Effects of the hepatic S9 fraction from aroclor-1254-treated rats on the mutagenicity of benzo[alpha]pyrene and 2-aminoanthracene in the Salmonella/microsome assay.

The mutagenicity of benzo[alpha]pyrene and 2-aminoanthracene for Salmonella typhimurium TA98 in the plate-incorporation test was studied using liver S9 from untreated and aroclor-1254-treated rats. The induction of liver S9 protein, arylhydrocarbon hydroxylase (AHH), and cytochrome P448/450 was followed with time. There was no change in protein concentrations with induction; AHH and cytochrome levels were increased at 1, 3, 5 and 7 days post Aroclor treatment. Benzo[alpha]pyrene mutagenicity was enhanced with Aroclor treatment while 2-aminoanthracene mutagenicity was depressed. The benzo[alpha]pyrene mutagenicity showed a positive correlation with the levels of AHH and cytochrome on the plate; 2-aminoanthracene showed a negative correlation with activity in induced samples.     

Promutagen activation by rodent-liver postmitochondrial fractions in the L5178Y/TK cell mutation assay

Individual S9 microsomal fractions prepared from normal livers of 8 rodent species or strains and from 1 rat strain pretreated with Aroclor 1254, were used to metabolize the promutagens N-acetyl-2-aminofluorene, 1,2--benzanthracene, to metabolize the promutagens N-acetyl-2-aminofluorene, 1,2-benzanthracene, benzo[a]pyrene, and 3-methylcholanthrene to active forms during 3-h co-incubation in the presence of L5178Y/TK^+/− cells. The 8 compatible S9 preparations all converted each of the 4 chemical carcinogens into active mutagens with varied efficiencies except for the Aroclor-induced rat S9/benzanthracene combination which produced only weak activity. Aroclor induction did not notably enhance the mutagenicity of benzo[a]pyrene or 3-methylcholanthrene beyond that activity mediated by the other non-induced preparations. Syrian hamster S9 and, to a lesser degree, C57BL/6J mouse S9 were exceptionally active in converting N-acetyl-2-aminofluorene to toxic and mutagenic metabolites. One source of Swiss mouse liver (Blu : Ha ICR) provided the most active S9 when tested with the 3 polycyclic aromatic hydrocarbons.In general, mutagenicity and cytotoxicity were roughly correlated within S9 + promutagen combinations. Almost all of the methylcholanthrene metabolizing activity was lost by the 12th week when Aroclor-induced rat S9 was held at −20°C, yet this activity remained constant when similar S9 was stored at −80°C for 14 weeks. Surprisingly, some S9 sources including the induced rat-liver preparation converted anthracene to a weak or border-line mutagen. The activation of both 1,2-benzanthracene and anthracene may be linked within each species or strain although Aroclor induction enhanced anthracene mutagenicity yet attenuated the mutagenicity of 1,2-benzanthracene. Collectively, these data underscore the current inchoate state of development for S9 coupled somatic cell mutation assays.     

Effect of induction by DDT on metabolism and mutagenicity of benzo[a]pyrene

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.     

The effect of liver postmitochondrial fraction concentration from Aroclor 1254-treated rats on promutagen activation in L5178Y cells

L5178Y/TK^+/− cells were treated with either N-acetyl-2-aminofluorene (AAF), 2-aminoanthracene (2A), benzanthracene (BA), benzo[a]pyrene (BP), 3-methylcholanthrene (3MCA), or dimethylnitrosamine (DMN) in the presence of varied concentrations (2.5–10% v/v) of liver S9 (9000 × g) postmitochondrial fraction from Aroclor 1254-dosed male CD rats. Consistent S9 concentration-dependent decreases in trifluorothymidine-resistant (TFT^r) mutant induction were noted following 3 h exposure of L5178Y/TK^+/− cells to either 2.5 μg/ml BP, 50 or 67 μg/ml AAF, 0.96 μg/ml 2A, 7.35 μg/ml BA, or 5.4 μg/ml 3MCA. The exception was DMN which yielded a moderate S9 concentration-dependent increase in TFT^r mutant induction when L5178Y/TK^+/− cells were treated for 3 h with 74.1 μg/ml DMN. Depending upon the promutagen being tested, these results suggest two different metabolic events: (1) activation via non-induced enzymes or other factors whose activities are totally S9 volume-dependent (DMN), and (2) deactivation via induced detoxification pathways, a sequence favored by increasing S9 concentration (all others). Utilization of a single “standard” (10%) concentration of liver S9 from Aroclor 1254-treated rats did not appear to provide optimal metabolic activation for 5 of these 6 promutagens.     

