A sensitive method for the detection of mutagenic nitroarenes: construction of nitroreductase-overproducing derivatives of Salmonella typhimurium strains TA98 and TA100

'Classical nitroreductase' is an enzyme involved in the intracellular metabolic activation of mutagenic nitroarenes. The nitroreductase gene of Salmonella typhimurium TA1538 was cloned into pBR322 and the plasmids harboring the gene were introduced into TA98 and TA100. The resulting strains (YG1021 and YG1026) had more than 50 times higher nitrofurazone-reductase activity than TA1538 containing pBR322, and were extremely sensitive to the mutagenic action of 2-nitrofluorene, 1-nitropyrene and 2-nitronaphthalene. These results indicate that the new strains permit the efficient detection of mutagenic nitroarenes.     

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.     

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.     

Sensitive method for the detection of mutagenic nitroarenes and aromatic amines: new derivatives of Salmonella typhimurium tester strains possessing elevated O-acetyltransferase levels

Acetyl-CoA: N-hydroxyarylamine O-acetyltransferase is an enzyme involved in the intracellular metabolic activation of arylhydroxylamines derived from mutagenic nitroarenes and aromatic amines. The acetyltransferase gene of Salmonella typhimurium TA1538 was cloned into pBR322 and the plasmids harboring the gene were introduced into TA98 and TA100. The resulting strains (YG1024 and YG1029) had about 100 times higher 2-hydroxyamino-6-methyldipyrido[1,2-a:3',2'-d]-imidazole (N-hydroxy-Glu-P-1) O-acetyltransferase activity than TA1538 containing pBR322, and were extremely sensitive to the mutagenic actions of 2-nitrofluorene, 1-nitropyrene, 1,8-dinitropyrene, 2-amino-6-methyldipyrido[1,2-a:3',2-d)-imidazole (Glu-P-1), 2-aminofluorene and 2-aminoanthracene. These results indicate that the new strains permit the efficient detection of the mutagenicity of environmental nitroarenes and aromatic amines.     

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.     

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.     

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.     

Application of Salmonella strains with altered nitroreductase and O-acetyltransferase activities to the evaluation of the mutagenicity of airborne particles

The Ames test was applied to evaluation of the mutagenicity of month's samples of airborne particles from the center of Wroc?aw (SW Poland) collected in August and December 1997. The strains used for the study were TA 98, TA 100 and their derivatives: TA 98 NR, YG 1021, YG 1024, YG 1026, YG 1029, YG 1041, YG 1042. Both studied samples were mutagenic for almost all tested strains, with the exception of the August sample which did not influence the strain TA 100 without the metabolic activation with the S9 fraction. The December sample exhibited higher genotoxic activity than the August sample. Mutagenicity ratios of the strains with reduced nitroreductase and O-acetyltransferase activities were higher, and of the strain without the nitroreductase--lower than those of the parent strains. This indicates that nitro and amino derivatives of PAHs are responsible for the significant proportion of total mutagenicity of the studied samples of particulates. Metabolic activation with the S9 fraction caused the increase of the mutagenic activity of the samples, which indicates the presence of promutagens. The GC-MS analysis revealed the presence of known indirect mutagens from the PAHs group.     

Involvement of nitro-compounds in the mutagenicity of urban Pm2.5 and Pm10 in Turin

Fine particles can be active carriers of toxic compounds into the alveoli of the lungs. Among these compounds are numerous mutagens and carcinogens. The direct mutagenicity per unit mass of fine particulate matter (PM) is significantly higher than that of coarse particles, especially in urban areas. In this study, the mutagenic properties of urban PM2.5 and PM10 were evaluated, and the role of nitro-compounds was estimated. PM2.5 and PM10 samplings, and measurements of NOx and some PAHs were performed daily in 2007 in Turin, following a consolidated in vitro test - the Salmonella mutagenicity assay - conducted with organic extracts of PM2.5 and PM10. The mutagenic properties were assessed for each month of sampling with Salmonella typhimurium strain TA98 and TA98-derived strains: a nitroreductase-deficient mutant strain (TA98NR) and an additional nitroreductase-producing plasmid strain (YG1021). The annual measured mean levels of PM2.5 and PM10 were 34±20 and 48±18μg/m(3). The PM2.5/PM10 ratio ranged from 0.36 to 0.89. The Salmonella assay showed higher mutagenicity in autumn/winter (20±15 TA98NR; 54±39 TA98; 173±161 YG1021 net revertants/m(3)) compared with spring/summer (2±2 TA98NR; 7±8 TA98; 24±27 YG1021 net revertants/m(3)) (p<0.01). There are also statistically significant seasonal differences in the gravimetric analysis data. The number of TA98 net revertants per μg of PM2.5 is 6.5 times greater than per μg PM10. Moreover, the bioassay results showed an amplified response in the YG1021 strain and a reduced response in the TA98NR strain. The net revertant ratio TA98NR/YG1021 is 11±4 for organic extracts of PM2.5 and 13±6 for extracts of PM10 (p<0.01). There is a significant correlation between the NOx and PAH concentrations. These findings illustrate the relevant role of nitro compounds, and they underline the priority in improving preventive measures to reduce air pollution by nitrated molecules.     

