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 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.     

Metabolic activation of 2,4-dinitrobiphenyl derivatives for their mutagenicity in Salmonella typhimurium TA98

In order to elucidate the mechanisms of mutagenic activation of nitroarenes, we tested the mutagenic potency of 18 kinds of nitroarenes including nitrated biphenyl, fluorene, phenanthrene and pyrene on Salmonella typhimurium TA98 in the absence and presence of S9 mix. The mutagenicities of 2,4-dinitrobiphenyl derivatives and 4-nitrobiphenyl were enhanced by the addition of S9. 2,4,6-Trinitrobiphenyl (3 net rev./10 micrograms without S9) was activated 60-fold by the mammalian metabolic system (181 net rev./10 micrograms with 10% S9). The mutagenic potency of 2,4,2',4'-tetranitrobiphenyl in TA98, TA98NR and TA98/1,8-DNP6 was also enhanced by the addition of 10% S9. But 1-nitropyrene and 1,3-dinitropyrene, which are well-known mutagens and carcinogens, were deactivated to 3% and 0.4%, respectively, by the addition of 10% S9. Separate addition of microsomal and cytosolic fractions slightly activated the mutagenicity of 2,4,6-trinitrobiphenyl, and 2,4,2',4'-tetranitrobiphenyl was activated not only by S9 but also by the cytosolic fraction.     

Mutagenicity of K-region derivatives of 1-nitropyrene; remarkable activity of 1- and 3-nitro-5H-phenanthro[4,5-bcd]pyran-5-one

The mutagenic activities toward S. typhimurium strains TA98 and TA100 of K-region derivatives of 1-nitropyrene and pyrene were determined. The compounds tested were trans-4,5-dihydro-4,5-dihydroxy-1-nitropyrene (Compound 3), trans-4,5-dihydro-4,5-dihydroxypyrene (Compound 4), 1-nitropyrene-4,5-quinone (Compound 5), 1-nitropyrene-9,10-quinone (Compound 6), pyrene-4,5-quinone (Compound 7), and the lactones, 1-nitro-5H-phenanthro[4,5-bcd]pyran-5-one (Compound 8), 3-nitro-5H-phenanthro[4,5-bcd]pyran-5-one (Compound 9), and 5H-phenanthro[4,5-bcd]pyran-5-one (Compound 10). Neither pyrene nor any of its K-region derivatives was mutagenic, either in the absence or presence of S9 mix at the doses tested. Of the K-region derivatives of 1-nitropyrene, the lactones (Compounds 8 and 9) were generally the most active; 0.25 microgram/plate induced 900-2200 revertants in TA98 or TA100 without activation. The 4,5-dihydrodiol (Compound 3), an established mammalian metabolite of 1-nitropyrene, was less mutagenic than was 1-nitropyrene in TA98, but was more mutagenic than was 1-nitropyrene in TA100, regardless of the presence of S9 mix. The quinones (Compounds 5 and 6) were less mutagenic than was 1-nitropyrene in the absence of S9 mix in both strains, but their activities were increased in the presence of S9 mix. The mutagenic activities of the lactones (Compounds 8 and 9) were lower in strains TA98NR and TA98/1,8-DNP6 than in TA98, indicating that nitro-reduction and esterification are involved in their activation. The results of this study indicate that K-region derivatives of 1-nitropyrene may be important in its metabolic activation.     

Conversion of polycyclic aromatic hydrocarbons by <Emphasis Type="Italic">Sphingomonas</Emphasis> sp. VKM B-2434