Ellipticines and human liver microsomes: Spectral interaction with cytochrome P-450 and hydroxylation. Inhibition of aryl hydrocarbon metabolism and mutagenicity

Some pharmacological properties of ellipticine (E) and its derivatives linked to their interaction with cytochrome P-450 have been investigated with human liver microsomes. 9-Hydroxyellipticine (9-OHE) interacts with human liver cytochrome P-450 exhibiting a type II spectrum (λ_max: 428 nm, K_s = 1.1 μM). After incubation with human liver microsomes the E was converted to 9-OHE; 7-hydroxyellipticine was not produced. The cytotoxic effect of this biotransformation has been evaluated on leukemic L1210 cells, in vitro, and found to be equal to those elicited by liver microsomes of control or phenobarbital (PB) pretreated rats. Moreover, 9-OHE and 9-fluoroellipticine (9-FE) strongly inhibit the benzo[a]pyrene hydroxylase (AHH) activity of human liver microsomes (I₅₀ = 2.6 μM and 1.6 μM, respectively) as well as the mutagenesis induced by the polycyclic aromatic hydrocarbon 2-acetylaminofluorene (AAF); 1 μg/plate of each of these compounds is able to inhibit by more than 50% the mutagenicity of 5 μg/plate AAF.     

Covalent binding of benzo[a]pyrene to cytochrome P-450βNF-B2 and other proteins in reconstituted mixed-function oxidase systems

A reconstituted mixed-function oxidase system, containing the major β-naphthoflavone-induced isozyme of rat liver cytochrome P-450 bound benzo[a]pyrene covalently in the presence of NADPH. NADPH-cytochrome P-450 reductase was required for binding and a maximum rate of adduct formation was obtained at 8 units of reductase per nmol cytochrome P-450. Phosphatidylcholine inhibited this reaction. Benzo[a]pyrene was bound to the cytochrome, but not to the reductase, as shown by sodium dodecyl sulfate (SDS)-polyacrylamide gel electrophoresis. Approximately 6 molecules of benzo[a]pyrene bound to each molecule cytochrome P-450 during prolonged incubations. No binding occurred when the β-naphthoflavone-induced isozyme of cytochrome P-450 was replaced by the major isozyme induced by phenobarbital, but both cytochromes incorporated benzo[a]pyrene to approximately the same extent when they were incubated together in the presence of the reductase and NADPH. Metabolically activated benzo[a]pyrene also bound covalently to purified epoxide hydrodrolase, when this enzyme was added to the reconstituted mixed-function oxidase system.     

Non-enzymic activation of polycyclic aromatic hydrocarbons as mutagens.

Samples of 22 polycyclic aromatic hydrocarbons and related derivatives were subjected to ⁶⁰Co gamma radiation in air, and the irradiated samples were tested for mutagenicity with the Salmonella typhimurium strains TA 98, TA 1535, TA 1537, and TA 1538. Testing was conducted with the bacterial strains alone, thus not fortified with liver-microsomal enzymes or other metabolizing systems. Marked mutagen responses were obtained for several irradiated samples with the TA 98, TA 1537, and TA 1538 strains but not with the TA 1535 strain. Irradiated samples of benzo[a]anthracene, benzanthrone, benozo[g,h,i]perylene, benzo[a]pyrene, chrysene, fluorene, 9-methylanthracene, 1-methylphenanthrene, 2-methylphenanthrene, and pyrene gave positive mutagenic tests and dose-responses, whereas unirradiated control samples of these were inactive. Acenaphthene, phenanthrene, and phenanthrenequinone exhibited toxicity which interfered with interpretation of mutagenicity testing. Samples of 2-methylanthracene and tetracene were mutagenic with or without irradiation. Alizarin, anthracene, anthraquinone, anthrone, dobenzo[a,h]anthracene, picene, and triphenylene negative results. Samples of benzo[a]pyrene adsorbed on silica gel irradiated in air by ⁶⁰Co gamma radiation or by 254 nm ultraviolet light and samples adsorbed on filter paper irradiated by visible light yielded preparations mutagenic towards the TA 98, TA 1537, and TA 1538 strains. These results suggest that parent polycyclic aromatic hydrocarbons not themselves mutagenic towards S. typhimurium may be oxidized in air by radiation-induced processes to products whose mutagenicity resembles that of liver-microsomal metabolites of the parent polycyclic aromatic hydrocarbon.     