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.     

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.     

Esterification of arylhydroxylamines: Evidence for a specific gene product in mutagenesis

Characterization of a $\text{Salmonella}\text{typhmurium}$ mutant strain (TA98/1,8-DNP₆) resistant to the mutagenicity of nitrated polycyclic aromatic hydrocarbons (nitroarenes) revealed that it was also non-responsive to the mutagenic action of nitroso- and N-hydroxylaminoarenes. The mutant strain was fully sensitive to the mutagenic action of the corresponding hydroxamic acid ester. These results suggest that TA98/1,8-DNP₆ is deficient in a specific esterifying enzyme and that esterification of the penultimate mutagenic metabolites of nitro- and aminoarenes ($\text{e.g.}$, arylhydroxylamines) to form potent electrophiles is controlled by a specific gene.     

Genotoxic evaluation of the organophosphorous pesticide temephos

The chemical compound temephos (0,0,0',0'-tetrametyl-0,0'-thiodi-p-phenylene phosphorothioate) is an organophosphorous pesticide that has been used in Brazil since 1967 in control campaigns against the mosquito Aedes aegypti, the vector of dengue and yellow fever. We used single cell gel electrophoresis (SCGE), SOS/umu and Ames/Salmonella assays to test the toxicity and mutagenicity of temephos. Temephos was genotoxic in the SCGE assay, inducing severe DNA lesions (type IV lesions) at doses above 1.34 micro M. It was mutagenic, but not toxic, in the SOS/umu assay to Escherichia coli strain PQ37, but not to PQ35, at concentrations above 1.33 micro M, particularly when the S9 mixture was not used in the assay. Temephos was not mutagenic in the Ames assay with S. typhimurium strains TA97, TA98, TA100 and TA102, both with and without metabolic activation. However, temephos at concentrations above 3.33 micro M was mutagenic to TA98NR, YG7104 and YG7108, both with and without metabolic activation. In conclusion, temephos was genotoxic and mutagenic in all the three tests used, and in two of them at concentrations similar to those routinely used to combat Aedes aegypti.     

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.     

Evidence for an acetoxyarylamine as the ultimate mutagenic reactive intermediate of the carcinogenic aromatic amine 2,4-diaminotoluene

2,4-Diaminotoluene (2,4-DAT) is a mutagenic and hepatocarcinogenic aromatic amine, requiring metabolic activation. We have found that the mutagenic potency of 2,4-DAT in Salmonella TA98 is similar when activated by either Aroclor-1254-induced rat primary hepatocytes or 9000 x g supernatant. Previous work has demonstrated that 2,4-DAT is activated by cytochrome P450. The present report describes an investigation of the role of acetyltransferase in 2,4-DAT activation. Substitution of TA98 with the acetyltransferase-deficient strain TA98/1,8-DNP6 resulted in an approximately 90% decrease in the mutagenic potency for 2,4-DAT using S9 activation. The newly engineered acetyltransferase-enhanced Salmonella tester strain YG1024 (TA98(pYG219] demonstrated greatly enhanced sensitivity to the mutagenicity of 2,4-DAT. Inhibition of O-acetyltransferase activity, either with the selective acetyltransferase inhibitor thiolactomycin, or by competitive inhibition with an alternative substrate for the enzyme, reduced the mutagenicity of 2,4-DAT in this acetyltransferase-enhanced bacterial strain. From these data we conclude that following 2,4-DAT activation by N-hydroxylation by cytochrome P450, the resulting hydroxylamino intermediate is further activated in the bacteria via O-acetylation to form the ultimate reactive intermediate, which is postulated to be 4-acetoxyamino-2-aminotoluene.     

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.     

