Screening complex hazardous wastes for mutagenic activity using a modified version of the TLC/Salmonella assay

10 complex hazardous wastes were tested for mutagenic activity using a modified version of the TLC/Salmonella assay developed by Bj?rseth et al. (1982). This fractionation/bioassay scheme couples thin-layer chromatography (TLC) with the Salmonella/mammalian-microsome (Ames) assay for the detection of mutagenic constituents in complex mixtures. Crude (unadulterated) hazardous wastes and selected hazardous waste extracts were fractionated on commercially available cellulose TLC plates. Mutagenicity testing was performed in situ by applying a single overlay of minimal growth agar, tester strain TA98 or TA100, and the optional metabolic activation system directly onto the developed chromatogram. A mutagenic effect was indicated either by the appearance of localized clusters of revertant colonies or by an increase in total revertant growth vis-à-vis control plates. 7 of 10 hazardous wastes (including tars, emulsions, sludges, and spent acids and caustics) demonstrated mutagenic activity when tested by this method. To assess the sensitivity of the modified TLC/Salmonella assay, 14 Salmonella mutagens from a wide range of chemical classes and polarities were tested. Selected compounds included heterocyclics, aromatic amines, alkylating agents, antitumor agents, a nitrosamine and a nitroaromatic. 11 of the 14 mutagens were positive in this test system. The 3 compounds refractory to analysis included a polycyclic aromatic hydrocarbon and two volatiles.     

Genotoxic effects and chemical compositions of four creosotes.

Four creosotes used in Finland for impregnating wood were tested in the Ames Salmonella test, the SCE test and the SOS chromotest. Compounds volatile at 37 degrees C were assayed using the taped plate testing protocol. The creosotes were fractionated according to their natural boiling ranges and the fractions were tested in the Ames Salmonella assay. Chemical compositions of creosotes and fractions were determined by high resolution gas chromatography/mass spectrophotometry techniques and by reversed phase high performance liquid chromatography. Mutagenic activities were shown to reside in fractions having the highest boiling point ranges (greater than 290 degrees C). The concentrations of mutagenic polycyclic aromatic hydrocarbons in creosotes and in some of their corresponding distillation fractions, when compared with mutagenic activities, indicated synergistic or antagonistic interactions.     

Mutagenicity of the Alternaria metabolites altertoxins I, II, and III.

The Ames Salmonella typhimurium assay was used to demonstrate that an extract of the mold Alternaria alternata was mutagenic. The mutagenic extract was fractionated, and the Ames test was used to determine which fractions were mutagenic. Subsequently, altertoxins I and II and a new compound referred to as altertoxin III were isolated by liquid chromatography and shown to be hydroxyperylenequinone compounds by mass spectrometry and infrared, ultraviolet, and proton magnetic resonance spectroscopy. Altertoxins I, II, and III were mutagenic to S. typhimurium TA98, TA100, and TA1537 with and without metabolic activation.     

Mutagenic and clastogenic activity of direct-acting components from air pollutants of the Silesian industrial region

Sequential elution solvent chromatography (SESC) developed by Farcasiu for characterization of coal liquids was used for the fractionation of benzene extracts of airborne particulate pollutants. Mutagenic and clastogenic activity of SESC fractions was determined by the Salmonella/microsome test and the assay for V79 cell chromosomal aberrations (CAs), respectively. Five out of 8 obtained fractions showed differentiated, direct and indirect mutagenic activity. Selected ‘direct’ fractions, examined by the rodent cell chromosome aberration test, also gave a clastogenic response that increased with prolonged treatment time. The SESC system combined with 2 biological assays, the Ames test and the CAs test, seems to be a useful method for examination of genotoxic components of environmental pollutants.     

