Takeshi Ohe

Mutagenic characteristics of river waters flowing through large metropolitan areas in North America

The hanging technique using blue rayon, which specifically adsorbs mutagens with multicyclic planar structures, has the advantages over most conventional methods of not having to bring large volumes of water back to the laboratory for extraction of organic materials. Therefore, for the same effort the hanging blue rayon technique allows for the analysis of more samples from remote sites, although it has a disadvantage of not allowing quantitative analysis. In this study, the blue rayon hanging technique was used to collect organic mutagens in river waters that flow through metropolitan areas in northeastern North America. Monitoring was performed at a total of 21 sites: the Providence River system (4 sites), the Charles River (2 sites), the Potomac River (6 sites), the St. Lawrence River (5 sites), the Hudson River (3 sites), and the East River (1 site). Mutagenicity was evaluated using the Salmonella assay with strains TA98, TA100, YG1024, YG1041, and YG1042 with and without metabolic activation. The results demonstrated that strains YG1041 and YG1024 were much more sensitive than TA98 with S9 mix. Fifteen samples out of 21 were positive in YG1041 with S9 mix. Six samples gave 5000-18,400 revertants/g blue rayon equivalent. YG1042 was also much more sensitive than TA100. Eight samples were positive in YG1042 with S9 mix. The highest activity was 10,200 revertants/g blue rayon equivalent. The overall results showed that rivers flowing through major cities in North America contain frameshift-type, aromatic amine-like mutagenic activity. However, the levels of mutagenic activity in these rivers were much lower than expected based on prior analyses and calculated population-to-discharge ratios. Further research, such as detailed chemical analyses and/or simultaneous comparisons of several different adsorbents (e.g. XAD and blue rayon), will be needed to clarify the observed differences between North American blue rayon values and published values for European and Asian river systems.

Identification of 2-[2-(acetylamino)-4-amino-5-methoxyphenyl]-5-amino-7-bromo-4-chloro-2H-benzotriazole (PBTA-4) as a potent mutagen in river water in Kyoto and Aichi prefectures, Japan.

We have previously isolated five mutagens in blue rayon-adsorbed substances from water at a site below sewage plants in the Nishitakase River, in Kyoto, Japan, and identified two of them as 2-phenylbenzotriazole derivatives, 2-[2-(acetylamino)-4-[bis(2-methoxyethyl)amino]-5-methoxyphenyl]-5-amino-7-bromo-4-chloro-2H-benzotriazole (PBTA-1) and 2-[2-(acetylamino)-4-[(2-cyanoethyl)ethylamino]-5-methoxyphenyl]-5-amino-7-bromo-4-chloro-2H-benzotriazole (PBTA-2). In the present study, we collected adsorbed materials on blue cotton (3 kg x 9 times) at the same location, and isolated a sufficient amount (97 microg) of one of the remaining three mutagens other than PBTA-1 and PBTA-2, for structural analysis, by multiple column chromatography. The structure of mutagen, accounting for 12% of the total mutagenicity of the blue rayon-adsorbed substances, was determined to be a PBTA-1 analogue, 2-[2-(acetylamino)-4-amino-5-methoxyphenyl]-5-amino-7-bromo-4-chloro-2H-benzotriazole (PBTA-4). PBTA-4 is a potent mutagen, inducing 190,000 and 7,800,000 revertants of Salmonella typhimurium TA98 and YG1024 per microgram, respectively, in the presence of S9 mix. In addition to the water of the Nishitakase River, PBTA-4 was detected in water samples from two rivers that flow through other regions where textile-dyeing industries have been developed. Like other PBTA analogues, PBTA-4 might also be produced from azo dyes during industrial processes in dyeing factories and treatment at sewage plants.