Comparison of two extraction procedures for the assessment of sediment genotoxicity: implication of polar organic compounds

Four sediment samples (Va?ne Airport VA, Va?ne Center VC, Va?ne North VN and Reference North RN) were collected in the Berre lagoon (France). Sediments were analyzed for polycyclic aromatic hydrocarbons (PAHs) by use of pressurized fluid extraction with a mixture of hexane/dichloromethane followed by HPLC with fluorescence detection analysis. Organic pollutants were also extracted with two solvents for subsequent evaluation of their genotoxicity: a hexane/dichloromethane mixture intended to select non-polar compounds such as PAHs, and 2-propanol intended to select polar contaminants. Sediment extracts were assessed by the Salmonella/microsome mutagenicity test with Salmonella typhimurium TA98+S9 mix and YG1041±S9 mix. Extracts were also assessed for their DNA-damaging activity and their clastogenic/aneugenic properties by the comet assay and the micronucleus test with Chinese Hamster ovary (CHO) cells. The PAH concentrations were 611ngg(-1)dw, 1341ngg(-1) dw, 613ngg(-1)dw and 482ngg(-1)dw for VA, VC, VN and RN, respectively. Two genotoxic profiles were observed, depending on the extraction procedure. All the non-polar extracts were mutagenic for TA98+S9 mix, and VA, VC, VN sediment samples exerted a significant DNA-damaging and clastogenic activity in the presence of S9 mix. All the polar extracts appeared mutagenic for TA98+S9 mix and YG104±S9 mix, and VA, VC, VN were genotoxic and clastogenic both with and without S9 mix. These results indicate that the genotoxic and mutagenic activities mainly originated from PAHs in the non-polar extracts, while these activities came from other genotoxic contaminants, such as aromatic amines and nitroarenes, in the polar extracts. This study focused on the important role of uncharacterized polar contaminants such as nitro-PAHs or aromatic amines in the global mutagenicity of sediments. The necessity to use appropriate extraction solvents to accurately evaluate the genotoxic hazard of aquatic sediments is also highlighted.     

Genotoxicity and DNA adduct formation of incense smoke condensates: comparison with environmental tobacco smoke condensates

Indoor air pollution has now been recognized as a potentially important problem for public health, since people spend most of their day in closed environments. Incense burning is possibly associated with elevated risks of leukemia and brain tumor in children from the epidemiological studies. Thus, evaluation of the genotoxicity of smoke condensates from incense burning is needed. We examined the genotoxicity of incense smoke condensates (ISC) using the Ames test in S. typhimurium strains with different mutagenic specificity and level of metabolic enzyme, the SOS chromotest in E. coli PQ37, and sister chromatid exchange assay in Chinese hamster ovary cells (SCE/CHO). The genotoxicity of environmental tobacco smoke condensates (TSC) was also evaluated by the three assays to compare with the genotoxicity of ISC, ISC showed a positive response in TA98, but not in TA100. It suggested that ISC only contained frame shift mutagens. The mutagenicity of ISC in both strains of TA98NR with deficient nitroreductase and TA98/1,8-DNP₆ with deficient O-acetyl-transferase was markedly decreased compared to that in TA98 strain. However, the mutagenicity was enhanced in YG1024 with overexpression of O-acetyltransferase activity. Thus, nitroarenes seemed to be responsible in part for the mutagenicity of ISC. Interestingly, all of the four ISC and two TSC samples showed a dose-dependent genotoxic response in the SOS chromotest with E. coli PQ37 but a low SCE induction of those samples were observed in CHO cells. When the genotoxicity was analyzed based on the condensates per one gram of original samples, the genotoxicity of two TSC condensates in prokaryotic cells was higher than that of four ISC samples except for the genotoxicity of TSC-2 in TA98 strain. However, the genotoxicity of certain ISC in eukaryotic cells based on the SCE/CHO assay was higher than that of TSC. To compare the covalent binding of DNA reactive intermediates of ISC and TSC to S. typhimurium TA98, the DNA adducts were evaluated by the ³²P-postlabeling method with butanol extraction version. Similar diagonal radioactive zone (DRZ) was observed between ISC and CSC. However, DNA adduct levels induced by TSC were much greater than that of ISC.     