Mutagens formed from butylated hydroxyanisole treated with nitrite under acidic conditions

The reaction products from butylated hydroxyanisole treated with nitrite under acidic conditions were investigated for mutagenic activity in Salmonella typhimurium his reversion assay and for DNA-damaging activity using H17 Rec+ (wild) and M45 Rec- (recombinationless) of Bacillus subtilis. The chloroform extract of the reaction mixture showed 9 spots on thin-layer chromatography (TLC). Compounds from 2 spots on the TLC had high mutagenic activity in TA100 without S9 mix, with DNA-damaging activity. The 2 mutagens were then crystallized from the reaction mixture and identified to be 2-tert.-butyl-p-quinone (t-BQ) and the dimer of t-BQ; 3,3'-di-tert.-butyl-biphenyldiquinone-(2,5,2',5') (BBDQ), from their instrumental analysis. The mutagenic activities of t-BQ and BBDQ were determined by Ames test, and the induced mutation frequencies were about 1.9 X 10(-4) (t-BQ) and 8.3 X 10(-5) (BBDQ).     

Mutagenicity of the Alternaria metabolites altertoxins I, II, and III

The Ames Salmonella typhimurium assay was used to demonstrate that an extract of the mold Alternaria alternata was mutagenic. The mutagenic extract was fractionated, and the Ames test was used to determine which fractions were mutagenic. Subsequently, altertoxins I and II and a new compound referred to as altertoxin III were isolated by liquid chromatography and shown to be hydroxyperylenequinone compounds by mass spectrometry and infrared, ultraviolet, and proton magnetic resonance spectroscopy. Altertoxins I, II, and III were mutagenic to S. typhimurium TA98, TA100, and TA1537 with and without metabolic 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.     

The interaction of methanol, rat-liver S9 and the aromatic amine 2,4-diaminotoluene produces a new mutagenic compound

Methanol is a widely used solvent for organic compounds and a human toxicant. In our studies of the metabolism of aromatic amines in the Ames/Salmonella assay, we observed a rapid and quantitative conversion of the mutagenic and carcinogenic aromatic amine 2,4-diaminotoluene (2,4-DAT) to a single product. This product was only produced in the presence of methanol, and not other organic solvents. Isolation of this product showed that it was highly mutagenic in Salmonella TA98 with S9 activation. Characterization of the product of the interaction of methanol and 2,4-DAT indicated that methanol is activated to a reactive intermediate, probably formaldehyde, by the 9000 X g supernatant used in the Ames/Salmonella assay. The formaldehyde subsequently reacts with 2,4-DAT to form the mutagenic product, identified as bis-5,5'(2,4,2',4'-tetraaminotolyl)methane. Results of this study demonstrate that methanol may be an inappropriate solvent for mutation and metabolism studies of aromatic amines and possibly other chemicals, and that solvent-xenobiotic interactions may in some cases lead to the misinterpretation of results.     

The release of mutagens from airborne particles in the presence of physiological fluids

Airborne particulates collected indoors in residences and outdoors were extracted by soxhlet extraction and sonication with methanol. In a comparative study in which mutagenic activity was evaluated in the Salmonella typhimurium reversion assay both soxhlet extraction and sonication proved to be suitable extraction methods. First, the residue, obtained by sonication of loaded filters with methanol followed by evaporation to dryness (tar), was sonicated with newborn calf serum and lung lavage fluid from pigs. All serum extracts of the tar were mutagenic to Salmonella typhimurium TA98, and contained direct- and indirect-acting mutagens. However, the mutagenic activity recovered by serum was only about half of the total mutagenic activity of the tar. The other part of the mutagenic activity remained in the tar. Lung lavage fluid was only able to remove 5-10% of direct-acting mutagens from the tar of all samples. About 20% of indirect-acting mutagens from indoor air were recovered in lung lavage fluid, while the lung lavage fluid extract from outdoor air did not show indirect mutagenic activity. Second, mutagenic activity recovered by direct sonication of the filters with physiological fluids was comparable with the recovery obtained by sonication of the tar. However, after sonication of the filter with lung lavage fluid hardly any mutagenic activity remained on the filter, whereas after sonication of the tar a clear mutagenic activity was observed in the non-soluble residue.     