Quantification of mutagenic/carcinogenic heterocyclic amines, MeIQx, Trp-P-1, Trp-P-2 and PhIP, contributing highly to genotoxicity of river water

Four mutagenic/carcinogenic heterocyclic amines (HCAs), 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) and 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine (PhIP), in organic extracts obtained by blue rayon hanging method from the Yodo River water were quantified. Blue rayon extracts obtained were separated in two stages of fractionation by reversed-phase high performance liquid chromatography (HPLC), and the quantification of corresponding fractions was performed by HPLC with an electrochemical detector for MeIQx and a fluorometric detector for Trp-P-1, Trp-P-2 and PhIP. The geometrical mean values of MeIQx, Trp-P-1, Trp-P-2 and PhIP in extracts collected at 11 locations from the Yodo River systems were 4.8, 26.9, 37.3, and 11.9 ng/g blue rayon equivalent, respectively. The total amounts of four HCAs accounted for mean 24% of the genotoxicity of blue rayon extracts evaluated by the umu test using an O-acetyltransferase-overproducing strain NM2009.

Catechins are not major components responsible for anti-genotoxic effects of tea extracts against nitroarenes

The anti-genotoxic properties of tea leaf extracts were examined in a Salmonella umu-test. Seven non-fermented teas (green tea), one semi-fermented tea (oolong tea), two fermented teas (black tea and Chinese pu er tea) and two other teas were examined for their anti-genotoxic abilities and for their catechins contents. This was to study the relationship between catechins contents and anti-genotoxic activity of various tea leaf extracts. All types of tea extracts showed more potent suppressive effects against umu gene expression of the SOS response in Salmonella typhimurium TA1535/pSK 1002 induced by four nitroarenes (1-nitropyrene, 2-nitrofluorene, 3-nitrofluoranthene and a mixture of 1,6- and 1,8-dinitropyrene) rather than 4-NQO, AF-2 and MNNG. The anti-genotoxic effect of 12 tea leaf extracts on 1-NP, 2-NF, 3-NF and DNP decreased in the order: oolong tea (semi-fermented tea)>black tea (fermented tea)>sencha (non-fermented tea, an ordinary grade green tea)>tocyucya (other tea)>Chinese pu er tea (fermented tea). The amount of catechins (EGC, C, EGCG, EC and ECG) in various teas in decreasing order was non-fermented tea>semi-fermented tea>fermented tea>other tea. A remarkable feature was the effectiveness of black tea and Chinese pu er tea in suppressing the genotoxicity induced by nitroarenes, in spite of the fact that these fermented teas do not have high catechins contents. Statistical analysis showed that no significant (P<0.01) correlation was found between the anti-genotoxicity of tea extracts against nitroarenes and the catechins contents in tea leaf extracts. In further experiment, fractionation of sencha extract by HPLC revealed that anti-genotoxicity of the peak fraction corresponding to catechins accounted for <10% of the total anti-genotoxic activity of sencha extract against for 1-nitropyrene. These results suggest that catechins are not major components responsible for the anti-genotoxic effects of tea leaf extracts against direct-acting nitroarenes.

Synthesis of 2-phenylbenzotriazole-type mutagens, PBTA-5 and PBTA-6, and their detection in river water from Japan

We previously determined the chemical structures of four 2-phenylbenzotriazole mutagens (PBTA-1, -2, -3 and -4) in blue rayon-adsorbed material from the Nishitakase River in Kyoto prefecture and the Nikko River in Aichi prefecture in Japan. On the basis of a synthesis study, these four PBTA derivatives were deduced to have originated from corresponding dinitrophenylazo dyes by reduction and chlorination. 2-[(2-Bromo-4,6-dinitrophenyl)azo]-5-[bis(2-acetoxyethyl) amino]-4-methoxyacetanilide (Color Index Name, Disperse Blue 79:1; CAS Registry Number, 75497-74-4) is a very common dinitrophenylazo dye used in textile dyeing factories. In the present study, we synthesized 2-[4-[bis(2-acetoxyethyl)amino]-2-(acetylamino)-5-methoxyphenyl]-5-amino-7-bromo-4-chloro-2H-benzotriazole (PBTA-5) from Disperse Blue 79:1 by reduction with sodium hydrosulfite and subsequent chlorination with sodium hypochlorite. On hydrolysis of PBTA-5 with alkali, 2-[2-(acetylamino)-4-[bis(2-hydroxyethyl)amino]-5-methoxyphenyl]-5-amino-7-bromo-4-chloro-2H-benzotriazole (PBTA-6) was obtained. Both PBTA-5 and -6 were potent mutagens, inducing 723,000 revertants and 485,000 revertants per microgram of Salmonella typhimurium YG1024, respectively, in the presence of S9 mix. To clarify whether PBTA-5 and -6 exist in the environment, water samples were collected from five rivers flowing through regions where textile dyeing industries are developed. PBTA-6 was detected at levels of 3-134 ng/g blue rayon in all water samples that were examined. On the other hand, the amount of PBTA-5 in the samples was less than the detection limit.

