Clastogenicity of 1-nitropyrene, dinitropyrenes, fluorene and mononitrofluorenes in cultured Chinese hamster cells

The chromosomal aberration test using a Chinese hamster lung cell line (CHL) was carried out on 1-nitropyrene (NP), 3 dinitropyrenes (DNPs), fluorene and 4 mononitrofluorenes with and without metabolic activation (rat S9 mix). The 3 DNPs (1,3-, 1,6- and 1,8-DNP) induced chromosomal aberrations in the absence of S9 mix. The frequencies of cells with aberrations after treatment for 48 h were 43% at 2 micrograms/ml of 1,3-DNP, 55% at 0.1 microgram/ml of 1,6-DNP and 45% at 0.025 microgram/ml of 1,8-DNP, indicating the order of clastogenic potency as 1,8- greater than 1,6- greater than 1,3-DNP. On the other hand, 1-NP, which is known to be a direct-acting mutagen in bacteria, was negative in the chromosomal aberration test without S9 mix, but clearly positive with S9 mix. This effect was dependent on the concentration of the S9 fraction in the reaction mixture. High-pressure liquid chromatography analysis showed that 1-NP was converted by S9 mix to several metabolites, including 1-aminopyrene (AP). The clastogenic activity of 1-AP, however, was equivocal without S9 mix, suggesting that active clastogens other than 1-AP exist. Fluorene induced chromosomal aberrations only in the presence of S9 mix (61.8% at 25 micrograms/ml). 1-, 2-, 3- and 4-nitrofluorene (NF) were more clastogenic in the presence of S9 mix than in the absence of S9 mix, suggesting that NFs were converted to more active clastogens by S9 mix.     

Mutagenic effects of nitropyrenes in a soybean test system

The mutagenic activity of 1-nitropyrene (1-NP), 1,3-dinitropyrene (1,3-DNP), 1,6-dinitropyrene (1,6-DNP) and 1,8-dinitropyrene (1,8-DNP) was assayed in heterozygous soybean plants (Y11y11), based on the appearance of mutational spots (yellow, dark green and twin) on the leaves. 1-NP, 1,3-DNP, 1,6-DNP and 1,8-DNP were direct-acting mutagens in a soybean test system, and mutagenicity was enhanced by addition of pyrene as a precursor. The mutagenicity of dinitropyrenes was enhanced by pretreatment with hepatic microsomal fractions of Aroclor 1254-treated rats. Binary and ternary isomeric mixtures of dinitropyrenes produced synergistic mutational response in the test system. The numbers of yellow and dark green spots per leaf increased by treatment with nitropyrenes. The frequency of twin spots did not change. Nitropyrenes stimulated the induction of forward and reverse mutations in soybeans. The number of light green spots (Y11y11) per leaf on homozygous soybeans (y11y11) increased markedly by treatment with 1-NP, 1,3-DNP, 1,6-DNP, and 1,8-DNP. These nitropyrenes would thus appear to cause point mutation and segmental loss as major effects.     

Mutagenicity of mono-, di- and tri-nitropyrenes in Chinese hamster ovary cells

1-Nitropyrene (1-NP), 1,3-dinitropyrene (1,3-DNP), 1,6-dinitropyrene (1,6-DNP), 1,8-dinitropyrene (1,8-DNP) and 1,3,6-trinitropyrene (1,3,6-TNP) were tested for mutagenicity in cultured Chinese hamster ovary (CHO) cells. Mutation at the hypoxanthine-guanine phosphoribosyl transferase gene locus was quantified. While 1-NP and 1,3-DNP had only marginal direct-acting mutagenicity, 1,6-DNP, 1,8-DNP and 1,3,6-TNP showed definite mutagenicity, with specific mutagenic activities of 8.1, 21 and 54 mutants/10⁶ survivors/μg·ml⁻¹ respectively. The mutagenicity of 1-NP increased with increasing concentrations of Aroclor-1254 induced liver homogenate (S9) in the treatment medium. However, S9 at all concentrations tested decreased the mutagenicity of 1,6-DNP and 1,8-DNP. S9 at low concentrations enhanced the mutagenicity of 1,3-DNP and 1,3,6-TNP and that at high concentrations decreased their mutagenicity. The positive mutagenic response of the nitropyrenes suggests that they are potentially carcinogenic, and that further research into their possible human health risk should be performed.     