1-Hydroxypyrene as an indicator of the mutagenicity of coal tar after activation with human liver preparations

Liver S9 fractions were prepared from male Wistar rats, either non-induced or induced with Aroclor 1254 and from 5 human kidney transplant donors. The preparations were compared for their ability to metabolize the premutagens present in coal tar to mutagenic metabolites in the Salmonella mutagenicity assay towards strain TA98. Low levels of mutagenicity of coal tar were seen with human S9 preparations. The differences between the S9 mix of the 5 donors in capacity to activate premutagens were approximately 6-fold. The activation of coal tar by rat liver S9 preparations was higher than by the human S9 preparations. The metabolic conversion of pyrene in coal tar to 1-hydroxypyrene by the same human S9 preparations was determined in a parallel assay. 3 human preparations showed a high correlation between the formation of 1-hydroxypyrene and bioactivation of coal tar to mutagenic metabolites. The slope values of the individual regression lines were equal, suggesting that 1-hydroxypyrene is a good indicator for the activation of premutagens present in coal tar.     

Assessment of mutagenic activity of repeatedly used deep-frying fats

Mutagenic activity of repeatedly used deep-frying fats was evaluated in relation to chemical characteristics. Deep-frying fat samples were collected from local restaurants and snack bars after sensory indication of abuse. A total of 20 deep-frying fat samples and 2 unused control fat samples was tested. Fat samples were fractionated into non-polar and polar compounds by column chromatography. Amounts of polar compounds obtained ranged from 2% (by weight) for unused fat to 44% for used deep-frying fat. Levels of di- and polymeric triglycerides (DPTG) were determined using gel-permeation chromatography. DPTG concentrations of 13 used deep-frying fat samples exceeded the threshold level of 10% above which fats are rejected for use. In addition thiobarbituric acid-reactive substances (TBA-RS) were measured. Amounts of TBA-RS were just above detection levels for most fat samples. Five used fat samples, however, contained relatively high concentrations of TBA-RS, ranging from 82 to 177 nmoles malondialdehyde/g. Non-polar and polar fractions were screened for mutagenic activity using the Ames mutagenicity assay. Mutagenic activity was found predominantly in polar fractions at doses higher than 1 mg/plate in strains TA97, TA100 and TA104, variously with and without metabolic activation. The highest number of mutagenic samples was detected by strain TA97, which appeared to be most sensitive. Some samples exhibited toxic effects. Chromatography blanks, consisting of solvents processed according to the same procedures as used for fat samples, were not mutagenic. Mutagenic activity was also detected in polar material obtained from unused frying fat. Non-polar fractions of unused frying fats showed no mutagenicity. A frying experiment carried out under laboratory conditions indicated that during repeated and prolonged use of deep-frying fat mutagenic polar substances were formed. Fat samples taken after 20 and 40 h of frying contained increasing amounts of polar compounds. Mutagenic activity was highest after 20 h of frying but was slightly decreased after 40 h of frying. At this stage, however, mutagens also appeared in the non-polar fraction. Mutagenic activity of polar fractions of used deep-frying fats in strain TA97 was positively correlated with levels of TBA-RS, which may indicate the involvement of lipid oxidation products in mutagenicity of used deep-frying fats. No significant correlations were found with other chemical characteristics. In the process of deep-fat frying numerous degradation products are formed, which may include mutagenic heterocyclic amines and other pyrolysates.(ABSTRACT TRUNCATED AT 400 WORDS)     

Mutagenicity of tetrachloroethene in the Ames test--metabolic activation by conjugation with glutathione

