Mutagens formed from beta-carbolines with aromatic amines

Norharman, widely distributed in our environment such as cigarette smoke and cooked foods, is not mutagenic to Salmonella strains, but becomes mutagenic to Salmonella typhimurium TA98 and YG1024 with S9 mix in the presence of aromatic amines, including aniline and o-toluidine. Therefore, we have designated norharman as a "co-mutagen". Since, humans are simultaneously exposed to norharman and aromatic amines in daily life, it is important to clarify the mechanisms of its co-mutagenic action to further understanding of the potential genotoxic effects in humans. Regarding the mechanisms of this action of norharman with aniline, a mutagenic compound, 9-(4'-aminophenyl)-9H-pyrido[3,4-b]indole[aminophenylnorharman (APNH)] is produced by their interaction, and converted to the hydroxyamino derivative which eventually forms the DNA adduct, dG-C8-APNH through possible ultimate reactive forms with esterification, and this induces mutations. Also other aminophenyl-beta-carboline compounds, such as 9-(4'-amino-3'-methylphenyl)-9H-pyrido[3,4-b]indole[amino-3'-methylphenylnorharman (3'-AMPNH)], 9-(4'-amino-2'-methylphenyl)-9H-pyrido[3,4-b]indole [amino-2'-methylphenylnorharman (2'-AMPNH)], 9-(4'-aminophenyl)-1-methyl-9H-pyrido[3,4-b]indole[aminophenylharman (APH)] and 9-(4'-amino-3'-methylphenyl)-1-methyl-9H-pyrido[3,4-b]indole[amino-3'-methylphenylharman (AMPH)], have been found on reaction of norharman or harman with aniline or toluidine isomers. These compounds showed mutagenic and clastogenic actions in bacterial and mammalian cells. Among them, APNH demonstrated the most potent activity, and it was most extensively studied. When APNH was administered as a single dose to F344 rats, severe testicular toxicity was observed after 6 days. Moreover, liver preneoplastic lesions (GST-P-positive foci) in the liver clearly developed in animals fed 10-50 ppm of APNH in the diet for 4 weeks. Since, APNH was detected in 24 h urine of rats upon simultaneous administration with norharman and aniline by gavage, it is likely to be also produced from norharman and aniline in the human body. From these findings, it is suggested that aminophenyl-beta-carboline derivatives may be classified as one of the novel types of endogenous mutagens and carcinogens.     

Induction of sister chromatid exchanges and chromosome aberrations in cultured mammalian cells treated with aminophenylnorharman formed by norharman with aniline

Aminophenylnorharman (APNH) is a newly identified mutagenic heterocyclic amine formed by coupling of norharman with aniline in the presence of S9 mix. Furthermore, mutagenic amino-3'-methylphenylnorharman (AMPNH) and aminophenylharman (APH) have been identified from a reaction mixture of norharman and o-toluidine and that of harman and aniline, respectively, with S9 mix. Among these three heterocyclic amines, APNH shows most potent mutagenic activity towards Salmonella typhimurium TA98 and YG1024 with S9 mix. In the present study, the induction of sister chromatid exchanges (SCEs) by APNH was examined in Chinese hamster lung (CHL) cells in vitro, comparing it to those of AMPNH and APH. On incubation with rat S9 for 6h, followed by a recovery culture period of 18h, a dose-dependent effect was found at concentrations between 0.00125 and 0.01 microg/ml for APNH and between 0.3125 and 5 microg/ml for AMPNH and APH. The approximate chemical concentrations leading to a three-fold of control SCE levels calculated from slopes of the linear regressions of induced SCEs were 0.005 for APNH, 0.51 for AMPNH and 1.7 microg/ml for APH. Because of the very strong SCE-causing ability of APNH, we further explored its genotoxicity by examining the induction of chromosome aberrations in CHL cells. A dose-dependent effect was found for chromosome aberrations at concentrations between 0.00125 and 0.04 microg/ml of APNH. The aberrations observed were primarily chromatid exchanges (cte) and breaks (ctb). In conclusion, the potency of SCE induction and clastogenic activity induced by APNH is stronger than Actinomycin D, Mitomycin C (MMC) or 1,8-dinitropyrene which are considered to be the potent clastogens in the literature. Further studies are needed for elucidating mechanisms of the genotoxic actions of these compounds and for evaluating their potential hazards to human health.     