Mutagenic and chemical assay of extracts of airborne particulates

The mutagenic activity of extracts of airborne particulates was evaluated in the Salmonella system. The mutagenicity of airborne particulates was not always correlated with the content of benzo[a]pyrene (B[a]P) in the complex mixtures, especially when the samples were collected at different sites.Large-scale fractionation of extracts of airborne particulates was used to determine the content of specific mutagenic chemicals. The neutral fraction of material soluble in cyclohexane and nitromethane contained the polycyclic aromatic hydrocarbon (PAH) compounds, which accounted for 27.9% of the mutagenic activity of the whole extracts. 9 kinds of PAH compound were identified quantitatively by thin-layer chromatography. They included, per 1000 m³ of air, 12.6 μg of benzo[e]pyrene (B[e]P), 10.7 μg of chrysene (CHRY), 10.0 μg of fluoranthene (FL), 6.43 μg of benzo[ghi]perylene (B[ghi]P), 5.75 μg of benz[a]anthracene (B[a]A), 5.33 μg of B[a]P, 3.38 μg of pyrene (PYR), 1.83 μg of coronene (COR), and 1.34 μg of perylene (PERY).Mutagenicity of the ether-soluble acidic, basic and methanol-soluble neutral fractions accounted for 10.9, 9.71 and 6.78% of the total mutagenic activity of crude extract, respectively, when assayed in strain TA98 with liver S9 fraction. The total recovery of mutagenic activity after fractionation was 58%.Two acidic fractions (weak and strong ether-soluble acids) and the methanol-soluble neutral fraction reverted strain TA98 dramatically to prototrophy in the presence of rat-lung S9 fraction more than liver. But the mutagenic chemicals in these fractions remain to be clarified. Direct mutagens were present in essentially all fractions.The particulates, which had diameters ranging from 0.3 to 1.0 μm and were able to penetrate alveoli, contained a high content of mutagens.     

Activation of benzo[a]pyrene and 2-aminoanthracene to bacteria mutagens by mussel digestive gland postmitochondrial fraction

The ability of the mussel postmitochondrial fraction (S9) to activate benzo[a]pyrene (BaP) and 2-aminoanthracene (2AA) to mutagenic metabolites towards Salmonella typhimurium strain TA98 was tested. The mechanisms involved in this activation were investigated and mussel cytochrome P-450-dependent monooxygenases and its NADPH cytochrome c reductase were found to contribute to the activation of BaP. This activation was improved by treating the mussel with 4,5,4′,5′-tetrachlorobiphenyl (TCB) (a 3-methylcholanthrene-type inducer of cytochrome P-450-dependent monooxygenase in marine fish) and was inhibited by α-naphthoflavone (ANF), a cytochrome P-450 inhibitor. However, both BaP activation and cytchrome P-450-related metabolic activities are much weaker in mussels than in vertebrates. Mussel S9 activates aromatic amines more effectively than BaP. Pretreatment of mussels with TCB or addition of ANF in the incubation medium has no effect on 2AA activation. As suggested by Kurelec (1985), aromatic amine metabolism may be supported by a flavoprotein mixed-function amine oxidase which is NADPH-dependent.     