The mutagenicity of tetrachloroethene (tetra) and its S conjugate, S-(1,2,2-trichlorovinyl)glutathione (TCVG) was investigated using a modified Ames preincubation assay. TCVG was a potent mutagen in presence of rat kidney particulate fractions containing high concentrations of gamma-glutamyl transpeptidase (GGT) and dipeptidases. Purified tetra was not mutagenic without exogenous metabolic activation or under conditions favoring oxidative metabolism. Preincubation of tetra with purified rat liver glutathione (GSH) S-transferases in presence of GSH and rat kidney fractions resulted in a time-dependent formation of TCVG as determined by (HPLC) analysis and in an unequivocal mutagenic response in the Ames test. Experiments with tetra in the isolated perfused rat liver demonstrated TCVG formation and its excretion with the bile; bile collected after the addition of tetra to the isolated perfused liver was unequivocally mutagenic in bacteria in the presence of kidney particulate fractions. The mutagenicity was reduced in all cases by the GGT inhibitor serine borate or the beta-lyase inhibitor aminooxyacetic acid. These results support the suggestion that cleavage of the GSH S conjugate formed from tetra by the enzymes of the mercapturic acid pathway and by beta-lyase may be involved in the nephrocarcinogenic effects of this haloalkene in rats.     

The dosing determines mutagenicity of hydrophobic compounds in the Ames II assay with metabolic transformation: Passive dosing versus solvent spiking

The Ames II bacterial mutagenicity assay is a new version of the standard Ames test for screening chemicals for genotoxic activity. However, the use of plastic micro-titer plates has drawbacks in the case of testing hydrophobic mutagens, since sorptive and other losses make it difficult to control and define the exposure concentrations, and they reduce availability for bacterial uptake or to the S9 enzymes. With passive dosing, a biocompatible polymer such as silicone is loaded with the test compound and acts as a partitioning source. It compensates for any losses and results in stable freely dissolved concentrations. Passive dosing using silicone O-rings was applied in the Ames II assay to measure PAH mutagenicity in strains TA98 and TAMix – a mixture of six different bacterial strains detecting six different base-pair substitutions – after metabolic activation by S9. Initially, 10 PAHs were tested with passive dosing from saturated O-rings, aiming at levels in the test medium close to aqueous solubility. Fluoranthene, pyrene and benzo(a)pyrene were mutagenic in both TA98 and TAMix, whereas benz(a)anthracene was mutagenic in TA98 only. The concentration-dependent mutagenic activity of benzo(a)pyrene was then compared for passive dosing and solvent spiking. With spiking, nominal concentrations greatly exceeded aqueous solubility before mutagenicity was observed, due to sorptive losses and limiting dissolution kinetics. In contrast, the passive dosing concentration-response curves were more reproducible, and shifted towards lower concentrations by several orders of magnitude. This study raises fundamental questions about how to introduce hydrophobic test substances in the Ames II assay with biotransformation, since the measured mutagenicity not only depends on the compound potency but also on its supply, sorption and consumption during the assay.     

Genotoxicity of six pesticides by Salmonella mutagenicity test and SOS chromotest

Two in vitro tests (Ames test and SOS chromotest), one for bacterial mutagenicity and one for primary DNA damage, were assayed to determine the genotoxic activity of 6 pesticides (atrazine, captafol, captan, chlorpyrifosmethyl, molinate and tetrachlorvinphos). Assays were carried out both in the absence and presence of S9 fractions of liver homogenate from rat (Sprague–Dawley) pretreated with Aroclor 1254. Captan and captafol were genotoxic on both the Ames test and the SOS chromotest. Comparisons with mutagenesis data in Salmonella indicated that the SOS assay detected as genotoxic the pesticides that were mutagenic on the Salmonella test. Non-genotoxic effects were not detected in vitro either in the Salmonella/microsome assay nor in the SOS chromotest when bacterial tester strains were exposed to atrazine, molinate, chlorpyrifosmethyl and tetrachlorvinphos in the absence or presence of S9 mix.     