Nitropyrenes are inducers of polyoma viral DNA synthesis

The biological activity of a series of nitropyrenes was assayed by measuring their ability to induce the asynchronous replication of viral DNA in rat fibroblasts transformed by a ts-a mutant of polyoma virus. Concentrations of 10-30 micrograms/ml of 1-nitropyrene (1-NP) induced viral replication, and this effect was enhanced by addition of rat-liver S9 microsomal fraction (300 micrograms/ml) to the culture medium. The response was less than that obtained with 0.1 micrograms/ml of the activated metabolite of benzo[a]pyrene (BP), BP trans-7,8-dihydrodiol-9,10 epoxide (anti) (BPDE). A series of di-, tri-, and tetra-nitropyrenes were also found to induce polyoma DNA replication, in the absence of exogenous microsomal activation, displaying strongly positive effects at 0.5-2.0 microgram/ml. Dose-response curves with 1,6-dinitropyrene (1,6-DNP) from 0.01 to 0.5 microgram/ml indicated that this compound was approximately equipotent with BPDE for induction of polyoma DNA synthesis. Studies of drug metabolism, DNA binding and DNA adduct formation indicate that 1,6-DNP is metabolized in this cell line, binds to DNA, and forms stable adducts. The level of DNA modification seen with 1,6-DNP is higher than that observed under comparable conditions with an equivalent dose of BPDE. These findings provide additional evidence that the nitropyrene class of compounds can exert biological effects in mammalian cells, and that the dinitropyrenes are more potent than 1-NP.     

Nitropyrene-induced DNA repair in Clara cells and alveolar type-II cells isolated from rabbit lung

DNA excision repair, as measured by unscheduled DNA synthesis (UDS), was examined in different cell types of rabbit lung exposed to nitropolycyclic aromatic hydrocarbons (NO-PAH) in vitro. Dose-related increases in UDS were observed. 1,6-Dinitropyrene (1,6-DNP) and 1,8-dinitropyrene (1,8-DNP) induced UDS more effectively in alveolar type-II cells compared with Clara cells. On the other hand, 1-nitropyrene (1-NP) caused a weak UDS response in Clara cells but no DNA repair in alveolar type-II cells.     

Purified NAD(P)H-quinone oxidoreductase enhances the mutagenicity of dinitropyrenes in vitro.

The effect of highly purified rat liver cytosolic NAD(P)H-quinone oxidoreductase [EC 1.6.99.2] on the mutagenicity of 1,3- 1,6- and 1,8-dinitropyrene (DNP) was studied in the Ames Salmonella typhimurium mutagenicity assay. NAD(P)H-quinone oxidoreductase over the range of 0.02-0.8 micrograms/plate (38-1500) units increased up to threefold the mutagenicity of all three DNPs in S. typhimurium TA 98. In TA98NR, a strain deficient in "classical" nitro-reductase, the mutagenicity of 1,6- and 1,8-DNP was essentially unchanged, whereas that of 1,3-DNP was markedly reduced. NAD(P)H-quinone oxidoreductase enhanced the mutagenicity of 1,6- and 1,8-DNP to approximately equivalent extents in TA98NR and TA98. The mutagenicity of 1,3-DNP in TA98NR was potently enhanced by the addition of NAD(P)H-quinone oxidoreductase in a dose-responsive manner. In the presence of 0.8 micrograms NAD(P)H-quinone oxidoreductase, 1,3-DNP displayed a mutagenic response in TA98NR that was comparable to that obtained in TA98. NAD(P)H-quinone oxidoreductase was found to increase the mutagenicity of 1,6- but not 1,3- or 1,8-DNP to mutagenic intermediates in TA98/1,8-DNP6, a strain deficient in O-acetyltransferase activity. The results suggest that NAD(P)H-quinone oxidoreductase not only catalyzes reduction of the parent DNP but also that of partially reduced metabolites generated from that DNP. Such reductive metabolism may lead to increased formation of the penultimate mutagenic species.     