Identification of co-mutagenic chlorinated harmans in final effluent from a sewage treatment plant

Harman (1-methyl-9H-pyrido[3,4-b]indole) reacted readily with sodium hypochlorite in an aqueous medium to give the mono-chlorinated derivatives, which reportedly have greater co-mutagenic activity than harman in the presence of o-toluidine toward Salmonella typhimurium TA 98 with S9 mix. Mono-chlorinated harmans were detected by concentration using blue rayon (BR) and GC/MS analysis in the final effluent from a sewage treatment plant in Shizuoka, Japan. The amounts adsorbed for 24h were 1-45ng/gBR for mono-chlorinated harman and 110-730ng/gBR for harman.     

Mutagenicities of indole and 30 derivatives after nitrite treatment

Indole and 7-derivatives, L- and D-tryptophan and 9 derivatives, and beta-carboline (norharman) and 11 derivatives were tested for mutagenicity to Salmonella typhimurium TA100 and TA98 after nitrite treatment. 1-Methylindole, which is present in cigarette smoke condensate (Grob and Voellmin, 1970; Hoffmann and Rathkamp, 1970), was the most mutagenic to TA100 without S9 mix after nitrite treatment, inducing 615,000 revertants/mg. 2-Methylindole, 1-methyl-DL-tryptophan, harmaline and (-)-(1S,3S)-1,2-dimethyl-1,2,3,4-tetrahydro-beta-carboline-3- carboxylic acid also showed strong mutagenicity after nitrite treatment, inducing 129,000, 184,000, 103,000 and 197,000 revertants/mg, respectively. These mutagenic potencies were comparable with those of benzo[alpha]pyrene, 3-methylcholanthrene and 2-amino-9H-pyrido[2,3-b]indole (A alpha C) (Sugimura, 1982). Of 31 compounds tested, 22 were mutagenic after nitrite treatment. Since various indole compounds are ubiquitous in our environment, especially in plants, the presence of their mutagenicities after nitrite treatment warrants further studies, including those on their in vivo carcinogenicities.     

Mutagenicity of adsorbates to a copper-phthalocyanine derivative recovered from municipal river water

Blue cotton, bearing a covalently bound copper-phthalocyanine derivative capable of adsorbing polycyclic aromatic hydrocarbons (PAHs) over 3 rings, was applied to recover mutagens from the Katsura River which is a tributary of the Yodo River. The Ames Salmonella/microsome assay with TA98 and TA100 of the blue cotton concentrate recovered from the river water demonstrated indirect mutagenicity toward TA98. The subfractions separated by Sephadex G-25 gel chromatography also showed direct mutagenicity in strains YG1021 and YG1024, the nitroreductase- and O-acetyltransferase-overproducing derivatives of TA98; this activity was greatly increased by the addition of S9 mix, especially in YG1024. However, these subfractions were less mutagenic with TA98NR or TA98/1,8-DNP6, regardless of whether S9 mix was present or not. The behaviors of these mutagenic activities therefore suggested that frameshift mutagens of both directly mutagenic nitroarenes and indirectly mutagenic aminoarenes were present in the blue cotton concentrate from the river water.     

Chlorination of harman and norharman with sodium hypochlorite and co-mutagenicity of the chlorinated products

Harman and norharman are widely distributed in the environment and consequently contaminate in domestic waste-water. It has been reported that they have co-mutagenic activity in the presence of non- mutagenic aromatic amines such as aniline and o-toluidine with S9 mix. When these beta-carbolines were treated with sodium hypochiorite under mild conditions, chlorinated derivatives were produced. Among them, 6-chloroharman and 6-chloronorharman showed much more potent co-mutagenic activities than harman and norharman in the presence of o-toluidine toward Salmonella typhimurium TA98 with S9 mix. These results suggest that the chlorination of harman and norharman occurs during disinfection at the sewage plant to produce potent co-mutagens that contaminate river water.     

