Airplane emissions: a source of mutagenic nitrated polycyclic aromatic hydrocarbons

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

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.     

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.     

Indirect- and direct-acting mutagenicity of diesel,coal and wood burning-derived particulates and contribution of polycyclic aromatic hydrocarbons and nitropolycyclic aromatic hydrocarbons

Particulates exhausted from two types of diesel engines (DEPs), burning-derived particulates from three types of coal (CBPs) and burning-derived particulates from three types of wood (WBPs) were separated into four fractions by silica-gel column chromatography using n-hexane, n-hexane–dichloromethane (3:1, v/v), dichloromethane and methanol, as the corresponding eluents. The indirect-acting mutagenicity of each fraction was assayed by the Ames test using the Salmonella typhimurium TA100 strain with S9 mix and the direct-acting mutagenicity was assayed using the S. typhimurium TA98 strain without S9 mix. The polycyclic aromatic hydrocarbons (PAHs) and nitropolycyclic aromatic hydrocarbons (NPAHs) of each fraction were determined by high-performance liquid chromatography (HPLC). Both direct- and indirect-acting of mutagenicities were the highest in samples of DEPs. The contributions of PAHs in samples of WBPs and NPAHs in DEPs were the largest, respectively.     

Photodecomposition of 1-nitropyrene and other direct-acting mutagens extracted from diesel-exhaust particulates

The effect of irradiation with wavelengths of 320-418 nm on direct-acting mutagenicity of 1-nitropyrene (1-NP) and particulate-matter extracts of a direct-injecting diesel engine was examined. The activity of samples in the Ames test with and without addition of S9 mix in Salmonella typhimurium strain TA98, TA100 and TA1538 decreased with increasing irradiation energy. Visible light was sufficient to destroy the mutagenicity of a 0.1-mM 1-NP solution. The same was true for particulate matter crude extracts as well as the transitional and oxygenate subfractions isolated by column chromatography. UV spectroscopy, thin-layer chromatography and GC-MS analysis were performed to characterize the irradiation products of 1-NP. The mechanism of photodecomposition of 1-NP at different wavelengths and the significance of this finding for the evaluation of health risks from diesel vehicles are discussed.     

Bioactivation of cysteine conjugates of 1-nitropyrene oxides by cysteine conjugate beta-lyase purified from Peptostreptococcus magnus.

To determine the role of cysteine conjugate beta-lyase (beta-lyase) in the metabolism of mutagenic nitropolycyclic aromatic hydrocarbons, we determined the effect of beta-lyase on the mutagenicities and DNA binding of cysteine conjugates of 4,5-epoxy-4,5-dihydro-1-nitropyrene (1-NP 4,5-oxide) and 9,10-epoxy-9,10-dihydro-1-nitropyrene (1-NP 9,10-oxide), which are detoxified metabolites of the mutagenic compound 1-nitropyrene. We purified beta-lyase from Peptostreptococcus magnus GAI0663, since P. magnus is one of the constituents of the intestinal microflora and exhibits high levels of degrading activity with cysteine conjugates of 1-nitropyrene oxides (1-NP oxide-Cys). The activity of purified beta-lyase was optimal at pH 7.5 to 8.0, was completely inhibited by aminooxyacetic acid and hydroxylamine, and was eliminated by heating the enzyme at 55 degrees C for 5 min. The molecular weight of beta-lyase was 150,000, as determined by fast protein liquid chromatography. S-Arylcysteine conjugates were good substrates for this enzyme. As determined by the Salmonella mutagenicity test, 5 ng of beta-lyase protein increased the mutagenicity of the cysteine conjugate of 1-NP 9,10-oxide (10 nmol per plate) 4.5-fold in Salmonella typhimurium TA98 and 4.1-fold in strain TA100. However, beta-lyase had little effect on the cysteine conjugate of 1-NP 4,5-oxide (10 nmol per plate). Both conjugates exhibited only low levels of mutagenicity with nitroreductase-deficient strain TA98NR. In vitro binding of 1-NP oxide-Cys to calf thymus DNA was increased by adding purified beta-lyase or xanthine oxidase.(ABSTRACT TRUNCATED AT 250 WORDS)     

Assessing the Mutagenic Potential of Surface Sediments from Beijing Guanting Reservoir to Salmonella typhimurium

Mutagenicity of organic extracts from Beijing Guanting Reservoir sediments was investigated with TA98 and TA100 of Salmonella typhimurium. TA98 and TA100 were employed to detect frameshift mutation and base-pair substitution mutation, respectively. For TA100, no positive result was found, while TA98 was more sensitive and pro-mutagenic frameshift mutagens were mainly detected in sediments. Sediments from northern and southern Guanting Reservoir were at potential mutagenic risk. No mutagenicity was found in the sediments from the entrance of the tributaries, but strong mutagenicity was observed in the sediments from the outlet of the reservoir. Chemical analysis was also performed, and poor correlation was found between mutagenicity and organochlorine pesticides (OCPs). However, significant positive correlation was found for polycyclic aromatic hydrocarbons (PAHs) (r = 0.603–0.946), which showed that PAHs were dominated for the tested mutagenicity in the sediments. Polychlorinated biphenyls (PCBs) might induce mutagenicity or promote the mutagenicity of other substances.     