Identification of dinitropyrenes in diesel-exhaust particles. Their probable presence as the major mutagens

The direct-acting mutagens in diesel particulate extracts were identified. It is concluded that the major mutagens are in all probability 1,6- and 1,8-dinitropyrene (DNP). 1-Nitropyrene (NP) and 3-nitrofluoranthene (NF) were also present. The DNP isomers contributed 43% of the total mutagenic activity of the crude extracts, whereas 1-NP (or 3-NF) was responsible for less than 10% of the activity. The quantities of 1,6- and 1,8-DNP were 1.2 and 3.4 ppm of the crude extracts, respectively, and the induction of both DNPs in the diesel particulate matter corresponded to about 1.7-4.8% by weight of the 1-NP content (70.5 ppm in the crude extracts).     

Purified NAD(P)H-quinone oxidoreductase enhances the mutagenicity of dinitropyrenes in vitro

The effect of highly purified rat liver cytosolic NAD(P)H-quinone oxidoreductase [EC 1.6.99.2] on the mutagenicity of 1,3- 1,6- and 1,8-dinitropyrene (DNP) was studied in the Ames Salmonella typhimurium mutagenicity assay. NAD(P)H-quinone oxidoreductase over the range of 0.02–0.8 μ g/plate (38–1500) units increased up to threefold the mutagenicity of all three DNPs in S. typhimurium TA 98. In TA98NR, a strain deficient in “classical” nitroreductase, the mutagenicity of 1,6- and 1,8-DNP was essentially unchanged, whereas that of 1,3-DNP was markedly reduced. NAD(P)H-quinone oxidoreductase enhanced the mutagenicity of 1,6- and 1,8-DNP to approximately equivalent extents in TA98NR and TA98. The mutagenicity of 1,3-DNP in TA98NR was potently enhanced by the addition of NAD(P)H-quinone oxidoreductase in a dose-responsive manner. In the presence of 0.8 μg NAD(P)H-quinone oxidoreductase, 1,3-DNP displayed a mutagenic response in TA98NR that was comparable to that obtained in TA98. NAD(P)H-quinone oxidoreductase was found to increase the mutagenicity of 1,6- but not 1,3- or 1,8-DNP to mutagenic intermediates in TA98/1,8-DNP₆, a strain deficient in O-acetyltransferase activity. The results suggest that NAD(P)H-quinone oxidoreductase not only catalyzes reduction of the parent DNP but also that of partially reduced metabolites generated from that DNP. Such reductive metabolism may lead to increased formation of the penultimate mutagenic species.     

Mutagenicity of mono-, di- and tri-nitropyrenes in Chinese hamster ovary cells

1-Nitropyrene (1-NP), 1,3-dinitropyrene (1,3-DNP), 1-6-dinitropyrene (1,6-DNP), 1,8-dinitropyrene (1,8-DNP) and 1,3,6-trinitropyrene (1,3,6-TNP) were tested for mutagenicity in cultured Chinese hamster ovary (CHO) cells. Mutation at the hypoxanthine-guanine phosphoribosyl transferase gene locus was quantified. While 1-NP and 1,3-DNP had only marginal direct-acting mutagenicity, 1,6-DNP, 1,8-DNP and 1,3,6-TNP showed definite mutagenicity, with specific mutagenic activities of 8.1, 21 and 54 mutants/10(6) survivors/micrograms . ml-1 respectively. The mutagenicity of 1-NP increased with increasing concentrations of Aroclor-1254 induced liver homogenate (S9) in the treatment medium. However, S9 at all concentrations tested decreased the mutagenicity of 1,6-DNP and 1,8-DNP. S9 at low concentrations enhanced the mutagenicity of 1,3-DNP and 1,3,6-TNP and that at high concentrations decreased their mutagenicity. The positive mutagenic response of the nitropyrenes suggests that they are potentially carcinogenic, and that further research into their possible human health risk should be performed.     