A versatile bacterial strain able to convert polycyclic aromatic hydrocarbons (PAHs) was isolated, and a conversion by the isolate of both individual substances and PAH mixtures was investigated. The strain belonged to the Sphingomonas genus as determined on the basis of 16S rRNA analysis and was designated as VKM B-2434. The strain used naphthalene, acenaphthene, phenanthrene, anthracene and fluoranthene as a sole source of carbon and energy, and cometabolically oxidized fluorene, pyrene, benz[a]anthracene, chrysene and benzo[a]pyrene. Acenaphthene and fluoranthene were degraded by the strain via naphthalene-1,8-dicarboxylic acid and 3-hydroxyphthalic acid. Conversion of most other PAHs was confined to the cleavage of only one aromatic ring. The major oxidation products of naphthalene, phenanthrene, anthracene, chrysene, and benzo[a]pyrene were identified as salicylic acid, 1-hydroxy-2-naphthoic acid, 3-hydroxy-2-naphthoic acid, o-hydroxyphenanthroic acid and o-hydroxypyrenoic acid, respectively. Fluorene and pyrene were oxidized mainly to hydroxyfluorenone and dihydroxydihydropyrene, respectively. Oxidation of phenanthrene and anthracene to the corresponding hydroxynaphthoic acids occurred quantitatively. The strain converted phenanthrene, anthracene, fluoranthene and carbazole of coal-tar-pitch extract.     

Mutagenicity of the phenolic microsomal metabolites of 3-nitrofluoranthene and 1-nitropyrene in strains of Salmonella typhimurium

The environmental pollutant 3-nitrofluoranthene is metabolized in vitro and in vivo to several products including the phenolic metabolites 3-nitrofluoranthen-6-ol (3NF-6-ol), 3-nitrofluoranthen-8-ol (3NF-8-ol), and 3-nitrofluoranthen-9-ol (3NF-9-ol). Similarly, 1-nitropyrene is metabolized to the phenolic metabolites 1-nitropyren-3-ol (1NP-3-ol), 1-nitropyren-6-ol (1NP-6-ol), and 1-nitropyren-8-ol (1NP-8-ol). The mutagenicity of these compounds was investigated using strains of Salmonella typhimurium deficient in either certain nitroreductase or the aryl hydroxylamine O-esterificase. In TA98, 3-nitrofluoranthene and 3NF-8-ol were equally mutagenic at approximately 10³ revertants/nmole while 3NF-6-ol and 3NF-9-ol were 10-fold less mutagenic. 1-Nitropyrene and 1NP-3-ol likewise were equally mutagenic at approximately 700 revertants/nmole and 1NP-6-ol and 1NP-8-ol were 100-fold less mutagenic. The mutagenicity of 1-nitropyrene was dependent on the ‘classical nitroreductase’ which is absent in TA98NR, and that of 3-nitrofluoranthene, 3NF-8-ol, and 1NP-3-ol was less dependent on this nitroreductase. Using TA98/1,8DNP₆, it was determined that the mutagenicity of 3-nitrofluoranthene, 3NF-8-ol, and 1NP-3-ol but not 1-nitropyrene was dependent on the presence of the O-esterificase. 3-Nitrofluoranthene and 3NF-8-ol were mutagenic in TA100, while 3NF-6-ol and 3NF-9-ol were considerably less mutagenic. 3-Nitrofluoranthene was not mutagenic in TA100NR nor in TA100-Tn5-1,8-DNP1012. None of the phenolic metabolites of 3-nitrofluoranthene were mutagenic in TA100-Tn5-1,8DNP1012 indicating a strong dependence for mutagenicity of the O-esterificase of the 1,8-dinitropyrene nitroreductase which is absent in this strain. These results are discussed in view of possible mechanisms for the differences in the mutagenicity of the phenolic metabolites of these two nitrated arenes.     

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.     

Reduction and mutagenic activation of nitroaromatic compounds by a Mycobacterium sp.

Mycobacterium sp. strain Pyr-1 cells, which were grown to the stationary phase in media with and without pyrene, were centrifuged and resuspended in a medium containing 1-nitropyrene. Cells that had been grown with pyrene oxidized up to 20% of the added 1-nitropyrene to 1-nitropyrene-cis-9,10- and 4,5-dihydrodiols. However, cells that had been grown without pyrene reduced up to 70% of the 1-nitropyrene to 1-aminopyrene but did not produce dihydrodiols. The nitroreductase activity was oxygen insensitive, intracellular, and inducible by nitro compounds. Nitroreductase activity was inhibited by p-chlorobenzoic acid, o-iodosobenzoic acid, menadione, dicumarol, and antimycin A. Extracts from cells that had been grown without pyrene activated 1-nitropyrene, 1-amino-7-nitrofluorene, 2,7-dinitro-9-fluorenone, 1,3-dinitropyrene, 1,6-dinitropyrene, and 6-nitrochrysene to DNA-damaging products, as shown in Salmonella typhimurium tester strains by the reversion assay and by induction of the umuC gene. Activation of nitro compounds, as shown by the umu test, was enhanced by NADPH. This study shows that Mycobacterium sp. strain Pyr-1 metabolizes nitroaromatic compounds by both oxidative and reductive pathways. During reduction, it generates products that are mutagenic.     