Mutagenicity and polycyclic aromatic hydrocarbons analysis of airborne particulate matters from Taipei City

The mutagenic activity of dichloromethane extracts of 147 air particulate samples collected from 8 stations during December 1986-June 1987 in Taipei city was consistently higher in S. typhimurium strain TA 98 than in strain TA 100 in the presence of S9 mixture. Among the 8 stations, Nan Kang Police Station, Fu Hsing Elementary School, and Chung Hsing University which were located in the industrial district, downtown area, and heavy traffic zone, respectively, had significantly higher levels of PAHs than the other stations. In contrast, the levels of PAHs were much lower in the suburban station, near Pei Tou Elementary School. However, PAH contents of the air particulate samples collected from these stations did not show good correlation with their mutagenicity. The air particulates collected at some stations on Sunday when the traffic changed from heavy to light showed lower mutagenicity and PAH contents as compared with the other weekdays at the same stations. On the contrary, the samples collected at Pei Tou station in a suburban area where the traffic changed from light to heavy on Sunday showed higher mutagenicity and PAH contents. The monthly average of PAHs of air particulate samples collected over a 7-month period from 8 stations in Taipei city was lower than the average in 1980. Moreover, when compared with other countries, such as U.S.A., the Netherlands, West Germany, Italy, Norway, and Japan, the levels of PAHs and mutagenicity of air particulate matters in Taipei city were similar or slightly lower. The mutagenicity and contents of PAHs of air particulates collected from burnt ABS were significantly higher than those of burnt PVC. One sample PT-6-3 was collected while a nearby garbage collection area was on fire. The mutagenicity of that sample increased 3 to 16 fold and contained an 11 to 33 times higher content of the six PAHs (BaP, BeP, BbF, BaA, Chr, and DbA) as compared with the other samples collected at the same location at a different time. The higher mutagenicity and PAH contents of that sample might be due to the pollution of the air from combustion of the garbage containing products made of ABS.     

Mutagenicity in Salmonella typhimurium mutants of serum extracts from airborne particulates

Airborne particulates collected from urban and non-urban air were extracted with calf serum or benzene, and their mutagenic potencies were evaluated in the Salmonella reversion assay. The serum extracts were mutagenic to strains TA98 and TA100 and contained both direct- and indirect-acting mutagens. Mutagenic activities for TA98 recovered from the particulates by serum or benzene extraction were much less in the serum extracts than in the benzene extracts. There was no significant difference in mutagenic potencies of the extracts between the urban and non-urban particulates, irrespective of the presence of S9 mix. The calculated mutagenic activities per m3 of air, however, were greater for urban air than for non-urban air, because of higher concentration of particulates in urban air than in non-urban air. Serum effectively reduced both direct and indirect mutagenic activities of the benzene extracts except for an insufficient reduction in direct mutagenicity at a high dose of benzene extracts. These findings suggest that serum could contribute greatly to decrease the mutagenicity of airborne particulates by mechanisms such as less efficient solubilization of mutagenic components and inactivation by protein binding. Biological availability of mutagens, therefore, should be considered for evaluation of actual mutagenic hazard by airborne particulates.     

Evaluation of the mutagenicity of combustion particles from several common biomass fuels in the Ames/Salmonella microsome test

We have evaluated the mutagenicity of dichloromethane extracts of combustion particles from several biomass fuels that are commonly used in developing countries in Salmonella strains TA98 +/- S9 and TA100 +/- S9. Combustion-particle extracts from dried cow dung and crop residue exhibited mutagenic potencies similar to wood-smoke extracts (0.0-1.0 rev./microgram extract). However, extracts from coconut-shell-smoke particles showed relatively potent direct-acting mutagenicity (1.6 rev./micrograms, TA98-S9). Results from testing this sample in nitroreductase- and acetylase- deficient strains TA98NR and TA98 (1,8-DNP-6) revealed no contribution from nitroarenes.     