Inhibition of dinitropyrene mutagenicity in vitro and in vivo using Salmonella typhimurium and the intrasanguinous host-mediated assay

Dinitropyrenes (DNP), present in polluted air, are potent direct-acting mutagens in Salmonella typhimurium TA98. This mutagenicity is markedly reduced in the presence of rat-liver S9 or microsomes. This has now been confirmed using mouse hepatic fractions. Since most in vitro test systems do not adequately simulate conditions encountered in the intact animal, we have investigated dinitropyrene mutagenicity to Salmonella in the host-mediated assay. 1,8-Dinitropyrene (1,8-DNP) given p.o. to BALB/c mice induced a weak mutagenic effect in S. typhimurium TA98 recovered from the liver 1 h after i.v. administration (optimum time). Over the entire dose range tested no toxicity to bacterial cells was detected. Mutation induction in vivo was dose-related with maximum response at 1 mg DNP/kg body weight. This optimum dose, however, was non-mutagenic to strains TA98/1,8-DNP6 (O-transacetylase-deficient) or TA98NR/1,8-DNP6 (nitroreductase- and O-transacetylase-deficient). 1,3-Dinitropyrene and 1,6-dinitropyrene were weakly mutagenic to TA98 at doses similar to 1,8-DNP. Studies with [14C]1,8-DNP showed that 1 h after oral dosing (1 mg/kg), over 100 ng of 1,8-DNP equivalents were present in the liver (= 0.73% dose). However, only about 5.5 ng were present in the bacterial pellet, suggesting that hepatic components in vivo, as in vitro, bind to DNP, thus interfering with its interaction with Salmonella.     

Airplane emissions: a source of mutagenic nitrated polycyclic aromatic hydrocarbons

Organic solvent extracts from airplane emission particulates are mutagenic for Salmonella typhimurium strain TA98. Using Salmonella tester strains deficient in enzymes required for the bioactivation of various nitroarenes, the mutagenicity present in these emissions was ascribed to the presence of nitrated polycyclic aromatic hydrocarbons. Based on the known aircraft particulate emission rates at U.S. airports, and using 1-nitropyrene (1-NP) and 1,8-dinitropyrene (1,8-DNP) as surrogates, it is calculated that at a minimum 7 kg 1-NP and 20 g, 1,8-DNP are emitted daily at a typical U.S. airport.     

Mutagenicity of surface soil from residential areas in Kyoto city, Japan, and identification of major mutagens