Evaluation of extracts from Coccoloba mollis using the Salmonella/microsome system and in vivo tests

The common everyday use of medicinal plants is an ancient, and still very widespread practice, whereby the need for studies on their possible toxicity and mutagenic properties. The species Coccoloba mollis has been much used in phytotherapy, mainly in cases involving loss of memory and stress. In order to investigate its genotoxic and mutagenic potential, ethanolic extracts from the leaves and roots underwent Salmonella/microsome assaying (TA98 and TA100 strains, with and without exogenous metabolism - S9), besides comet and micronucleus tests in vivo.There was no significant increase in the number of revertants/plate of Salmonella strains in any of the analyzed root-extract concentrations, although the extract itself was extremely toxic to the Salmonella TA98 strain in the tests carried out with S9 (doses varying from 0.005 to 0.5 μg/plate). On the other hand, the leaf-extract induced mutations in the TA98 strain in the absence of S9 in the highest concentration evaluated, although at very low mutagenic potency (0.004 rev/ μg). Furthermore, there was no statistically significant increase in the number of comets and micronuclei, in treatments involving Swiss mice. It was obvious that extracts of Coccoloba mollis, under the described experimental conditions, are not mutagenic.     

The influence of automobile exhausts on mutagenicity of soils: contamination with, fractionation, separation, and preliminary identification of mutagens in the Salmonella/reversion assay and effects of solvent fractions on the sister-chromatid exchanges in human lymphocyte cultures and in the in vivo mouse bone marrow micronucleus assay

To test the assumption that automobile exhausts contribute to soil mutagenicity, two soils with low levels of mutagenic activities were exposed to traffic exhausts at a heavily charged junction of German motorways (Autobahnen) for 3, 7, 10, 13, 17, 21, and 26 weeks. Indeed, in the presence of a metabolic activation system from rat liver (S9), an average increase of 8 and 9 (4 and 12) revertants per gram per week was found in Salmonella typhimurium TA 98 (TA 100). In the absence of S9, meaningful measurements were impossible on account of a concurrent dose dependent increase of toxicity. No correlation between the increase of mutagenicity and the contents of polycyclic aromatic hydrocarbons (PAH) could be detected. In another series, soils sampled at the roadside and at distances of 10 and 50m of five roads near Mainz expressed 10-20-fold higher mutagenicity (revertants per gram) under identical test conditions as compared with the average of agricultural soils. Toxic effects, however, again confounded the results and no correlation between the distance from roads and the levels of mutagenicity could be demonstrated. Subsequently, Soxhlet-extraction with the solvent sequence dichloromethane, acetone, and toluene/diethylketone was found to be an optimum procedure for soils at roadsides. The mass balance of solvent fractionation of such soils revealed that <2% each belonged to organic acids and bases, approximately 4% to fractions designed polar neutrals, approximately 8% to polar aromatics, approximately 7% to dichloromethane solubles, and approximately 79% to cylohexane solubles, among them approximately 63% acetone soluble compounds. The major part of mutagenicity (55-65%) was present in the fraction of polar aromatics, followed by polar neutrals and the acetone subfraction of cyclohexane solubles ( approximately 10% each) summarizing the results obtained with S. typhimurium TA 98, TA 98NR, YG 1021, YG 1024, TA 100, YG 1026, and YG 1029 with and without addition of S9. The modified tester strains, either deficient in nitroreductase (TA 98NR) or overproducing nitroreductase (YG 1021, 1026) or O-acetyl-transferase (YG 1024, 1026), indicated a major contribution of nitroarenes to soil mutagenicity. With respect to mutagenic PAH, high pressure liquid chromatography (HPLC) revealed that >90% of dibenz[a,h]anthracene (4.18mg/kg soil), benzo[a]pyrene (1.96mg), benzofluoranthenes (0.14mg), and benz[a]anthracene (0. 18mg) were present in the acetone subfraction of cyclohexane solubles. Concentrations and mutagenic activities, however, did not correlate. Additional preparative and analytical HPLC of the solvent fractions of polar neutrals and polar aromatics, resulted in the tentative identification of 2-nitrofluorene. Analysis of the vertical profile of soil revealed an increase of mutagenicity per gram from the surface to a maximum at 5-15cm depth and a subsequent decrease with very little activity remaining deeper than 35cm. In human lymphocyte cultures, the fraction of polar aromatics, 0.01-0. 3microg/ml, induced 11.27+/-4.76-20.70+/-6.19 sister-chromatid exchanges (SCE) per cell in the absence of S9 (solvent control: 10. 16+/-4.83 SCE per cell) and 12.77+/-6.53-17.87+/-4.93 SCE per cell in the presence of S9 (solvent control: 8.37+/-3.92 SCE per cell). However, no activities could be detected in the fractions of polar neutrals and non-polar neutrals. Again, negative results were obtained in the in vivo mouse bone marrow micronucleus assay at 2000mg/kg p.o. with all fractions.