Mutagenic activity of 2-chloro-4-nitroaniline and 5-chlorosalicylic acid in Salmonella typhimurium: two possible metabolites of niclosamide

Niclosamide is an anti-helminthic drug susceptible to being metabolized into a bacterial mutagen by the action of enzymes present in the S9 activation mixture. Additional results from genotoxic studies in rodents and humans suggest that the drug is absorbed from the gastrointestinal tract, and mutagenic metabolites are excreted both in the free form and as conjugated glucuronides. As in the case of other secondary amides, phase I metabolism of niclosamide may result in a hydrolytic cleavage of the amide bond, giving rise to 5-chlorosalicylic acid and 2-chloro-4-nitroaniline as the main metabolites. In this study, the mutagenicity of these compounds was tested using the Salmonella typhimurium assay. Bacterial mutagenicity tests with these 2 compounds reveal a non-mutagenic response with 5-chlorosalicylic acid and a mutagenic one with 2-chloro-4-nitroaniline. However, the mutagenic potency observed with this compound is lower than that of niclosamide. The role of nitroreduction in the activation of niclosamide and 2-chloro-4-nitroaniline was also investigated with the help of S. typhimurium strains TA98NR, YG1020, YG1021 and YG1024. The results show a pattern of response which is qualitatively similar for both compounds and this indicates that its mutagenicity depends on both nitroreduction and transacetylation.     

Evaluation of nitroreductase and acetyltransferase participation in N-nitrosodiethylamine genotoxicity

N-Nitroso compounds, such as N-nitrosodiethylamine (NDEA), are a versatile group of chemical carcinogens, being suspected to be involved in gastrointestinal tumors in humans. The intestinal microflora can modify a wide range of environmental chemicals either directly or in the course of enterohepatic circulation. Nitroreductases from bacteria seem to have a wide spectrum of substrates, as observed by the reduction of several nitroaromatic compounds, but their capacity to metabolize N-nitroso compounds has not been described. To elucidate the participation of nitroreductase or acetyltransferase enzymes in the mutagenic activity of NDEA, the bacterial (reverse) mutation test was carried out with the strains YG1021 (nitroreductase overexpression), YG1024 (acetyltransferase overexpression), TA98NR (nitroreductase deficient), and TA98DNP6 (acetyltrasferase deficient), and YG1041, which overexpresses both enzymes. The presence of high levels of acetyltransferase may generate toxic compounds that must be eliminated by cellular processes or can lead to cell death, and consequently decrease the mutagenic effect, as can be observed by the comparison of strain TA98DNP6 with the strains TA98 and YG1024. The slope curves for TA98 strain were 0.66 rev/microM (R(2) = 0.51) and 52.8 rev/microM (R(2) = 0.88), in the absence and presence of S9 mix, respectively. For YG1024 strain, the slope curve, in the presence of S9 mix was 6897 rev/microM (R(2) = 0.78). Our data suggest that N-nitroso compounds need to be initially metabolized by enzymes such as cytochromes P450 to induce mutagenicity. Nitroreductase stimulates toxicity, while acetyltransferase stimulates mutagenicity, and nitroreductase can neutralize the mechanism of mutagenicity generating innoccuos compounds, probably by acting on the product generated after NDEA activation.     

Mutagenicity of native cigarette mainstream smoke and its gas/vapour phase by use of different tester strains and cigarettes in a modified Ames assay

The "Bacterial Reverse Mutation Assay" is generally accepted to analyse the genotoxic capacity of single compounds or complex mixtures such as cigarette-smoke condensates. With an adapted and modified Ames assay, the mutagenicity of native cigarette mainstream whole smoke (WS) and its gas/vapour phase (GVP) was studied. The bacteria were directly exposed to the smoke in a CULTEX1 system closely connected to a smoking robot (VC10). A variety of standard tester strains (TA98, TA100, TA1535, TA1537, TA1538, TA102, WP2uvrApKM101) and descendants of TA98 (YG1021, YG1024, YG1041) and TA100 (YG1026, YG1029 and YG1042) were exposed to whole and filtered smoke of the research cigarette K2R4F to find the most sensitive strains for analysing the mutagenic activity of these test atmospheres. Mutagenicity of WS was detected by TA98, TA100 and their YG descendant strains as well as by WP2uvrApKM101 in the presence of S9 mix. The GVP induced a mutagenic signal in TA100, YG1029 and YG1042 and WP2uvrApKM101 only in the absence of S9 mix. To detect mutagenicity in WS the presence of the plasmid pKM101 is required and a frame-shift mutation is more effective than a missense mutation. To detect mutagenicity in GVP, the presence of the plasmid pKM101 and a missense mutation are required. The differentiating capacity of this modified Ames assay was demonstrated by exposing strain TA98 to WS and TA100 to the GVP of cigarettes with different tar content. The mutagenic activity of WS and the GVP increased with rising tar content of the cigarettes with two exceptions in WS. Thus, the concept of tar content alone is misleading and does not reflect the mutagenic activity of a cigarette.     