To clarify the mutagenic potential of surface soil in residential areas in Kyoto city, surface soil samples were collected twice or three times from 12 sites, and their organic extracts were examined by the Ames/Salmonella assay. Almost all (>92%) samples showed mutagenicity in TA98 without and with S9 mix, and 8/25 (32%) samples showed high (1000-10,000 revertants/g of soil) or extreme (>10,000 revertants/g of soil) activity. Moreover, to identify the major mutagens in surface soil in Kyoto, a soil sample was collected at a site where soil contamination with mutagens was severe and continual. The soil extract, which showed potent mutagenicity in TA98 without S9 mix, was fractionated by diverse column chromatography methods. Five major mutagenic constituents were isolated and identified to be 1,6-dinitropyrene (DNP), 1,8-DNP, 1,3,6-trinitropyrene (TNP), 3,9-dinitrofluoranthene (DNF), and 3,6-dinitrobenzo[e]pyrene (DNBeP) by co-chromatography using high performance liquid chromatography and spectral analysis. Contribution ratios of 1,6-DNP, 1,8-DNP, 1,3,6-TNP, 3,9-DNF, and 3,6-DNBeP to total mutagenicity of the soil extract in TA98 without S9 mix were 3, 10, 10, 10, and 6%, respectively. These nitroarenes were detected in surface soil samples collected from four different residential sites in other prefectures, and their contribution ratios to soil mutagenicity were from 0.7 to 22%. These results suggest that surface soil in residential areas in Kyoto was widely contaminated with mutagens and there were some sites where surface soils were heavily polluted. 1,6-DNP, 1,8-DNP, 1,3,6-TNP, 3,9-DNF, and 3,6-DNBeP may be major mutagenic constituents that contaminate surface soil in Kyoto and other residential areas.     

New O-acetyltransferase-deficient Ames Salmonella strains generated by specific gene disruption

CoASAc-dependent N-hydroxyarylamine O-acetyltransferase (OAT) is an enzyme involved in the intracellular metabolic activation of N-hydroxyarylamines derived from mutagenic nitroarenes and aromatic amines. The oat gene encoding the enzyme of S. typhimurium TA98 and TA100 was specifically disrupted and the sensitivities of the resulting strains, i.e., YG7130 and YG7126, to mutagens were compared with those of the conventional oat-deficient strains, i.e., TA98/1,8DNP6 and TA100/1,8DNP, respectively. The new oat-deficient strains and the conventional strains exhibited similar sensitivity against most of the chemicals tested: both strains YG7130 and strain TA98/1,8-DNP6 were resistant to mutagenicity by 1,8-dinitropyrene (1, 8-DNP), 1-nitropyrene, 2-amino-6-methyldipyrido[1,2-alpha:3', 2'-d]imidazole (Glu-P-1) and 2-amino-3-methyl-3H-imidazo[4, 5-f]quinoline (IQ); neither strain YG7130 nor strain TA98/1,8-DNP6 was resistant to the mutagenicity of 3-amino-1-methyl-5H-pyrido[4, 3-b]indole (Trp-P-2); strain YG7126 and strain TA100/1,8-DNP were refractory to the mutagenicity of 1,8-DNP. However, the order of the sensitivity against 2-nitrofluorene (2-NF) was TA98>YG7130>TA98/1, 8-DNP6 and TA100>YG7126>TA100/1,8-DNP. Since the strains YG7130 and YG7126 have chloramphenicol resistance (Cmr) gene in place of the chromosomal oat gene for gene disruption, the possible involvement of chloramphenicol acetyltransferase (CAT) encoded by the Cmr gene in the activation of 2-NF was examined. Strikingly, introduction of plasmid pACYC184 carrying the Cmr gene alone substantially enhanced the sensitivity of the conventional oat-deficient strains to 2-NF. These results suggest that the new strains as well as the conventional strains are useful to assess the roles of OAT in the metabolic activation of nitroaromatics and aromatic amines in S. typhimurium, and also that CAT has the ability to activate N-hydroxy aromatic amines to mutagens.     

Modulation of the mutagenicity of three dinitropyrene isomers in vitro by rat-liver S9, cytosolic, and microsomal fractions following chronic ethanol ingestion.