Genotoxic activity of 1-nitropyrene in water from the Yodo River, Japan

The identification of mutagenic 1-nitropyrene, one of the direct-acting nitroarenes, in a source of municipal drinking water is described. A diethyl ether extract recovered from river water by the XAD-2 resin column method was separated into neutral, acid and basic fractions. The neutral fraction accounted for 52 and 36%, respectively, of the genotoxicity of the extract in the absence and the presence of the metabolic activation system, for strain NM2009, which is sensitive to nitroarenes and/or aminoarenes. When separated by silica gel column chromatography, the benzene fraction of the neutral fraction, showed the highest genotoxic activity. The genotoxicity of the benzene fraction accounted for 80 and 60%, respectively, of the neutral fraction, in the absence and the presence of S9 mix. These results show that mutagenic nitroarenes might be contained in the benzene fraction of the neutral one. The benzene fraction was further subjected to HPLC and fractionated. A 1-nitropyrene-corresponding fraction was collected and subjected to capillary gas chromatography-mass spectrometry (GC-MS). The mass spectrum showed molecular and fragment ion peaks of 1-nitropyrene: 247, 217, 201, 189. Moreover, the concentration of 1-nitropyrene in municipal river water was 1 ng/l, accounting for only 1% of the total genotoxicity.

Mutation spectra in Salmonella of analogues of MX: implications of chemical structure for mutational mechanisms

We determined the mutation spectra in Salmonella of four chlorinated butenoic acid analogues (BA-1 through BA-4) of the drinking water mutagen 3-chloro-4-(dichloromethyl)-5-hydroxy-2(5H)-furanone (MX) and compared the results with those generated previously by us for MX and a related compound, MCF. We then considered relationships between the properties of mutagenic potency and mutational specificity for these six chlorinated butenoic acid analogues. In TA98, the three most potent mutagens, BA-3, BA-4, MX, and the organic extract, all induced large percentages of complex frameshifts (33-67%), which distinguish these agents from any other class of compound studied previously. In TA100, which has only GC sites for mutation recovery, >71% of the mutations induced by all of the agents were GC-->TA transversions. The availability of both GC and TA sites for mutation in TA104 resulted in greater distinctions in mutational specificity than in TA100. MX targeted GC sites almost exclusively (98%); the structurally similar BA-4 and BA-2 produced mutations at similar frequencies at both GC and AT sites; and the structurally similar BA-3 and BA-1 induced most mutations at AT sites (69%). Thus, large variations in structural properties influencing relative mutagenic potency appeared to be distinct from the more localized similar structural features influencing mutagenic specificity in TA104. Among a set of physicochemical properties examined for the six butenoic acids, a significant correlation was found between pK(a) and mutagenic potency in TA100, even when the unionized fraction of the activity dose was considered. In addition, a correlation in CLOGP for BA-1 to BA-4 suggested a role for bioavailability in determining mutagenic potency. These results illustrate the potential value of structural analyses for exploring the relationship between chemical structure and mutational mechanisms. To our knowledge, this is the first study in which such analyses have been applied to structural analogues for which both mutagenic potency and mutation spectra date were available.