Seasonal variations in mutagenic activity of air pollutants at an industrial district of Silesia

Organic material from airborne particulate pollutants collected over a 7-month period at a highly industrialized region in Silesia (Poland) was tested for mutagenicity using the Ames test. Sequential elution solvent chromatography (SESC) was used for the separation of crude benzene extracts. Five out of 8 fractions showed mutagenic activity with differential direct and indirect responses. The mutagenicity of each active fraction was tested during the whole sampling period (from August to February 1984/1985) and seasonal variations were observed. All of the fractions, except fraction 3, showed only quantitative distinctions in mutagenic potential, expressed as a number of revertants per m3 of air. Over a period of 7 months, a steady increase of activity of fractions 2 and 4 was observed but the type of mutagenic response, indirect and direct respectively, remained unchanged in the summer and winter months. Fraction 3 (the most abundant component, probably containing polar derivatives of PAHs and heterocyclics) differed quantitatively and qualitatively between summer and winter time. From August to December samples showed enhanced mutagenic potency upon addition of rat liver microsomal enzymes, whereas in January a 4-5-fold increase in direct response was noted. This significant increase in direct mutagenic activity was accompanied by a considerable decrease in mean air temperature and resulted most probably from the intensive use of coal for domestic heating.     

Mutagenicity of tetrachloroethene in the ames test—metabolic activation by conjugation with glutathione

The mutagenicity of tetrachloroethene (tetra) and its S conjugate, S-(1,2,2-trichlorovinyl)glutathione (TCVG) was investigated using a modified Ames preincubation assay. TCVG was a potent mutagen in presence of rat kidney particulate fractions containing high concentrations of γ-glutamyl transpeptidase (GGT) and dipeptidases. Purified tetra was not mutagenic without exogenous metabolic activation or under conditions favoring oxidative metabolism. Preincubation of tetra with purified rat liver glutathione (GSH) S-transferases in presence of GSH and rat kidney fractions resulted in a time-dependent formation of TCVG as determined by (HPLC) analysis and in an unequivocal mutagenic response in the Ames test. Experiments with tetra in the isolated perfused rat liver demonstrated TCVG formation and its excretion with the bile; bile collected after the addition of tetra to the isolated perfused liver was unequivocally mutagenic in bacteria in the presence of kidney particulate fractions. The mutagenicity was reduced in all cases by the GGT inhibitor serine borate or the β-lyase inhibitor aminooxyacetic acid. These results support the suggestion that cleavage of the GSH S conjugate formed from tetra by the enzymes of the mercapturic acid pathway and by β-lyase may be involved in the nephrocarcinogenic effects of this haloalkene in rats.     

Isolation and taxonomic affiliation of N-heterocyclic aromatic hydrocarbon-transforming bacteria

The azaarenes (nitrogen-containing heterocyclic aromatic hydrocarbons) are products of incomplete combustion processes and thus are widely distributed with tar and oil products in the environment. Despite their adverse organoleptic, toxic, and carcinogenic characteristics, the biodegradability and fate of multi-ring azaarenes have received little attention. This work demonstrates the presence of genetically diverse azaarene-degrading bacteria in coal tar-contaminated soils. Thirty-eight bacterial strains able to transform the three-ring azaarenes, 5,6- and 7,8-benzoquinoline, phenanthridine, phenazine, or acridine, were isolated. Only seven of these strains grew in liquid medium on the specific azaarene compounds on which they were isolated using plates; and the rest transformed the azaarenes without growth. Taxonomic characterization by 16S ribosomal DNA sequencing revealed that our enrichment technique provided a diversity of 18 different azaarene-transforming bacterial species. Only a few strains were able to mineralize the homocyclic analogue, phenanthrene. Several of the isolates, e.g., Dyadobacter fermentans, Methylopila capsulata, and Agrobacterium tumefaciens, were related to genera relatively unknown with respect to the biodegradation of xenobiotic compounds. These strains can provide further information on the fate of azaarenes in the environment.     