The effects of chronic ethanol feeding of rats on the ability of liver fractions to modulate the bacterial mutagenicity of three dinitropyrene isomers (1,3-, 1,6- and 1,8-DNP), which require bacterial enzymes but not an exogenous enzyme source for activation, were studied. The mutagenicity of the DNP isomers toward S. typhimurium TA98 and TA100 was attenuated in the presence of post-mitochondrial supernatants (S9) from both ethanol-fed and pair-fed rats albeit, that from the ethanol-fed group was more efficient in lowering the mutagenicity. The cytosolic fraction from ethanol-fed rats enhanced the mutagenicity of all of the DNP isomers in TA100. The most notable enhancement was with 1,3-DNP in which a more than 4-fold enhancement was obtained. Cytosol from pair-fed rats enhanced only the mutagenicity of 1,3-DNP, this by 2.9-fold. Cytosolic NADPH-nitroreductase activity from ethanol-treated rats toward 1,6-, 1,8- and 1,3-DNP was increased 2.8-, 1.7- and 1.3-fold, respectively over pair-fed controls. Cytosolic NADH-nitroreductase from ethanol-fed rats was increased with 1,3-DNP (1.7-fold) and 1,8-DNP (1.4-fold) as substrates, but not with 1,6-DNP. Microsomes decreased the mutagenicity of DNP similarly to S9, i.e., fractions from ethanol-fed rats were more efficient than those of pair-fed rats in deactivating all the DNP isomers. Per mg of protein, detoxification of DNP by S9 was more efficient than with microsomes, thus both cytosolic and microsomal enzymes are required for maximal detoxification. In summary, ethanol feeding modulates both the augmented cytosolic activation of DNP to mutagens and the deactivation of the direct-acting mutagenicity of DNP by microsomes. In combination, as is the case with S9, the microsomal detoxifying activity outcompetes the cytosolic activation.     

Mutagenicity of derivatives and metabolites of 1-nitropyrene: activation by rat liver S9 and bacterial enzymes

The mutagenicity and activation requirements of purified synthetic derivatives and potential metabolites of 1-nitropyrene have been characterized in the Ames plate incorporation assay with the Salmonella tester strains TA98, TA98NR and TA98/1,8-DNP6, in the presence or absence of exogenous metabolic activation provided by Aroclor-induced rat liver S9. All the compounds tested (1-aminopyrene, N-acetyl-1-aminopyrene, N-hydroxy-N-acetyl-1-aminopyrene, 3-hydroxy-1-nitropyrene, 6-hydroxy-1-nitropyrene, and 8-hydroxy-1-nitropyrene) exhibited mutagenic activity under one or more assay conditions. 1-Nitropyrene was metabolized to 3-hydroxy-1-nitropyrene, 6- or 8-hydroxy-1-nitropyrene, 1-aminopyrene, N-acetyl-1-aminopyrene and other unidentified products (including some bound to protein) by an S9 preparation analogous to that used for exogenous metabolic activation in the Ames assay. 1-Nitropyrene and 3-hydroxy-1-nitropyrene were activated primarily by the 'classical' nitroreductase, while the other compounds, particularly in the presence of S9 metabolic activation, were dependent on transesterification for expression of their mutagenicity.     

Demonstration of a powerful mutagenic dinitropyrene in airborne particulate matter

Of the many nitroarenes, dinitropyrenes (DNPs) have the potential to revert Salmonella typhimurium his- mutants. This study was conducted to investigate the potential mutagens present in airborne particulate matter collected in Santiago, Chile. 5 organic substances extracted with dichloromethane showed mutagenic rates of from 38.9 to 287 revertants per m3 of air for S. typhimurium his- strain TA98 without S9 mix. 4 of the samples had greatly reduced mutagenicity for strain TA98/1,8DNP6 but not for strain TA98NR. The 1-nitropyrene (1-NP) content accounted for 0.06-0.15 microgram per g of particulate, as determined by high-performance liquid chromatography (HPLC), but the contribution of the compound to mutagenicity was less than 1% of the total activity. On the other hand, by using two columns in the HPLC, DNPs of 1,6- and 1,8-isomers were detected in the samples pooled after the determination of 1-NP, and the amount of the derivatives was about 0.2 microgram per g of particulate matter.     