Structural activity relationship between Salmonella-mutagenicity and nitro-orientation of nitroazaphenanthrenes

Nitroazaphenanthrenes (NAphs) and their N-oxides (NAphOs) were synthesized as derivatives with nitrogen atoms in the 1, 4, and 9 positions of phenanthrene rings, and as nitrated derivatives substituted at the 1, 2, 3, 4, 5, 6, 7, and 8 positions of phenanthrene rings. To determine the structure activity relationship of these derivatives, all 19 isomers were bioassayed with Salmonella tester strains. NAphs substituted at the 4, 6, 7 and 8 positions were mutagenic for TA98, and 1-, 2-, and 3-N-9-AphOs, 6-N-1-AphO and 6-N-4-AphO were mutagenic for TA98 and TA100 without the S9 mix, while 5-N-1-AphO and 5-N-9-AphO were non- or weakly mutagenic. Nitrated derivatives, 6-N-4-Aph, 6-N-9-Aph, 6-N-1-AphO, and 6-N-4-AphO, were powerful mutagens for TA98 and TA100. Mutagenicity was enhanced by mutant strains producing nitroreductase, such as YG1021 and 1026, and by those producing O-acetyltransferase, such as YG1024 and 1029. Nitro derivatives substituted at positions 4 and 5 in the phenanthrene rings were perpendicular, while those at positions 2, 3, 6 and 7 were coplanar to the phenanthrene rings. NAphs substituted at the 1 and 8 positions were noncoplanar due to steric hindrance of the aromatic proton at the peri position. On the other hand, 1,5- and 1,8-dinitro-4-azaphenanthrenes showed high mutagenicity for strains TA98 and TA100 in the absence of the S9 mix, and were strongly enhanced by nitroreductase and O-acetyltransferase, over-producing mutants. Therefore, it was found that the mutagenic potency of NAphs and NAphOs was closely associated with the chemical properties and orientation of nitro substitution of aromatic rings.     

Relationships between structure of nitrated arenes and their mutagenicity in Salmonella typhimurium; 2- and 2,7-nitro substituted fluorene, phenanthrene and pyrene

In order to elucidate the mechanisms of mutagenic activation of nitroarenes, we studied the relationships between the mutagenic potency and chemical structure of 2-nitro- and 2,7-dinitro-arenes including nitrated fluorene (Fl), dihydrophenanthrene (DHPh), phenanthrene (Ph), tetrahydropyrene (THPy), dihydropyrene (DHPy) and pyrene (Py) together with 9-NO2-Ph, 1-NO2-Py and 1.3-diNO2-Py. The mutagenicity tests were carried out on Salmonella typhimurium TA98, TA98NR and TA98/1,8-DNP6 in the absence of S9 mix. The order of mutability of mononitro- and dinitro-arenes in TA98 is as given below: 2-NO2-THPy less than 2-NO2-Fl less than 2-NO2-DHPh less than 9-NO2-Ph less than 2-NO2-Ph less than 2-NO2-DHPy less than 1-NO2-Py less than 2-NO2-Py, and 2,7-diNO2-DHPh less than 2,7-diNO2-Fl less than 2,7-diNO2-THPy less than 2,7-diNO2-Ph less than 2,7-diNO2-DHPy less than 2,7-diNO2-Py less than 1,3-diNO2-Py. 9-NO2-Ph and 1-NO2-Py, which have been detected in environmental samples, are not as potent mutagens as 2-nitrated phenanthrene and pyrene, respectively. 2-NO2THPy (37.7 rev/nmole) was a weak mutagen, but 2,7-diNO2-THPy (3197 rev/nmole) was as potent a mutagen as 2,7-diNO2 (3925 rev/nmole). Tetrahydropyrene has a twisted form in its structure. 1,3-diNO2-Py (99660 rev/nmole) was more mutagenic than 2,7-diNO2-Py (37960.0 rev/nmole), and their mutagenicities were correlated with the behavior of the K-band in their UV spectra by the introduction of nitro groups on pyrene.     