The metabolism of benzo[a]pyrene phenols by rat liver microsomal fractions

The oxidative metabolism of benzo[a]pryrene (B[a]P) phenols catalyzed by liver microsomes in vitro leads to multiple products. High-pressure liquid chromatography analysis of the organic-soluble products formed indicates that regardless of the animal pretreatment regime, 3-hydroxy-B[a]P is metabolized to the 3,6-quinone and to a hydroxylated derivative tentatively identified as 3,9-dihyroxy-B[a]P. However, the distribution of products obtained with 9-hydroxy-B[a]P varied with animal pretreatment. A maximum of three distinct metabolites was obtained when the 9-phenol was metabolized in vitro with microsomes from phenobarbital-pretreated rats and the tentative 3,9-dihydroxy derivative was a common metabolite for all pretreatment regimes. Physical characterization, including mass spectrometry, indicates that all three products have an extra oxygen atom incorporated into their molecular structure from molecular oxygen. Studies utilizing specific inhibitors of the cytochrome P-450-dependent monooxygenase clearly suggest that the formation of dihydroxy or phenol-oxide derivatives is catalyzed by the hemoprotein, cytochrome P-450. These metabolites of the benzo[a]pyrene phenols are most likely related to the putative phenol-oxides of benzo[a]pyrene which have been demonstrated to alkylate DNA and protein. Repetitive scan difference spectrophotometric analysis of incubation mixtures containing rat liver microsomes, 3- or 9-hydroxy-B[a]P, NADPH, and oxygen shows the conversion of the phenols into products which absorb in the region from 400 to 500 nm. During and after the steady state of the reaction, it can be seen that certain of the hydroxy compounds produced are in equilibrium with their respective quinone form and may be involved in an oxygen-coupled redox cycle.     

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 (≅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.     

An aryl hydrocarbon hydroxylating hepatic cytochrome P-450 from the marine fish Stenotomus chrysops

Hepatic microsomal cytochrome P-450 from the untreated coastal marine fish scup, Stenotomus chrysops, was solubilized and resolved into five fractions by ion-exchange chromatography. The major fraction, cytochrome P-450E (M_r = 54,300), was further purified to a specific content of 11.7 nmol heme/mg protein and contained a chromophore absorbing at 447 nm in the CO-ligated, reduced difference spectrum. NH₂-terminal sequence analysis of cytochrome P-450E by Edman degradation revealed no homology with any known cytochrome P-450 isozyme in the first nine residues. S. chrysops liver NADPH-cytochrome P-450 reductase, purified 225-fold (M_r = 82,600), had a specific activity of 45–60 U/mg with cytochrome c, contained both FAD and FMN, and was isolated as the one-electron reduced semiquinone.Purified cytochrome P-450E metabolized several substrates including 7-ethoxycoumarin, acetanilide, and benzo[a]pyrene when reconstituted with lipid and hepatic NADPH-cytochrome P-450 reductase from either S. chrysops or rat. The purified, reconstituted monooxygenase system was sensitive to inhibition by 100 μM 7,8-benzoflavone, and analysis of products in reconstitutions with purified rat epoxide hydrolase indicated a preference for oxidation on the benzo-ring of benzo[a]pyrene consistent with the primary features of benzo[a]pyrene metabolism in microsomes. Cytochrome P-450E is identical to the major microsomal aromatic hydrocarbon-inducible cytochrome P-450 by the criteria of molecular weight, optical properties, and catalytic profile. It is suggested that substantial quantities of this aromatic hydrocarbon-inducible isozyme exist in the hepatic microsomes of some untreated S. chrysops. The characterization of this aryl hydrocarbon hydroxylase extends our understanding of the metabolism patterns observed in hepatic microsomes isolated from untreated fish.     

