Evaluation of hexamethylphosphoramide for gene mutations in Salmonella typhimurium using plate incorporation, preincubation, and suspension assays

Hexamethylphosphoramide (HMPA), a potent rat nasal carcinogen by inhalation, and three of its metabolites, pentamethylphosphoramide (PMPA), trimethylphosphoramide (TriMPA), and formaldehyde (HCHO), were assessed in Salmonella typhimurium gene mutation assays using various protocols, including plate incorporation, preincubation and suspension assays. HMPA (tested up to 15 000 μg/plate) was not mutagenic in plate incorporation or preincubation assays with or without metabolic activation. HCHO was mutagenic in the plate incorporation and preincubation assays (tested up to 150 μg/plate). In suspension assays, however, HMPA (tested up to 40 mg/ml), PMPA (up to 44 mg/ml) and HCHO (up to 45 μg/ml), but not TriMPA (up to 29 mg/ml), were mutagenic. HMPA and PMPA were positive only with activation. HMPA's mutagenicity was optimized using a relatively high level of rat liver S9 protein (3.5 mg/plate) in the metabolic activation mixture. Semicarbazide, an HCHO trapping agent, added at concentrations up to 167 μg/ml, markedly inhibited the mutagenic activities of HMPA and PMPA suggesting that HCHO generation may play a role in their mutagenicity. These studies show that HMPA is mutagenic in a modified Salmonella typhimurium reverse mutation assay with metabolic activation. Successive N-demethylation of HMPA eventually eliminates the mutagenic activity which further suggests that HMPA's mutagenic activity is related to the release of HCHO.     

Influence of inhibition of the metabolic activation on the mutagenicity of some nitrosamines, triazenes, hydrazines and seniciphylline in Drosophila melanogaster

It is determined to what extent certain inhibitors of the xenobiotic metabolizing enzyme systems have an influence on the mutagenicity of various pro-mutagens in Drosophila. 1-Phenylimidazole (PhI) is used as an inhibitor of the cytochrome P-450 (P-450) mediated monooxygenase activities. Iproniazid (Ipr) is a typical monoamine oxidase (MAO) inhibitor which as well seems capable of inhibiting to a certain extent P-450 mediated metabolism. N, N-Dimethyl benzylamine (N, N-DMB) is used as a competitive substrate for the N-oxidizing flavin-containing dimethylaniline monooxygenase (FDMAM). The enzyme-inhibiting activities of PhI and Ipr were determined in vitro using microsomes obtained from Drosophila larvae and adults. Both compounds were capable of inhibiting benzo[a]pyrene (BP) hydroxylation and p-nitroanisole (p-NA) demethylation, although for Ipr 100-fold higher concentrations were required compared to PhI. As model-mutagens were used: the nitrosamines dimethylnitrosamine (DMN) and diethylnitrosamine (DEN), the triazenes 1-(2,4,6-trichlorophenyl)-3,3-dimethyltriazene (Cl3PDMT), 1-(3-pyridyl)-3,3-dimethyltriazene (PyDMT) and dacarbazine (DTIC), the hydrazines procarbazine (PCZ), 1,1-dimethylhydrazine (1,1-DMH) and 1,2-dimethylhydrazine (1,2-DMH) as well as the pyrrolizidine alkaloid seniciphylline (SPh). Simultaneous or pretreatment with Ipr results in a clear decrease of the mutagenicity of Cl3PDMT, while PhI pretreatment leads to an increased mutagenicity. This indicates that these two inhibitors do not inhibit the same enzyme or isozyme. For SPh too, Ipr pretreatment results in some decrease of the mutagenicity. This is in contrast to DEN, where the activation is clearly inhibited by PhI while Ipr has only a minor effect. For DMN, DTIC and PCZ both Ipr and PhI pretreatment caused considerable decreases of the mutagenicity. Inhibition of the FDMAM catalyzed activity by N,N-DMB resulted in an increase of mutagenicity with Cl3PDMT, in a moderate decrease of mutagenicity with DTIC, and a marked decrease with DMN, which was strongly inhibited. In contrast to the clear-cut mutagenicity of PCZ, 1,1-DMH and 1,2-DMH are not mutagenic in Drosophila. No change was observed upon inhibition of the various metabolizing activities. Apart from using strain differences in metabolizing activities and enzyme induction, enzyme inhibition can also be used to determine the influence of metabolism on the in vivo mutagenicity of promutagens in Drosophila.     