Photochemical instability of 1-nitropyrene, 3-nitrofluoranthene, 1,8-dinitropyrene and their parent polycyclic aromatic hydrocarbons

The environmental contaminants pyrene, 1-nitropyrene, 1,8-dinitropyrene, fluoranthene, and 3-nitrofluoranthene were exposed to light (greater than or equal to 310 nm) either in DMSO, or following coating onto silica. Under all conditions tested the pyrenyl were less stable than the fluoranthenyl compounds. During irradiation in DMSO or on silica, 1-nitropyrene had half-lives of 1.2 and 6 days, while those of 3-nitrofluoranthene were 12.5 and greater than 20 days, respectively. The photodecomposition of 1,8-dinitropyrene resembled that of 1-nitropyrene with half-lives of 0.7 and 5.7 days. A principle photodecomposition product of 1,8-dinitropyrene was identified as 1-nitropyren-8-ol. It was also found that when the nitroarenes were exposed to light, the loss of compound was associated with a concomitant loss of mutagenicity in Salmonella typhimurium strain TA98. The mechanism of nitrated polycyclic aromatic hydrocarbon decomposition and 1-nitropyren-8-ol formation, and the relevance to the atmospheric disposition of these compounds are discussed.     

Mutagenic activities of selected nitrofluoranthene derivatives in Salmonella typhimurium strains TA98, TA98NR and TA98/1,8-DNP6

The mutagenic activities of novel nitrofluoranthene derivatives in Salmonella strains TA98, TA98NR and TA98/1,8-DNP6 (with and without S9 addition) are given. These derivatives were produced from the reactions of fluoranthene (FL) and its directly mutagenic 2- and 3-nitro derivatives with covalent dinitrogen pentoxide (N2O5) in CCl4 solution at ambient temperature. The influence of the addition of a nitro group on the observed activity of the resulting di- and tri-nitrofluoranthenes is discussed.     

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.     

1-Nitrosopyrene: an intermediate in the metabolic activation of 1-nitropyrene to a mutagen in Salmonella typhimurium TA1538

Incubation of Salmonella typhimurium TA1538, in suspension culture, with 1.5 or 23 microM 1-nitropyrene resulted in a time-dependent increase in reversions for up to 7 h. In contrast, when the bacteria were exposed to 1.5 microM 1-nitrosopyrene, a reduction product of 1-nitropyrene, maximum reversion induction occurred after 1 h and a much higher mutation frequency was detected. Examination of DNA isolated from Salmonella typhimurium incubated with 4.1 microM [4,5,9,10-3H]1-nitrosopyrene indicated the presence of one major adduct, N-(deoxyguanosin-8-yl)-1-aminopyrene, the same adduct observed previously when the bacteria were exposed to 1-nitropyrene. When calf thymus DNA was treated with 1-nitrosopyrene in the presence of ascorbic acid, 1-aminopyrene was formed concomitant with the production of N-(deoxyguanosin-8-yl)-1-aminopyrene. In the absence of ascorbic acid, a 20-fold reduction in DNA binding was observed and 1-aminopyrene was not detected. The observations that 1-nitrosopyrene forms the same DNA adduct and is more mutagenic than 1-nitropyrene, suggest that 1-nitrosopyrene is an intermediate in the mutagenic activation of 1-nitropyrene in Salmonella typhimurium TA1538. Since reduction of 1-nitrosopyrene was necessary to get appreciable DNA binding in vitro, further reduction of 1-nitrosopyrene to N-hydroxy-1-aminopyrene is probably required in the activation pathway.     

Mutagenicity of phenanthrene and phenanthrene K-region derivatives.