Monitoring airborne genotoxicants in the rubber industry using genotoxicity tests and chemical analyses

This research was designed to examine the presence of mutagenic/carcinogenic compounds in airborne pollutants in the rubber industry using an integrated chemical/biological approach. Inhalable airborne particulate matter (PM-10: <10 microm) was collected in four rubber factories using a high-volume sampler equipped with a cascade impactor for particle fractionation. The organic extracts of two different fractions (0.5-10 microm and <0.5 microm) were examined for mutagenicity with the Ames test and for in vitro DNA-damaging activity in human leukocytes by single-cell microgel electrophoresis (Comet assay). The extracts were also studied by gas chromatography/mass spectrometry (GC/MS) for polycyclic aromatic hydrocarbon (PAH) content. Nitrosamines in ambient air were sampled on cartridges and analysed by GC with a thermal energy analyser (TEA) detector. Airborne volatile genotoxins were monitored in situ using a clastogenicity plant test (Tradescantia/micronuclei test). The results showed that airborne particulates were mainly very fine (<0.5 microm) and that trace amounts of genotoxic nitrosamines (N-nitrosodimethylamine: 0.10-0.98 microg/m(3); N-nitrosomorpholine: 0.77-2.40 microg/m(3)) and PAH (total PAH: 0.34-11.35 microg/m(3)) were present in air samples. Some extracts, particularly those obtained from the finest fractions, were mutagenic with the Ames test and genotoxic with the Comet assay. In situ monitoring of volatile mutagens using the Tradescantia/micronuclei test gave positive results in two working environments. The results showed the applicability of this integrated chemical-biological approach for detecting volatile and non-volatile genotoxins and for monitoring genotoxic hazards in the rubber industry.     

The assessment of the mutagenic potential of vehicle engine exhaust in the Ames Salmonella assay using a direct exposure method

A method for the assessment of the mutagenic activity of vehicle engine exhaust in the Ames assay is described in which the bacterial strains used (TA98 and TA98/DNP) are exposed to the freshly produced engine exhaust using a "Cassella' slit sampler. The method is found to be effective both in the presence and absence of metabolic activation, using Aroclor-1254-induced rat liver S9 fractions. A comparison is made between the direct exposure method and the standard methods involving the collection of particulate samples on glass fibre filters and the testing of various extracts of these samples. Possible uses of the direct exposure testing method are suggested and the effect of sampling techniques on the results obtained in the Ames assay is also discussed.     

In vitro mutagenicity and metabolism of the cycloaliphatic epoxy Cyracure UVR 6105

Cyracure UVR 6105 is a cycloaliphatic epoxy monomer and has both carboxylate and epoxy groups, with the potential for rapid polymerization. It is widely used in industry for the preparation of inks, resins, coatings, and was proposed for incorporation into dental composites. The objective of this study was to determine the mutagenic potential of this chemical related to its metabolite products. Several doses of Cyracure UVR 6105 were dissolved in DMSO and subjected to the Ames Salmonella mutagenicity assay. A metabolic activation system (S9-mix) was used consisting of Arochlor-induced liver S9 homogenate enriched with NADP and glucose-6-phosphate cofactors. In contrast to studies without S9-mix, Cyracure UVR 6105 exhibited enhanced genotoxic activities with strains TA100 and TA1535 in the presence of liver S9-mix. From in vitro metabolism of Cyracure UVR 6105 with S9-mix, as used in the Ames assay, several metabolites were identified. The alcohol metabolite, 3,4-epoxycyclohexylmethanol, containing intact epoxy group was identified in the organic solvent extract. This metabolite was synthesized and proved to be mutagenic against TA100 when assayed in the presence and absence of S9-mix. Results showed that the increased mutagenicity of Cyracure UVR-6105 in the presence of liver enzymes is due to the formation of the mutagenic metabolite 3,4-epoxycyclohexylmethanol.