Evaluation of a battery of Salmonella typhimurium tester strains for biomonitoring of mutagenic polycyclic aromatic hydrocarbons, nitroarenes and aromatic amines

Various combinations of Salmonella typhimurium tester strains and S9 mix for bioactivation (TA98+S9 mix, TA98S; YG1041+S9 mix, YG1041S) and strain YG1041 in the absence of S9 mix (YG1041) were used to evaluate the mutagenic activity of eight polycyclic aromatic hydrocarbons (PAHs), seven nitroarenes (NAs) and seven aromatic amines (AAs). Three cigarette smoke extracts and two extracts of smokers' urine (SUE) were also included. Urinary mutagenicity was then determined on 31 individuals, potentially exposed to PAHs, for 0 h, 7 h, 12 h and 24 h. Concentrations of urinary 1-hydroxypyrene (1OHP) and 3-hydroxybenzo[a]pyrene (3OHBaP), the levels of atmospheric pyrene (Py) and benzo[a]pyrene (BaP), and particulate concentrations in air (AP) were also measured. PAHs could be detected by TA98S and YG1041S, with TA98S being more sensitive than YG1041S. While NAs could be detected by all combinations, YG1041 and YG1041S were more sensitive than TA98S. Although both YG1041S and TA98S could detect AAs, YG1041S was more sensitive than TA98S. Cigarette smoke extract contained mutagenic AAs and NAs, but AAs were the only mutagenic compounds detected in the extracts of smokers' urine. The concentrations of 1OHP (7 h and 12 h) were significantly higher than those at 0 h, but no difference could be detected with 3OHBaP. Correlations were found between Py and 1OHP (7 h and 24 h) and between BaP and 3OHBaP concentrations (7 h, 12 h and 24 h). A significantly elevated urinary mutagenicity was detected with YG1041S at 7h in the group of smokers. A good correlation was determined between AP and the test results with TA98S (7 h) and with YG1041 (0 h and 7 h). Urinary 1OHP correlated with the test results with YG1041S (0 h, 7 h and 12 h) while 3OHBaP correlated with those obtained with YG1041S (7 h). Overall, 21/31 individuals were occupationally exposed to AAs, 15/31 individuals were exposed to NAs, and 2/31 were exposed to PAHs as indicated by the Salmonella mutagenicity assay. The urine mutagenicity test was not effective at monitoring occupational exposure to PAHs. However, the correlation with AP implied the presence of unknown mutagenic atmospheric substances that could modulate the urinary mutagenicity.     

Role of hemin in the inhibition of mutagenic activity of 3-amino-1-methyl-5H-pyrido[4,3-b]indole (Trp-P-2) and other aminoazaarenes

The mechanism of inhibition by hemin of the mutagenic activities of food pyrolysate aminoazaarenes, particularly that of Trp-P-2 (3-amino-1-methyl-5H-pyrido[4,3-b]indole), was investigated. Hemin efficiently inhibited the metabolic activation by S9 of Trp-P-2, as demonstrated by high-performance liquid chromatographic analysis of the reaction mixtures in which Trp-P-2 had been treated with S9 in the presence or absence of hemin. N-Hydroxy-Trp-P-2, an activated form of Trp-P-2 having direct mutagenicity on Salmonella typhimurium TA98, undergoes spontaneous oxidative degradation in its aqueous solution, and the presence of hemin in the solution accelerated the degradation significantly. The presence of excess hemin with N-hydroxy-Trp-P-2 completely abolished the mutagenic activity of this mutagen towards Salmonella. A UV-visible spectroscopic study has suggested the formation of a complex between hemin and N-hydroxy-Trp-P-2/Trp-P-2. In support of this view, the fluorescence spectrum of a Trp-P-2 solution was quenched efficiently by the addition of hemin. These observations indicate that this complex formation plays a role in the observed multiple actions of hemin. Similar inhibitory actions of hemin on several other direct-acting aminoazaarene mutagens are also described, as well as the inhibition activities of protoporphyrin, chlorophyllin, biliverdin and bilirubin.     