Phenanthrene and 9 K-region derivatives, most of them potential metabolites of phenanthrene, were tested for mutagenicity by the reversion of histidine-dependent Salmonella typhimurium TA1535, TA1537, TA1538, TA98 and TA100 and the rec assay with Bacillus subtilis H17 and M45. The strongest mutagenic effects in the reversion assay were observed with phenanthrene 9,10-oxide, 9-hydroxyphenanthrene and N-benzyl-phenanthrene-9,10-imine. Interestingly, the mutagenic potency of the arene imine was similar to that of the corresponding arene oxide. This is the first report on the mutagenicity of arene imine. The mutagenic effects of all these phenanthrene derivatives were much weaker than that of the positive control benzo[a]pyrene 4,5-oxide. Even weaker mutagenicty was found with cis-9,10-dihydroxy-9,10-dihydrophenanthrene and with trans-9,10-dihydroxy-9-10-dihydrophenanthrene. The other derivatives were inactive in this test. However, 9-10-dihydroxyphenanthrene and 9,10-phenanthrenequinone were more toxic to the rec- B. subtilis M45 strain than to the rec+ H17 strain. This was also true for phenanthrene 9,10-oxide and 9-hydroxyphenanthrene, but not with the other test compounds that reverted (9,10-dihydroxy-9,10-dihydrophenanthrenes; N-benzyl-phenanthrene 9,10-imine; benzo[a]pyrene 4,5-oxide) or did not revert (phenanthrene, 9,10-bis-(p-chlorophenyl)-phenanthrene 9,10-oxide, 9-10-diacetoxyphenanthrene) the Salmonella tester strains. Although the K region is a main site of metabolism and although all potential K-region metabolites were mutagenic, phenanthrene did not show a mutagenic effect in the presence of mouse-liver microsomes and an NADPH-generating system under standard conditions. However, uhen epoxide hydratase was inhibited, phenanthrene was activated to a mutagen that reverted his- S. typhimurium. This shows that demonstration of the mutagenic activity of metabolites together with the knowledge that a major metabolic route proceeds via these metabolites dose not automatically imply a mutagenic hazard of the mother compound, because the metabolites in question may not accumulate in sufficient quantities and therefore the presence and relative activities of enzymes that control the mutagenically active metabolites are crucial. N-Benzyl-phenanthrene 9.10-imine was mutagenic for the episome-containing S. typhimurium TA98 and TA100 but not for the precursor strains TA1538 and TA1535. This arene imine would therefore be useful as a positive control during routine testing to monitor in the former strains the presence of the episome which is rather easily lost.     

Degradation of phenanthrene, fluorene, fluoranthene, and pyrene by a Mycobacterium sp.

Mycobacterium sp. strain BB1 was isolated from a former coal gasification site. It was able to utilize phenanthrene, pyrene, and fluoranthene as sole sources of carbon and energy and to degrade fluorene cometabolically. Exponential growth with solid phenanthrene, pyrene, and fluoranthene was obtained in fermentor cultures. The growth rates were 0.069, 0.056, and 0.040 h-1, respectively. Several metabolites of phenanthrene and fluorene metabolism were identified.     

Activation of two environmental mixtures by plant S9

Nitrated and ozonized pyrene mixtures were assayed for their mutagenic activity in the presence or absence of pea S9 using Salmonella typhimurium TA98 as the indicator organism. The plant enzymes increased the mutagenic response of these mixtures above that obtained in the absence of S9. The optimum S9 protein concentration for the activation of the nitrated pyrene mixture at 0.1 microgram was 3.9 mg/plate whereas that for the ozonized pyrene mixture at 33.3 micrograms was 3.2 mg protein/plate. BSA could not replace S9, and NADPH was a required co-factor in the activation of both mixtures by pea S9. Although the nitrated pyrene mixture was determined to consist of approximately 90% 1-nitropyrene, the mutagenic response due to this compound ranged from 30 to 50% of that of the mixture.     