Activation and detoxication of promutagens by toadfish (Opsanus tau) hepatic postmitochondrial fractions in the Salmonella assay

Three groups of experiments were conducted to characterize the hepatic postmitochondrial fraction (S9) from the oyster toadfish (Opsanus tau) as an activation system for promutagens in the Salmonella assay and to provide an initial evaluation of the extent to which data from standard in vitro assays with mammalian activation systems are predictive of possible genotoxic effects in this marine fish. In the first group of experiments the effects of increasing the concentration of S9 from untreated and 3-methylcholanthrene (MC)- or Aroclor 1254 (AC)-pretreated toadfish and Sprague-Dawley rats on the mutagenicities of different concentrations of 2-aminoanthracene (2AA) and benzo[a]pyrene (BAP) were examined in Salmonella (TA98) plate assays. The maximum levels of 2AA mutagenicity attained by S9 from untreated (UI S9) toadfish and rats were comparable, but UI S9 from toadfish was moreeffective than UI S9 from rats in mediating BAP mutagenicity. MC pretreatment decreased maximum levels of 2AA mutagenicity and increased maximum levels of BAP mutagenicity mediated by S9 from both species. MC pretreatment also altered the pattern of dependence of 2AA mutagenicity on the concentration of S9 protein for S9 from both species. A similar alteration in the pattern of dependence of BAP mutagenicity on the concentration of S9 protein was also observed with S9 from MC-pretreated toadfish. Although AC pretreatment of rats effected changes in the mutagenicities of both test chemicals similar to those effected by MC pretreatment, AC pretreatment of toadfish effected little or no change in the mutagenicities of either test chemical. The changes in the pattern of dependence of 2AA and BAP mutagenicities on the concentration of S9 protein effected by MC pretreatment of toadfish were confirmed in a separate group of experiments. A third group of experiments was designed to examine the effects of α-naphthoflavone (ANF) on the mutagenicities of 2AA and BAP mediated by UI and MC S9 from toadfish. Although ANF did not affect the 2AA mutagenicity mediated by UI S9, a significant decrease in 2AA mutagenicity and a significant increase in BAP mutagenicity mediated by MC S9 and a significant decrease in BAP mutagenicity mediated by UI S9 were observed. These results indicate that 2AA and BAP are effectively activated by toadfish S9 and that, as in rats, these two test chemicals are activated and/or detoxicated by different cytochrome P-450-dependent pathways. These results also support the contention that cytochrome P-450-dependent detoxication pathways can be an important determinant of the mutagenic potency of some promutagens in vitro.     

Degradation of Benzo[a]pyrene by Mycobacterium vanbaalenii PYR-1

Metabolism of the environmental pollutant benzo[a]pyrene in the bacterium Mycobacterium vanbaalenii PYR-1 was examined. This organism initially oxidized benzo[a]pyrene with dioxygenases and monooxygenases at C-4,5, C-9,10, and C-11,12. The metabolites were separated by reversed-phase high-performance liquid chromatography (HPLC) and characterized by UV-visible, mass, nuclear magnetic resonance, and circular dichroism spectral analyses. The major intermediates of benzo[a]pyrene metabolism that had accumulated in the culture media after 96 h of incubation were cis-4,5-dihydro-4,5-dihydroxybenzo[a]pyrene (benzo[a]pyrene cis-4,5-dihydrodiol), cis-11,12-dihydro-11,12-dihydroxybenzo[a]pyrene (benzo[a]pyrene cis-11,12-dihydrodiol), trans-11,12-dihydro-11,12-dihydroxybenzo[a]pyrene (benzo[a]pyrene trans-11,12-dihydrodiol), 10-oxabenzo[def]chrysen-9-one, and hydroxymethoxy and dimethoxy derivatives of benzo[a]pyrene. The ortho-ring fission products 4-formylchrysene-5-carboxylic acid and 4,5-chrysene-dicarboxylic acid and a monocarboxylated chrysene product were formed when replacement culture experiments were conducted with benzo[a]pyrene cis-4,5-dihydrodiol. Chiral stationary-phase HPLC analysis of the dihydrodiols indicated that benzo[a]pyrene cis-4,5-dihydrodiol had 30% 4S,5R and 70% 4R,5S absolute stereochemistry. Benzo[a]pyrene cis-11,12-dihydrodiol adopted an 11S,12R conformation with 100% optical purity. The enantiomeric composition of benzo[a]pyrene trans-11,12-dihydrodiol was an equal mixture of 11S,12S and 11R,12R molecules. The results of this study, in conjunction with those of previously reported studies, extend the pathways proposed for the bacterial metabolism of benzo[a]pyrene. Our study also provides evidence of the stereo- and regioselectivity of the oxygenases that catalyze the metabolism of benzo[a]pyrene in M. vanbaalenii PYR-1.     