Antigenotoxic activities of chitin and chitosan as assayed by sister chromatid exchange.

The antigenotoxic activities of chitin and chitosan were studied using sister chromatid exchange assay by examining the adsorption of four kinds of mutagens. These two dietary animal fibers showed similar patterns in reducing the genotoxicity of aqueous solutions of the hydrophobic mutagens, 4-nitroquinoline-N-oxide and dinitropyrene, in distilled water. Under similar conditions, the antigenotoxic activities of chitin and chitosan for mitomycin C were 87 and 0%, and those for adriamycin were 47 and 78%, respectively. In addition, the antigenotoxic activity of both fibers for MMC was affected by the pH value of the aqueous solution between 2.5 and 7.2, but that of ADM was not. The results demonstrate that chitin and chitosan may have protective effects against environmental mutagens by adsorbing them in ionic and nonionic solutions.

Levels and behavior of 2-phenylbenzotoriazole-type mutagens in the effluent of a sewage treatment plant

We previously reported on the isolation and structural determination of five 2-phenylbenzotriazole (PBTA)-type mutagens (PBTA-1, PBTA-2, PBTA-3, PBTA-4 and PBTA-6) in blue rayon/cotton adsorbed substances collected from surface waters at sites located downstream of sewage treatment plants. We also noted that PBTA-1 and PBTA-2 were discharged from sewage treatment plants and subsequently diluted or decomposed while moving down the Yodo River system. However, it has not been investigated whether they are commonly discharged from sewage treatment plants into rivers. The main purpose of this study was to make a comprehensive survey of levels and behavior of PBTA-type mutagens in effluents discharged from the sewage treatment plant located along the bank of the Uji River, one tributary of the Yodo River system. Water samples were collected at the outlet of the sewage treatment plant for 16 consecutive days in May 1999 and 11 consecutive days in December 1999. Organic constituents were obtained via sorption to blue rayon and subsequent methanol elution. Extract mutagenic activity was measured using Salmonella typhimurium YG1024 with metabolic activation. PBTA-type mutagens (PBTA-1, PBTA-2, PBTA-3, PBTA-4, PBTA-5 and PBTA-6) were quantified by HPLC with electrochemical detection, followed by HPLC purification on reverse-phase columns. The study showed that PBTA-2, PBTA-3, PBTA-4 and PBTA-6 were detected in most samples. The total contribution of these four PBTA-type mutagens to overall extract mutagenicity is on average 33% for the May 1999 sample and 58% for the December 1999 sample. The individual PBTA compounds that had the largest contribution to the overall mutagenicity were PBTA-3 and PBTA-4, accounting for 11 and 16% in May 1999, and 25 and 26% in December 1999. A further comparative study was done in December 1999 using the blue rayon hanging method and the results were similar to those obtained using the blue rayon column method. In conclusion, the present study showed that PBTA-2, PBTA-3, PBTA-4 and PBTA-6 were commonly discharged from a sewage treatment plant into the Uji River, and they accounted for a substantial portion of the effluent mutagenicity.

Gentoxocity of blue rayon extracts from river waters using sister chromatid exchange in cultured mammalian cells

Using cultured Chinese hamster lung (CHL) cells, sister chromatid exchange (SCE) assays were carried out with blue rayon extracts recovered at seven sampling locations from the Katsura, Nishitakase and Kamo Rivers, tributaries of the Yodo River, in Kyoto City, Japan. The downstream extracts of wastewater treatment plants showed higher SCE frequencies than the upstream extracts both with and without metabolic activation, suggesting that the effluents from wastewater treatment plants were the possible pollution sources of genotoxic chemicals in the rivers. The results show the possible use of SCE in CHL cells for the monitoring of genotoxicity of blue rayon extracts from river waters. In addition, simultaneous treatment with sodium thiosulfate significantly reduced the frequencies of SCE induced by blue rayon extracts.