Assessment of the Mutagenicity of Sediments from Yangtze River Estuary Using Salmonella Typhimurium/Microsome Assay

Sediments in estuaries are of important environmental concern because they may act as pollution sinks and sources to the overlying water body. These sediments can be accumulated by benthic organisms. This study assessed the mutagenic potential of sediment extracts from the Yangtze River estuary by using the Ames fluctuation assay with the Salmonella typhimurium his (−) strain TA98 (frameshift mutagen indicator) and TA100 (baseshift mutagen indicator). Most of the sediment samples were mutagenic to the strain TA98, regardless of the presence or absence of exogenous metabolic activation (S9 induction by β-naphthoflavone/phenobarbital). However, none of the samples were mutagenic to the strain TA100. Thus, the mutagenicity pattern was mainly frameshift mutation, and the responsible toxicants were both direct (without S9 mix) and indirect (with S9 mix) mutagens. The mutagenicity of the sediment extracts increased when S9 was added. Chemical analysis showed a poor correlation between the content of priority polycyclic aromatic hydrocarbons and the detected mutagenicity in each sample. The concept of effect-directed analysis was used to analyze possible compounds responsible for the detected mutagenic effects. With regard to the mutagenicity of sediment fractions, non-polar compounds as well as weakly and moderately polar compounds played a main role. Further investigations should be conducted to identify the responsible components.     

Genotoxic and mutagenic activity of environmental air samples in Flanders, Belgium

Atmospheric pollution is assumed to play a role in the incidence of respiratory diseases and cancers. Airborne particles are able to penetrate deep into the lung and are composed of complex chemical mixtures, including mutagens and carcinogens such as polycyclic aromatic compounds (PACs). The present study reports mutagenic and genotoxic activities associated with ambient air collected near a busy street in Borgerhout, at an industrial site in Hoboken and in Peer, a rural community 70 km east of Antwerp in Flanders, Belgium. Airborne particulates (PM10) and semi-volatile organic compounds were sampled during winter and summer. Samples were collected with a high-volume sampler using quartz filters (QF) and polyurethane foam (PUF) cartridges. The mutagenic and genotoxic activity of the organic extracts was determined using the Salmonella test/standard plate-incorporation assay and the Vitotox assay. Concentrations of 16 polycyclic aromatic hydrocarbons (PAHs) in the extracts were determined by reversed-phase high-performance liquid chromatography (HPLC). The mutagenicity assay, using Salmonella typhimurium strain TA98, demonstrated direct mutagenicity of up to 58 revertants/m3 for the QF extracts and low or no mutagenic activity in the PUF extracts. Metabolic activation of the samples resulted in high indirect mutagenicity for both QF and PUF extracts: up to 96 revertants/m3 were found in QF samples and 62 revertants/m3 in PUF samples. Genotoxic effects of the filter extracts were assessed with the Vitotox assay: some direct genotoxic effects were noted, i.e. without metabolic activation, but almost no effects were observed after metabolic activation. Without activation, most PUF extracts were bacteriotoxic. With metabolic activation this toxicity disappeared, but genotoxic effects were not observed. Statistical analysis showed that the observed biological effects correlated well with the PAH concentrations.     

Genotoxicity of urban air pollutants in the Czech Republic. Part I. Bacterial mutagenic potencies of organic compounds adsorbed on PM10 particulates

As part of a long-term program to investigate the impact of air pollution on the health of a population in a polluted region in Northern Bohemia, mutagenicity of extractable organic matter (EOM) from air particles PM10 was investigated by the means of Salmonella typhimurium indicator strains TA98 and YG1041 using the Ames plate incorporation assay. The air samples were collected in both the polluted and the control districts during the summers and winters of 1993-1994. In the polluted district, the collection was repeated during the winter of 1996-1997. The crude extracts from filters pooled according to the locality and the season were fractionated by acid-base partitioning into acid, base, and neutral fractions. The neutral fractions were further fractionated by silica gel column chromatography into five subfractions. The induction of revertants with the crude extracts was higher in winter samples than in summer samples. Both indirect-acting and direct-acting mutagenicity were observed. The indirect mutagenic potency of aromatic subfractions containing polycyclic aromatic hydrocarbons (PAHs) was generally low. The mutagenic potency detected with TA98 was more distinct only in the winter sample 1993-1994 from the polluted area, where the aromatic subfraction accounted for 23% of total mutagenicity. In both strains, the highest direct-acting mutagenicity was found in slightly polar fractions containing nitro-PAHs. The mutagenic potency detected with YG1041 was about two orders of magnitude higher than that detected with TA98. No substantial locational- or time-related variances in the mutagenic potencies of EOM, or in the spectrum of chemical components identified in individual fractions were found. The polluted district, in comparison to the control district, was found to have higher amounts of EOM, carcinogenic PAHs and mutagenicity of air particles (rev/m(3)). The fractionating process, combined with the bacterial mutagenicity test, confirmed that nitro-derivatives are the most important contributors to the bacterial mutagenicity of air particles. However, this study did not fulfill the expectancy to bring substantially new, clear-cut information on the composition and the biological activity of air pollution in both districts.     