Influence of metabolic factors on the mutagenic effectiveness of cyclophosphamide in Drosophila melanogaster

This paper describes the influence of changes in metabolic activity on the in-vivo mutagenic effectiveness of cyclophosphamide in Drosophila melanogaster. A dose-dependent increase in mutagenicity was observed until a plateau value is reached which was increased only slightly after enzyme induction with Aroclor 1254, whereas induction with phenobarbital resulted in a decrease, especially when cyclophosphamide was applied by injection. Treatment of the adult males with inhibitors of the monoamine oxidase (MAO, EC 1.4.3.4), such as iproniazid (Ipr), benzimidazole or tryptamine, led to a marked increase of the mutagenic effectiveness of cyclophosphamide especially in spermatocytes. This indicates the importance of metabolic de-activation processes for the limited mutagenicity of cyclophosphamide in Drosophila. The principal active metabolite of cyclophosphamide, phosphoramide mustard, is extensively de-activated by enzymes that can be inhibited by 1-phenylimidazole (PhI), presumably cytochrome P-450 (EC 1.14.14.1), but not by those blocked by MAO inhibitors. Inhibition of the FAD-containing dimethylaniline monooxygenase (FDMAM, EC 1.14.13.8) by N,N-dimethylbenzylamine (N,N-DMB) resulted in some increase in cyclophosphamide mutagenicity only in spermatids. The marginal mutagenicity of cyclophosphamide in Drosophila larvae could not be increased either by cytochrome P-450 induction with phenobarbital or by MAO inhibition with Ipr. In contrast to the failure of cyclophosphamide to induce rod-chromosome loss, a considerable activity was found when a ring-shaped chromosome was used. Similar to the sex-linked recessive lethal (SLRL) test, ring-X loss frequency could be enhanced by simultaneous treatment with MAO inhibitors. The observed ring-X loss frequency declined when males treated with cyclophosphamide were mated to DNA-repair deficient mei-9L1 females. Cyclophosphamide produces chromosome breaks, detected as 2-3 translocations, in Drosophila spermatocytes, the stage in spermatogenesis that is also the most sensitive to the induction of SLRL mutations.     

Microbial mutagenicity of selected hydrazines

Selected hydrazines and related compounds were examined for their mutagenic activity in S. typhimurium strains TA1535 and TA1537. These in vitro assays were conducted with and without metabolic activation by Aroclor-induced rat-liver enzymes. Relatively high levels of mutagenicity were observed with phenylhydrazine X HCl, methylhydrazine, N'-acetyl-4-(hydroxymethyl)phenylhydrazine, and 4-(hydroxymethyl)benzenediazonium tetrafluoroborate, the stabilized salt of a carcinogenic metabolite of agaritine; only low levels of mutagenicity were observed with other compounds, although most are strong carcinogens. Several of the compounds were highly toxic to the bacteria, and detection of mutagenicity was enhanced by calculating the increase in mutagenic activity on the basis of the surviving fractions of bacteria.     

Genotoxic activity of 1,3-butadiene and nitrogen dioxide and their photochemical reaction products in Drosophila and in the mouse bone marrow micronucleus assay.

The genotoxic activity of a photochemical reaction mixture of 1,3-butadiene and nitrogen dioxide was investigated in vivo in the mouse bone marrow micronucleus assay and the somatic mutation and recombination test in Drosophila (the wing spot test). Butadiene alone was not mutagenic in Drosophila, but induced micronuclei in mice at 10 ppm after 23 h of exposure. Nitrogen dioxide was not genotoxic in either test system. The photochemical reaction products were toxic but probably not mutagenic in Drosophila and not genotoxic in mouse bone marrow. The in vivo results do not confirm earlier in vitro results that demonstrated a strong direct-acting mutagenic activity of the photochemical products in Salmonella.     

Mutagenicity of chloro-olefins in the Salmonella/mammalian microsome test. I. Allyl chloride mutagenicity re-examined

Contrary to findings published up to now, allyl chloride, a well known directly acting mutagen for Salmonella typhimurium, is efficiently activated by rat-liver homogenate (S9 mix) under non-standard mutagenicity testing conditions. Its indirect, S9-mediated mutagenic activity is greatly enhanced when longer than standard preincubation times are applied. The indirect mutagenicity of allyl chloride, thus revealed, greatly exceeds its direct mutagenic activity. Obviously, standard mutagenicity testing conditions cannot be regarded as reliable tools for the evaluation of the full genotoxic potential of allyl chloride and, possibly, of other related compounds.     