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.     

Identification of a new mutagen, 4,4'-diamino-3,3'-dichloro-5-nitrobiphenyl, in river water flowing through an industrial area in Wakayama, Japan

3,3'-Dichlorobenzidine (DCB), which has been assigned as a possible carcinogen to humans (Group 2B) by IARC, is produced as a raw material in the manufacture of polymers and dye intermediates. In our previous paper, we identified DCB as an indirect-acting mutagenic constituent in the water concentrates from the Waka River, which flows through an industrial area in Wakayama, Japan. In this study, we have identified a novel mutagen in the water samples from the Waka River. Organic chemicals in the river water were adsorbed to blue rayon at the site where effluents from chemical plants and a sewage plant were discharged into the river. The adsorbate was highly mutagenic in Salmonella YG1024 in the presence and absence of S9 mix, inducing 440,000 and 170,000 revertants/g blue rayon equivalent, respectively. Two mutagenic fractions, which accounted for 18% and 12% of the total mutagenicity of the water concentrate in YG1024 with S9 mix, were separated by HPLC with a reversed-phase column following Sephadex LH20 column chromatography. Both fractions were further separated by HPLC using reversed-phase columns. On the basis of spectral analysis and co-chromatography using an authentic chemical standard, one mutagen in the former fraction was identified as DCB and one mutagen in the latter fraction was deduced to be a novel chemical, a 5-nitro derivative of DCB (5-nitro-DCB; 4,4'-diamino-3,3'-dichloro-5-nitrobiphenyl). 5-Nitro-DCB showed strong mutagenicity in YG1024 especially with S9 mix, inducing 24,200 revertants/microg. 5-Nitro-DCB was detected in water concentrates in the range from less than detection limit to 6.9 microg/g of blue rayon. DCB was also detected in the range from 13.2 to 104 micro/g of blue rayon. These results demonstrate that Waka River water might be continually contaminated with the indirect-acting mutagens DCB and 5-nitro-DCB as major mutagenic constituents of the river water.     

Detection of mutagenicity of diphenyl ether herbicides in Salmonella typhimurium YG1026 and YG1021

Three kinds of diphenyl ether herbicides, 4-nitrophenyl 2,4,6-trichlorophenyl ether (CNP, chlornitrofen), 2,4-dichlorophenyl 3-methoxy-4-nitrophenyl ether (chlomethoxynil) and 2,4-dichlorophenyl 3-methoxycarbonyl-4-nitrophenyl ether (bifenox), were tested for mutagenicity in Salmonella typhimurium YG1026 and YG1021, which have high nitroreductase activity, and also in S. typhimurium TA100 and TA98. CNP and chlomethoxynil showed mutagenicity in S. typhimurium YG1026, without S9 mix, inducing 50 and 304 revertants per μg. These mutagenicities were suppressed by the addition of S9 mix. CNP and chlomethoxynil were also mutagenic to YG1021 with and without S9 mix, and their mutagenicities were lower than those to YG1026. On the other hand, bifenox was mutagenic to YG1026 only with S9 mix, inducing 3.0 revertants per μg. These three herbicides showed no mutagenicity in S. typhimurium TA100 and TA98 either with or without S9 mix.     

Mutagens in coffee and tea.

Coffee prepared in the usual way for drinking contains a substance(s) that is mutagenic to Salmonella typhimurium TA100 without mammalian microsomal enzymes. One cup of coffee (200 ml) contains mutagen(s) inducing 1.4-4.6 X 10(5) revertants under standard conditions. Instant coffee too is mutagenic to TA100 and one cup of instant coffee prepared from 1 g of coffee powder and 200 ml of water induced 5.6-5.8 X 10(4) revertants of TA100. Caffeine-free instant coffee also has similar mutagenicity. Addition of microsomal enzymes abolished the mutagenicity. Black tea, green tea and Japanese roasted tea were also mutagenic to TA100 without S9 mix and one cup of these teas prepared in the ordinary way produced 1.7-3.8 X 10(4) revertants of TA100. Black tea and green tea were also mutagenic to TA98 in the presence of S9 mix after treatment with a glycosidase from Aspergillus niger, hesperidinase. This type of mutagen in one cup of black tea induced 2.4 X 10(5) revertants of TA98.     