Alteration of liver microsomal monooxygenases and substrate competition with aniline hydroxylase from rats chronically fed low-fat and high-fat-containing alcohol diets

Male Sprague-Dawley rats fed ethanol (EtOH) 36% of total calories for four weeks in a liquid diet containing either 34% (HF) or 12% (LF) of calories as fat were studied with respect to induction of microsomal monooxygenases (MFO) and substrate competition with EtOH-inducible aniline hydroxylase. The specific activity and turnover of aniline hydroxylase were induced to similar extents by HF-EtOH and LF-EtOH diets. Whereas, both LF-EtOH and HF-EtOH caused a decrease in the turnover of arylhydrocarbon (benzo[a]pyrene) hydroxylase (AHH) and aldrin epoxidase compared to pair-fed (PF) controls, LF-EtOH but not HF-EtOH increased the turnover of ethoxycoumarin and ethoxyresorufin O-deethylase (ECOD and EROD). The increase in ECOD and EROD and the decrease in AHH by EtOH is contrary to the parallel induction of these activities by J-methylcholanthrene (3-MC) and Aroclor 1254 (Aroclor). Benzo(a)pyrene (BaP) stimulated aniline hydroxylase in the HF-EtOH and PF systems, whereas with LF diet, stimulation was seen only in the EtOH group. Ethoxycoumarin (EC) inhibited aniline hydroxylase by microsomes from EtOH- and pyrazole-treated rats, whereas it stimulated aniline hydroxylase by control microsomes, suggesting that the EC effects were associated with EtOH-inducible cytochrome P-450. Ethoxyresorufin (ER) inhibited aniline hydroxylase in EtOH and PF groups, thus the differential effects of EC were not nonspecific O-deethylase effects. The effects of EtOH feeding on ECOD, EROD, and AHH (ie, substrates for 3-MC-inducible cytochrome P-450) displayed a greater differential between the experimental and control group with the LF- than with the HF-containing diet. The findings suggest that the alteration of certain MFO activities by chronic EtOH ingestion can be modified by the content of dietary fat. Moreover, the competition dynamics of MFO substrates toward EtOH-inducible aniline hydroxylase are altered by EtOH feeding and, in turn, modified by dietary fat.     

New procedure of high-voltage electrophoresis in polyacrylamide gel and its application to the sequencing of nucleic acids.

Addition of primary organic amines, such as n-butylamine, to the mobile phase altered the capacity factors and selectivity of benzo[a]pyrene metabolites obtained with reverse-phase high pressure liquid chromatography on an ODS column. Separation of benzo[a]pyrene phenols in particular was improved with 8 of the 10 available metabolites resolved, including those known to be biologically produced. The method offers sufficiently improved resolution or convenience that it should prove useful in comparative studies of metabolism of benzo[a]-pyrene and other polynuclear aromatic hydrocarbons. Applying the method to analysis of benzo[a]pyrene metabolites produced in vitro by hepatic microsomes from the marine fish Stenotomus versicolor indicated the principal phenolic derivatives produced by this fish were 1-hydroxy-, 3-hydroxy-, 7-hydroxy-, and 9-hydroxybenzo[a]pyrene.     

Enhancement of DNA binding,mutagenicity and carcinogenicity of polycyclic aromatic hydrocarbons after induction of cytochrome P-450 by ellipticines in rats and mice

Pretreatment of rats by ellipticines enhanced the microsomal concentration of cytochrome P-450, benzo[a]pyrene (BP) metabolism and activation and, to a smaller extent, ethoxycoumarin deethylation, but not acetanilide hydroxylation. This increased BP biotransformation was essentially due to the formation of bay-region metabolites, BP 9,10-diol, BP 7,8-diol and 9-hydroxy-BP, or to the formation of BP 7,8-diol-9,10-epoxide- and of 9-hydroxy-BP 4,5-oxide-DNA adducts. In the ellipticine series, 9-fluoroellipticine (9-FE) presents a slight inducing potency compared with the parent and 9-hydroxy molecules. Pretreatment of mice with 9-hydroxyellipticine (9-OHE) led also to an increased mutagenicity of BP and to an augmentation of skin carcinogenesis by 7,12-dimethylbenz[a]anthracene (DMBA). These results clearly show that 9-OHE induces the biosynthesis of cytochrome P-450 which markedly stimulates the mutagenic and carcinogenic potentialities of polycyclic aromatic hydrocarbons (PAH).     