Bioactivation of diesel exhaust particle extracts and their major nitrated polycyclic aromatic hydrocarbon components, 1-nitropyrene and dinitropyrenes, by human cytochromes P450 1A1, 1A2, and 1B1

The genotoxicities of four samples of diesel exhaust particle (DEP) extracts (DEPE) and nine nitroarenes found in DEPE were investigated after activation catalyzed by human cytochrome P450 (P450) family 1 enzymes co-expressed with NADPH-cytochrome P450 reductase (NPR) in Escherichia coli membranes. The DEPE samples induced umu gene expression in Salmonella typhimurium TA1535/pSK1002 without any P450 system and were further activated by human P450 1B1/NPR membranes. Moderate activation of the DEPE sample by P450 1A2/NPR membranes was also observed, but not by either P450 1A1/NPR or NPR membranes. 1-Nitropyrene (1-NP) was strongly activated by human P450 1B1/NPR membranes. 1,8-Dinitropyrene (1,8-DNP) was most highly activated by P450 1A1 and 1B1 systems for the three DNPs tested. In contrast, 1,3-DNP was inactivated by P450 1A1/NPR, 1A2/NPR, and 1B1/NPR systems and slightly activated by NPR membranes. 2-Nitrofluoranthene (2-NF) and 3-nitrofluoranthene (3-NF) showed activities similar to 1-NP after bioactivation by P450 1B1/NPR membranes. However, the genotoxicities of 6-nitrochrysene, 7-nitrobenz[a]anthracene, and 6-nitrobenzo[a]pyrene were all weak in the present assay system. Apparent genotoxic activities of DEPE were very low compared with standard nitroarenes in the presence of P450s, possibly because unknown component(s) of DEPE had inhibitory effects on the bioactivation of 1-NP and 1,8-DNP catalyzed by human P450 1B1. These results suggest that environmental chemicals existing in airborne DEP, in addition to 1-NP, 1,6-DNP, 1,8-DNP, 2-NF, and 3-NF, can be activated by human P450 1B1. Biological actions of air pollutants such as nitroarenes to human extrahepatic tissues may be of concern in tissues in which P450 1B1 is expressed.     

Comparative direct-acting mutagenicity of 1- and 2-nitropyrene: Evidence for 2-nitropyrene mutagenesis by both guanine and adenine adducts

The mutations and DNA adducts produced by the environmental pollutant 2-nitropyrene were examined in Salmonella typhimurium tester strains. 2-Nitropyrene was a stronger mutagen than its extensively studied structural isomer 1-nitropyrene in strains TA96, TA97, TA98, TA100, TA102, TA104 and TA1538. Both 1- and 2-nitropyrene were essentially inactive in TA1535. The mutagenicity of 1- and 2-nitropyrene in TA98 was much higher than in TA98NR and the activity of these compounds in TA100 was much higher than in TA100NR. While 1-nitropyrene exhibited similar mutagenicity in strains TA98 and TA98/1,8-DNP₆, the mutagenicity of 2-nitropyrene in TA98/1,8-DNP₆ was much lower than in TA98. Analysis of DNA from TA96 and TA104 incubated with 2-nitropyrene indicated the presence of two adducts, N-(deoxyguanosin-8-yl)-2-aminopyrene and N-deoxyadenosin-8-yl)-2-aminopyrene. The results suggest that 2-nitropyrene is metabolized by bacterial nitroreductase(s) to N-hydroxy-2-aminopyrene, and possibly by activation to a highly mutagenic O-acetoxy ester. DNA adduct formation with deoxyguanosine and deoxyadenosine correlates with the mutagenicity of 2-nitropyrene in tester strains possessing both G:C and A:T mutational targets.     