Genotoxicity of naturally occurring hydroxyanthraquinones

A variety of structurally related hydroxyanthraquinones (HA) were investigated in a test battery for the evaluation of mutagenicity and cell-transforming activity. The tests were: (1) the Salmonella typhimurium mutagenicity assay, (2) the V79-HGPRT mutagenicity assay, (3) the DNA-repair induction assay in primary rat hepatocytes and (4) the in vitro transformation of C3H/M2 mouse fibroblasts. In Salmonella, most of the tested compounds were mutagenic in strain TA1537, but only a few were active in other strains. Among these were HA with a hydroxymethyl group, such as lucidin and aloe-emodin. In V79 cells, only HA with 2 hydroxy groups in the 1,3 positions (1,3-DHA, purpurin, emodin) or with a hydroxymethyl sidechain (lucidin and aloe-emodin) were mutagenic. The compounds found to be active in V79 cells were also active in the DNA-repair assay and in the C3H/M2 transformation assay. Thus, it appears that the genotoxicity of HA is dependent on certain structural requirements.     

Genotoxic and mutagenic activity of environmental air samples from different rural, urban and industrial sites in Flanders, Belgium

The present study reports mutagenic and genotoxic activities associated with ambient air collected at 15 sites characteristic for urban, industrial or rural conditions in Flanders. Airborne particulates (PM10) and semi-volatile compounds were collected on quartz filters (QF) and polyurethane foam (PUF) cartridges using a high-volume sampling device. The mutagenic and genotoxic potency of the organic extracts--Soxhlet extraction with acetone--was determined by use of the Salmonella mutagenicity standard plate-incorporation assay and the Vitotox assay, respectively. Concentrations of 16 polycyclic aromatic hydrocarbons (PAHs) in the extracts were determined by reversed-phase high-performance liquid chromatography (HPLC). Ambient air samples contained significant PAH levels and mutagenic activities at all 15 sites: direct mutagenicity of up to 47 revertants per cubic meter was found in the QF extracts and more limited activity of up to 11 rev m(-3) in the PUF extracts. Metabolic activation of PUF extracts resulted in an important increase in mutagenic activity, up to 30 rev m(-3), but no such increase was observed for QF extracts. The highest values were observed outside large cities at industrial sites and at a rural site contaminated by pollution from a chemical plant at a distance of 4 km. Also at the background location near the North Sea a significant mutagenic activity was measured in the QF extracts (+S9: 9 rev m(-3); -S9: 7 rev m(-3)). Apparently, there is in Flanders a significant background exposure level to airborne mutagenicity, even in areas with limited or no nearby pollution sources. Based on the concentrations of 10 mutagenic PAHs and supposing additivity of their specific mutagenicities, only a few percent (mean 3%) of the observed indirect mutagenic activity could be explained. This implies that most mutagenic activity originated from other substances that were not identified or measured in our chemical analysis. This underscores the importance of bio-monitoring measurements.     

Mutagenic exposure in the rubber manufacturing industry: an industry wide survey

Mutagenic exposure conditions in several rubber manufacturing companies (n=9) in The Netherlands were studied. Mutagenicity of total suspended particulate matter in air (TSPM) and of wipe samples from possible contact surfaces were measured in the Ames mutagenicity assay with Salmonella typhimurium YG1041 in the presence of a metabolic activation system. Large differences in median mutagenicity of TSPM samples were observed between companies (range 49-1056rev/m(3)) and to a lesser extent between production functions (range 129-402rev/m(3)). The production function curing revealed overall the highest TSPM mutagenicity levels. Forty-one percent of the surface wipe samples revealed mutagenic activity ranging from 26 to 665rev/cm(2). Mixing had the largest proportion of positive samples resulting in a median surface mutagenic contamination of 39rev/cm(2). Surface mutagenic contamination, averaged per department/company combination, showed only a weak correlation with TSPM mutagenicity (r=0.28, P=0.05). Company, production function and total soluble matter (e.g. mass collected upon extraction with organic solvents with different polarity) explained 79 and 81% of the variability in mutagenicity of TSPM and surface contamination levels, respectively. "Company" was identified as the most important exposure determinant for mutagenic activity in TSPM and surface wipe samples. This indicates the importance of company specific determinants like production volume and rubber chemicals used for the encountered mutagenic exposure conditions. Detection of substantial mutagenic activity on possible contact surfaces supports furthermore the potential importance of the dermal route in the uptake of genotoxic compounds of workers in the rubber manufacturing industry.     

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.     

Mutagenicity of four hair dyes in Drosophila melanogaster.

The hair dye constituents p-phenylenediamine, 2,4-diaminoanisole sulfate, 2,4-diaminotoluene and 4-nitro-0-phenylenediamine were tested for mutagenicity in Drosophila melanogaster. The compounds were given orally to adult males. The induction of sex-linked recessive lethal mutation was used as a measure of mutagenicity. All four of the dyes tested were mutagenic with a peak mutagenic activity in metabolically active germ cells (spermatids and spermatocytes).     