A mutagen precursor in Chinese cabbage, indole-3-acetonitrile, which becomes mutagenic on nitrite treatment

After treatment with nitrite, Chinese cabbage showed direct-acting mutagenicity on Salmonella typhimurium TA100 inducing 3100 revertants per g. One of the mutagen precursors that became mutagenic after nitrite treatment was isolated, and identified as indole-3-acetonitrile. After treatment with nitrite, 1 mg of indole-3-acetonitrile induced 17 400 revertants of TA100 and 21 000 revertants of TA98 without S9 mix.     

Inhibitory effect of dibenzoylmethane on mutagenicity of food-derived heterocyclic amine mutagens

Dibenzoylmethane (DBM), a structural analogue of curcumin (a bioactive phytochemical present in a widely used spice turmeric) was screened for its inhibitory effect against seven cooked food mutagens (heterocyclic amines): 2-amino-3-methylimidazo[4,5-f]quinoline (IQ), 2-amino-3,4-dimethylimidazo[4,5-f]quinoline (MeIQ), 2-amino-3,8-dimethylimidazo[4,5-f]quinoxaline (MeIQx), 3-amino-1,4-dimethyl-5H-pyrido[4,3-b]indole (Trp-P-1), 3-amino-1-methyl-5H-pyrido[4,3-b]indole (Trp-P-2), 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine (PhIP) and 2-amino-6-methyldipyrido[1,2-a:3',2'-d]imidazole (Glu-P-1), in both TA98 and TA100 strains of Salmonella typhimurium using Ames Salmonella/reversion assay in the presence of Aroclor1254-induced rat liver S9 homogenate. DBM has been reported to antagonize the mutagenicity of several chemical carcinogens in vitro and has recently been shown to be even more effective than curcumin in suppressing the 7,12-dimethylbenz[a]anthracene (DMBA)-induced mammary tumors in rats. But there are no reports regarding its antimutagenic properties against cooked food mutagens. Results of the present investigations clearly indicate that dibenzoylmethane is a very potent antimutagenic agent, that could effectively inhibit mutagenicity induced by all the tested cooked food mutagens in both the frame shift (TA98) as well as the base pair mutation sensitive (TA100) strains of S. typhimurium. These highly potent inhibitory effects of dibenzoylmethane against heterocyclic amines observed in our preliminary investigations strongly warrant further studies of its efficacy as a cancer chemopreventive agent.     

Mutagenicity monitoring of airborne particulate matter (PM10) in the Czech Republic.

The mutagenic activities associated with inhalable airborne particulate matter (PM10) collected over a year in four towns (Czech Republic) have been determined. The dichloromethane extracts were tested for mutagenicity using the Ames plate incorporation test and the Kado microsuspension test both with Salmonella typhimurium TA98 and its derivative YG1041 tester strains in the presence and absence of S9 mixture. The aim of this study was to assess the suitability of both bacterial mutagenicity tests and to choose the appropriate indicator strain for monitoring purposes. To elucidate the correlation between mutagenicity and polycyclic aromatic hydrocarbons (PAHs), the concentration of PAHs in the air samples were determined by GC/MS. In general, the significant mutagenicity was obtained in organic extracts of all samples, but differences according to the method and tester strain used were observed. In both mutagenicity tests, the extractable organic mass (EOM) exhibited higher mutagenicity in the YG1041 strain (up to 97 rev/microg in the plate incorporation and 568 rev/microg in the microsuspension tests) than those in TA98 (up to 2.2 rev/microg in the plate incorporation and 14.5 rev/microg in the microsuspension tests). In the plate incorporation test, the direct mutagenic activity in YG1041 was on average 60-fold higher and in microsuspension assay 45-fold higher with respect to strain TA98. In the presence of S9 mix, the mutagenic potency in YG1041 declined (P<0.001) in summer, but increased in TA98 (P<0.05) in samples collected during the winter season. The microsuspension assay provided higher mutagenic responses in both tester strains, but in both strains a significant decrease of mutagenic potency was observed in the presence of S9 mix (P<0.001 for YG1041, P<0.05 for TA98 in winter). The mutagenic potencies detected with both indicator strains correlated well (r=0.54 to 0.87) within each mutagenicity test used but not (for TA98) or moderately (r=0.44 to 0. 66 for YG1041) between both of the tests. The mutagenic activity (in rev/m(3)) likewise the concentration of benzo[a]pyrene and sum of carcinogenic PAHs showed seasonal variation with distinctly higher values during winter season. A correlation between the PAH concentrations and the mutagenicity results for the plate incorporation, but not for the microsuspension tests was found. In samples from higher industrial areas, the higher mutagenicity values were obtained in plate incorporation test with TA98 and in both tests with YG1041 in summer season (P<0.05). According to our results, plate incorporation test seems to be more informative than microsuspension assay. For routine ambient air mutagenicity monitoring, the use of YG1041 tester strain without metabolic activation and the plate incorporation test are to be recommended.     