Mutagenicity in salmonella of hazardous wastes and urine from rats fed these wastes

15 hazardous industrial waste samples were evaluated for mutagenicity in the Salmonella plate-incorporation assay using strains TA98 and TA100 in the presence and absence of Aroclor 1254-induced rat liver S9. Dichloromethane/methanol extracts of the crude wastes were also evaluated. 7 of the crude wastes were mutagenic, but only 2 of the extracts of these 7 wastes were mutagenic; extracts of 2 additional wastes also were mutagenic. In addition, 10 of the crude wastes were administered by gavage to F-344 rats, and 24-h urine samples were collected. Of the 10 raw urines evaluated, 3 were mutagenic in strain TA98 in the presence of S9 and beta-glucuronidase. The 3 crude wastes that produced these 3 mutagenic urines were, themselves, mutagenic. Adequate volumes of 6 of the 10 raw urines were available for extraction/concentration. These 6 urines were incubated with beta-glucuronidase and eluted through Sep-Pak C18 columns; the methanol eluates of 3 of the urines were mutagenic, and these were the same 3 whose raw urines also were mutagenic. In general, the C18/methanol extraction procedure reduced the cytotoxicity and increased the mutagenic potency of the urines. To our knowledge, this is the first report of the mutagenicity of urine from rodents exposed to hazardous wastes. Based on the present results, the use of only strain TA98 in the presence of S9 might be adequate for general screening of hazardous wastes or waste extracts for genotoxicity. The urinary mutagenesis assay does not appear to be a useful adjunct to the Salmonella assay for screening hazardous wastes. The problems associated with chemically fractionating diverse types of hazardous wastes for bioassay are also discussed.     

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.     

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.     

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.     

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.     

The presence of the mutagenic polycyclic aromatic hydrocarbons benzo[a]pyrene and benz[a]anthracene in creosote P1

Several fractions of creosote P1 separated by TLC showed mutagenicity towards Salmonella typhimurium TA98. Thus mutagenicity is probably caused by the presence of mutagenic aromatic hydrocarbons. The mutagenic polycyclic aromatic hydrocarbons, benzo[a]pyrene and benz[a]anthracene, were detected in concentrations of 0.18 and 1.1% respectively. Because these compounds are probably not essential for the wood-preserving properties of creosote , a more selective composition of the product should be considered.     

Comparison of the mutagenic activity of XAD4 and blue rayon extracts of surface water and related drinking water samples

The combination of mutagenicity tests and selective extraction methodologies can be useful to indicate the possible classes of genotoxic organic contaminants in water samples. Treated and source water samples from two sites were analyzed: a river under the influence of an azo dye-processing plant discharge and a reservoir not directly impacted with industrial discharges, but contaminated with untreated domestic sewage. Organic extraction was performed in columns packed with XAD4 resin, that adsorbs a broad class of mutagenic compounds like polycyclic aromatic hydrocarbons (PAHs), arylamines, nitrocompounds, quinolines, antraquinones, etc., including the halogenated disinfection by-products; and with blue rayon that selectively adsorbs polycyclic planar structures. The organic extracts were tested for mutagenicity with the Salmonella assay using TA98 and TA100 strains and the potencies were compared. A protocol for cleaning the blue rayon fibers was developed and the efficiency of the reused fibers was analyzed with spiked samples. For the river water samples under the influence of the azo-type dye-processing plant, the mutagenicity was much higher for both blue rayon and XAD4 extracts when compared to the water from the reservoir not directly impacted with industrial discharges. For the drinking water samples, although both sites showed mutagenic responses with XAD4, only samples from the site under the influence of the industrial discharge showed mutagenic activity with the blue rayon extraction, suggesting the presence of polycyclic compounds in those samples. As expected, negative results were found with the blue rayon extracts of the drinking water collected from the reservoir not contaminated with industrial discharges. In this case, it appears that using the blue rayon to extract drinking water samples and comparing the results with the XAD resin extracts we were able to distinguish the mutagenicity caused by industrial contaminants from the halogenated disinfection by-products generated during water treatment.