]pyrene, and the weaker mutagen (+/-)-7 beta,8 alpha-dihydroxy-9 beta,10 beta-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene, B[a]P-deiol-epoxide II, was studied at both the biological and molecular levels. Caffeine, at nontoxic dose levels, caused a synergistic reduction in cell survival induced by both isomers and also inhibited DNA elongation as measured by alkaline sucrose-gradient analysis of nascent DNA. However, caffeine did not affect the induction of either ouabain-resistant mutants or sister-chromatid exchanges by either isomer. These results suggest that enhanced cell killing by caffeine in benzo[a]pyrene-diol-epoxide treated V79 cells may be related to caffeine's inhibitory effect on DNA elongation. However, inhibition of DNA elongation by caffeine did not influence the resulting induced levels of mutagenesis or sister-chromatid exchanges.     

Mixtures of polycyclic aromatic compounds inhibit mutagenesis in the Salmonella/microsome assay by inhibition of metabolic activation

We observed that complex mixtures of aromatic compounds isolated from a coal-derived oil suppressed the mutagenic activity of the indirect mutagens benzo[a]pyrene, 7,12-dimethylbenz[a]anthracene, 2-aminofluorene, and 2-acetylaminofluorene as measured in the Salmonella/microsome mutagenicity assay, using strain TA98 and metabolic activation with Aroclor-induced rat-liver S9 or microsomes. The mixture also inhibited S9-dependent benzo[a]pyrene metabolism and covalent binding to DNA in a cell-free system. The mixture did not suppress the activity of either the direct acting mutagens 2-nitrofluorene and benzo[a]pyrene diol-epoxide, or of the indirect mutagen N-hydroxy-2-acetylaminofluorene which requires a microsomal deacetylase for metabolic activation. Spectrophotometric measurements showed that components of the mixture bound to microsomal cytochrome P-450. The mixture did not inhibit microsomal NADPH-cytochrome c (P-450) reductase. These observations show that the mixtures inhibited metabolic activation by the microsomal monooxygenase system, probably by binding of unidentified components to cytochrome P-450. The resulting inhibition of mutagenesis may have implications for risk estimates for the mixtures we examined as well as for other types of complex mixtures for which similar inhibitory effects have been observed.