Aryl hydrocarbon hydroxylase in larvae of the southern armyworm (Spodoptera eridania)

Aryl hydrocarbon (benzo[a]pyrene) hydroxylase (AHH) activity in midgut microsomes of southern armyworm (Spodoptera eridania) larvae was induced 11-fold and 5.6-fold respectively following three days of feeding on diets containing pentamethylbenzene or naphthalene (both 0.2% w/v). β-Naphthoflavone and Aroclor 1254 were less effective inducers of AHH activity, phenobarbital was only slightly active and 3-methylcholanthrene caused a decrease in enzyme activity. AHH activity in microsomes from untreated and induced larvae was susceptible to inhibition by α-naphthoflavone, 1-phenylimidazole and piperonyl butoxide. Equilibrium dialysis studies with 1-(4′-³H-phenyl)imidazole showed that control and induced armyworm midgut microsomes contained a class of cytochrome(s) P-450 with a uniformly high affinity for phenylimidazole. It is concluded that AHH activity in the armyworm is catalyzed by a class of cytochrome(s) P-450 with characteristics intermediate between mammalian cytochrome(s) P-450 and P-448.     

Influence of the microsomal inducer and the incubation system on mutagenicity of complex mixtures

The mutagenicity of SRM 1649 and 1650 was tested in the presence of rat liver S9 mix which was induced by polychlorinated biphenyl (PCB) or by the combination of phenobarbital and 5,6-benzoflavone. The S9 mix induced by PCB activated benzo[a]pyrene strongly. The S9 mix induced by phenobarbital-5,6-benzoflavone activated the complex mixtures to approximately the same extent as that induced by PCB. This finding indicates that phenobarbital-5,6-benzoflavone instead of PCB may be suitable as an inducer under some conditions.The preincubation procedure for the mutagenicity test was performed by preincubating the test compound, S9 mix and bacteria for 20 min in a water bath. This procedure was as effective as the plate incorporation test.     

Selenium inhibition of benzo[a]pyrene, 3-methylcholanthrene, and 3-methylcholanthrylene mutagenicity in Salmonella typhimurium strains TA98 and TA100

Selenium (Se) decreased the mutagenicity of benzo[a]pyrene (BP), 3-methylcholanthrene (3MC), and 3-methylcholanthrylene (3MCE) in Salmonella typhimurium strains TA98 and TA100. Metabolism of BP, 3MC and 3MCE to mutagens was accomplished with the liver S9 fraction from Aroclor 1254-treated male Sprague-Dawley rats. Exposure of the bacteria to 4 nmoles BP, 10 nmoles 3MC, or 10 nmoles 3MCE in the presence of S9, and up to 200 nmoles Se as Na2SeO3 resulted in decreased mutagenicities up to 39, 66 and 60% of their respective control activities without Se in TA98 and up to 46, 52 and 64% of their respective control activities without Se in TA100. Se (200 nmoles) alone was not mutagenic in strains TA98 or TA100 with or without S9. BP, 3MC and 3MCE were not mutagenic in either strain without S9. None of the tested concentrations of BP, 3MC, 3MCE and Se were cytotoxic. Assays of the aryl hydrocarbon hydroxylase (AHH) activity in the S9 preparation revealed decreased AHH activity with increase in Se concentration. The decreased mutagenicity and AHH activity were Se (as Na2SeO3) dependent and could not be duplicated by sulfur (S as Na2SO3). Inhibition of AHH activity by Se provides an explanation of the mechanism of Se inhibition of BP, 3MC and 3MCE mutagenicities in S. typhimurium TA98 and TA100.