Metabolic activation of 1-nitropyrene and 1,6-dinitropyrene by nitroreductases from Bacteroides fragilis and distribution of nitroreductase activity in rats

Nitrated polycyclic aromatic compounds, 1-nitropyrene (1-NP) and 1,6-dinitropyrene (1,6-diNP), are environmental mutagens and carcinogens. Nitroreductases purified from an anaerobic bacterium, Bacteroides fragilis, catalyzed the metabolic activation of these compounds to produce DNA- and tRNA-bound adducts in vitro. Formation of the adducts was inhibited by p-chloromercuribenzoic acid, which is an inhibitor of nitroreductases from B. fragilis. The enzyme and coenzyme (NADPH) were essential for the adduct formation. These results suggest that nitroreduction is a necessary step in the metabolic activation of nitropyrenes. 1-NP bound specifically to poly(G) and poly(dG), and 1,6-diNP bound to poly(G), poly(dG), and poly(X). The other purine polynucleotides were weak acceptors. However, the reactive products of nitropyrenes formed by nitroreductases could not bind to pyrimidine polynucleotides. Enzymatic hydrolysis of 1-NP-bound DNA and subsequent analysis by high-performance liquid chromatography showed one major and two minor adducts in the hydrolysate. The peak of the major adduct corresponded to that of N-(deoxyguanosin-8-y1)-1-aminopyrene, which is the same as an adduct formed by xanthine oxidase, a mammalian nitroreductase. Nitroreductase activity in the various organs and intestinal contents of Sprague-Dawley rats was assayed in the presence of NADPH or NADH under nitrogen gas. Nitroreductase activity was widely distributed in the organs of the rats; in particular, that of the liver and of the small intestine was relatively high, but that of the respiratory organs such as lung and alveolar macrophages was very low. Intestinal contents had high nitroreductase activity, which was proportional to the number of bacteria, especially anaerobic bacteria, in the intestine. These results suggest that the nitroreductase activity of the normal bacterial flora is very high in rats and that the intestinal bacteria play a major role in the metabolism of nitropyrenes in vivo.     

Aerobic and anaerobic reduction of nitrated pyrenes in vitro

Nitrated pyrenes are mutagenic and tumorigenic environmental pollutants that are activated to DNA-binding derivatives via nitroreduction. We have investigated the enzymatic nitroreduction of 1-nitropyrene, 1,3-, 1,6- and 1,8-dinitropyrene to determine if differences in the extent of nitroreduction may help explain differences in their biological potencies. Each nitrated pyrene was incubated aerobically and anaerobically with 105,000 X g supernatant (S105) from Salmonella typhimurium TA98 and the nitroreductase-deficient strain, TA98NR, and with cytosol and microsomes from rat and human liver. Under anaerobic conditions, 1-nitropyrene and 1,3-dinitropyrene were reduced by TA98 S105 to a lesser extent than 1,6- and 1,8-dinitropyrene. The extent of 1,6- and 1,8-dinitropyrene metabolism was not altered relative to TA98 when using TA98NR S105, but the nitroreduction of 1-nitropyrene and 1,3-dinitropyrene was decreased. Both rat and human liver cytosol and microsomes reduced 1,6- and 1,8-dinitropyrene to greater extents than 1-nitropyrene and 1,3-dinitropyrene. Under aerobic conditions rat and human liver cytosols were similar to TA98 S105 in that aminopyrene decreased while nitrosopyrene formation increased. By comparison, oxygen decreased the microsomal formation of both nitrosopyrenes and aminopyrenes. The reduction of succinoylated cytochrome c was measured during the hepatic metabolism of nitro- and nitrosopyrenes under aerobic conditions. The data indicated that reduced nitro- and nitrosopyrene intermediates were directly reducing succinoylated cytochrome c and that the assay could be used as a measure of aerobic nitroreduction. These studies demonstrate that 1,6- and 1,8-dinitropyrene are reduced to a greater extent than 1-nitropyrene and 1,3-dinitropyrene, which corresponds to their relative biological potencies as mutagens and carcinogens. Furthermore, although more extensive nitroreduction is detected under anaerobic conditions, the nitroreduction that occurs aerobically may be important for the mutagenic and tumorigenic properties of these compounds.