Some chloro derivatives of polynuclear aromatic hydrocarbons are potent mutagens in Salmonella typhimurium

A series of chlorinations of some polynuclear aromatic hydrocarbons (PAH) were carried out and the products were tested for mutagenicity on Salmonella typhimurium TA98 and TA100. We conclude that the chlorination of certain PAHs with low mutagenicity, such as pyrene and benzo[e]pyrene, resulted in the formation of two types of product. The chlorination of pyrene was studied in some detail. The major products of this chlorination were chloro-substituted pyrenes. These compounds showed an S9-dependent mutagenicity and were identified as 1-chloro-, 1,6-dichloro-, 1,8-dichloro- and 1,3-dichloropyrene. On tester strain TA100 the mutagenic effect ranged from 1.4 to 14 revertants/nmol, 1,3-dichloropyrene being the most potent of the isomers. Minor products eluting from a chromatograph in a more polar fraction than the major products were also formed. These compounds were less stable than the major products and were identified as pyrene with chloro additions in the 4- and 5-positions, with various chloro substituents at other positions. These minor products showed a high mutagenic effect on Salmonella in the absence of S9. The mutagenic effect on strain TA100 ranged from 10 to 15 revertants per ng which is at least 40 and 4000 times higher than for 1-nitropyrene and pyrenequinones, respectively. These unstable chloro derivatives of pyrene are difficult to analyse chemically because they are easily degraded and give rise to the more stable 4-chloropyrene.     

Nitroarenes in Suimon River sediment

Mutagenic activity was observed in sediments of the Suimon River bed with and without S9 mix. The direct-acting mutagens in the sediment were investigated. The sediment was extracted with methanol and fractionated on a Silica gel column. The benzene fraction from the Silica gel column exhibited mutagenic activity without S9 mix in strain TA98, while it failed to show mutagenic activity in nitroreductase-deficient strain TA98NR. This observation led to the suspicion that nitro compounds were the direct-acting mutagens of these samples. The benzene fraction was treated by heptafluorobutyric anhydride (HFBA) and investigated with gas chromatography equipped with an electron capture detector (GC-ECD). 2-Nitrofluorene, 4,4'-dinitrobiphenyl, 2,7-dinitrofluorene and 1-nitropyrene were detected and measured quantitatively. The mutagenic activity of a mixture of these compounds was compared with that of the original fraction and the direct-acting mutagenicity of Suimon River sediment can be explained by these nitroarenes, especially 1-nitropyrene.     

A sensitive umu test system for the detection of mutagenic nitroarenes in Salmonella typhimurium NM1011 having a high nitroreductase activity.

A sensitive umu test system for the detection of mutagenic nitroarenes has been developed using a new tester strain Salmonella typhimurium NM1011 having a high nitroreductase activity. The new strain was constructed by subcloning the bacterial nitroreductase gene into a plasmid pACYC184 and introducing the plasmid into the original strain S. typhimurium TA1535/pSK1002 harboring a fusion gene umuC'-'lacZ (pSK1002). Thus, the tester strain enabled us to monitor the genotoxic activities of various nitroarene compounds by measuring the beta-galactosidase activity in the cells. The sensitivity of strain NM1011 was compared with that of the parent tester strain S. typhimurium TA1535/pSK1002 or a nitroreductase-deficient strain S. typhimurium NM1000 with respect to the induction of umuC gene expression by 17 mutagenic nitroarenes. The newly developed strain with high nitroreductase activity had about 3 times higher nitrofurazone-reductase activity than the parent strain and was highly sensitive to the compounds 2-nitrofluorene, 1-nitronaphthalene, 2-nitronaphthalene, 1-nitropyrene, m-dinitrobenzene, 4,4'-dinitrobiphenyl, 3-nitrofluoranthene, 3,7-dinitrofluoranthene, 3,9-dinitrofluoranthene, 5-nitroacenaphthene and 2,4-dinitrotoluene. By contrast, the enzyme-deficient strain did not show any considerable response to 2-nitrofluorene, m-dinitrobenzene, 1-nitronaphthalene, 2-nitronaphthalene, 1-nitropyrene, 4,4'-dinitrobiphenyl, 3-nitrofluoranthene, 3,7-dinitrofluoranthene, 2,4-dinitrotoluene and 5-nitroacenaphthene. These results suggest that the newly developed tester strain with high nitroreductase activity is very useful for the detection of potent mutagenic nitroarene compounds.