Inhibitory effect of curcumin and its natural analogues on genotoxicity of heterocyclic amines from cooked food

Curcumin (C) and its natural analogues demethoxycurcumin (dmC) and bisdemethoxycurcumin (bdmC), known for their potent anti-inflammatory, antioxidant, antimutagenic and anticarcinogenic effects, were tested for their possible inhibitory effects against seven cooked food mutagens (heterocyclic amines): 2-amino-3-methylimidazo[4,5-f]quinoline (IQ), 2-amino-3,4-dimethylimidazo[4,5-f]quinoline (MeIQ), 2-amino-3,8-dimethylimidazo[4,5-f]quinoxaline (MeIQx), 3-amino-1,4-dimethyl-5H-pyrido[4,3-b]indole (Trp-P-1), 3-amino-1-methyl-5H-pyrido[4,3-b]indole (Trp-P-2), 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine (PhIP) and 2-amino-6-methyldipyrido[1,2-a:3',2'-d]imidazole (Glu-P-1), in both TA98 and TA100 strains of Salmonella typhimurium using Ames Salmonella/reversion assay in the presence of Aroclor induced rat liver S9 homogenate. In the present investigations, curcumin as well as its two natural analogues i.e., dmC and bdmC were found to be highly effective in suppressing genotoxicity of all the tested cooked food mutagens in a dose-dependent manner, in both the frame shift (TA98) as well as base pair mutation sensitive (TA100) strains of S. typhimurium. However, bdmC appeared to be a relatively less active antimutagen compared to C and dmC. More than 80% inhibition of mutagenicity was observed at 200 microg/plate in case of C and dmC in both TA98 and TA100 against all tested cooked food mutagens. Where as, bdmC showed 39-79% inhibition in TA100 and 60-80% inhibition in TA98, at a dose of 200 microg/plate. These findings warrant further biochemical, enzymatic and in vivo investigations in animal models as well as in humans to establish the chemoprotective effect of these agents against mutagenic heterocyclic amines found in cooked food.     

Mutagenicity of urine from rats after 1-nitropyrene and 2-nitrofluorene administration using new sensitive Salmonella typhimurium strains YG1012 and YG1024

1-Nitropyrene (1-NP) and 2-nitrofluorene (2-NF), two of the most abundant nitro-substituted polycyclic aromatic hydrocarbons (nitro-PAH) present in combustion products such as diesel engine exhaust, were administered intraperitoneally to rats at a dose of 5 mg per animal. Urine samples, 1-NP and 2-NF were tested in the Ames assay using the newly developed Salmonella typhimurium strains YG1012 and YG1024 (overproducing O-acetyltransferase) and their parent strains TA1538 and TA98. In urine, collected over 3 periods of 24 h after administration, most of the mutagens appeared during the first 24 h. The mutagenicity was found to be a factor 2-30 higher in the YG strains when compared to the TA strains. Addition of S9 mix and rat liver cytosol both with and without beta-glucuronidase increased the mutagenicity of urine samples from 1-NP-treated rats. Addition of beta-glucuronidase revealed that a considerable part of the mutagenic metabolites of 1-NP and 2-NF were excreted as glucuronide conjugates. The increase in mutagenicity of urine samples from 2-NF-treated rats after the addition of rat liver cytosol referred to N,O-acyl transfer as a step in activating 2-NF to strong mutagens. The high sensitivity of the YG tester strains indicated that these strains might be used to explore environments where people are exposed to nitro-PAH, such as work places with diesel emission sources.