Quantitative comparative mutagenesis in bacteria, mammalian cells, and animal-mediated assays A convenient way of estimating genotoxic activity in vivo?

The accumulation of environmental compounds which exhibit genotoxic properties in short-term assays and the increasing lag of time for obtaining confirmation or not in long-term animal mutagenicity and carcinogenicity tests, makes it necessary to develop alternative, rapid methodologies for estimating genotoxic activity in vivo. In the experimental approach used here, it was assumed that the genotoxic activity of foreign compounds in animals, and ultimately humans, is determined among others by exposure level, organ distribution of (DNA) dose, and genotoxic potency per unit of dose, and that knowledge about these 3 parameters may allow to rapidly determine the expected degree of genotoxicity in various organs of exposed animals. In view of the high degree of qualitative correlation between mutagenic activity of chemicals in bacteria and in cultured mammalian cells, and their mutagenic and carcinogenic properties in animals, and in order to be able to distinguish whether mutagenic potency differences were due to differences in (DNA) dose rather than other physiological factors, the results of mutagenicity tests obtained in the present experiments using bacteria and mammalian cells were compared on the basis of DNA dose rather than exposure concentrations, with the following questions in mind: Is there an absolute or a relative correlation between the mutagenic potencies of various ethylating agents in bacteria (E. coli K12) and in mammalian cells (V79 Chinese hamster) after treatment in standardized experiments, and can specific DNA adducts be made responsible for mutagenicity? Is the order of mutagenic potency of various ethylating agents observed in bacteria in vitro representative of the ranking of mutagenic potency found in vivo? Since the answer to this last question was negative, a further question addressed to was whether short-term in vivo assays could be developed for a rapid determination of the presence (and persistence) of genotoxic factors in various organs of mice treated with chemicals. In quantitative comparative mutagenesis experiments using E. coli K12 and Chinese hamster cells treated under standardized conditions in vitro with 5 ethylating agents, there was no indication of an absolute correlation between the number of induced mutants per unit of dose in the bacteria and the mammalian cells. The ranking of mutagenic potency was, however, identical in bacteria and mammalian cells, namely, ENNG greater than ENU greater than or equal to DES greater than DEN congruent to EMS, the mutagenic activity of DEN being dependent on the presence of mammalian liver preparations.(ABSTRACT TRUNCATED AT 400 WORDS)     

Mutagens in contaminated soil: a review

The intentional and accidental discharges of toxic pollutants into the lithosphere results in soil contamination. In some cases (e.g., wood preserving wastes, coal-tar, airborne combustion by-products), the contaminated soil constitutes a genotoxic hazard. This work is a comprehensive review of published information on soil mutagenicity. In total, 1312 assessments of genotoxic activity from 118 works were examined. The majority of the assessments (37.6%) employed the Salmonella mutagenicity test with strains TA98 and/or TA100. An additional 37.6% of the assessments employed a variety of plant species (e.g., Tradescantia clone 4430, Vicia faba, Zea mays, Allium cepa) to assess mutagenic activity. The compiled data on Salmonella mutagenicity indicates significant differences (p<0.0001) in mean potency (revertents per gram dry weight) between industrial, urban, and rural/agricultural sites. Additional analyses showed significant empirical relationships between S9-activated TA98 mutagenicity and soil polycyclic aromatic hydrocarbon (PAH) concentration (r2=0.19 to 0.25, p<0.0001), and between direct-acting TA98 mutagenicity and soil dinitropyrene (DNP) concentration (r2=0.87, p<0.0001). The plant assay data revealed excellent response ranges and significant differences between heavily contaminated, industrial, rural/agricultural, and reference sites, for the anaphase aberration in Allium cepa (direct soil contact) and the waxy locus mutation assay in Zea mays (direct soil contact). The Tradescantia assays appeared to be less responsive, particularly for exposures to aqueous soil leachates. Additional data analyses showed empirical relationships between anaphase aberrations in Allium, or mutations in Arabidopsis, and the 137Cs contamination of soils. Induction of micronuclei in Tradescantia is significantly related to the soil concentration of several metals (e.g., Sb, Cu, Cr, As, Pb, Cd, Ni, Zn). Review of published remediation exercises showed effective removal of genotoxic petrochemical wastes within one year. Remediation of more refractory genotoxic material (e.g., explosives, creosote) frequently showed increases in mutagenic hazard that remained for extended periods. Despite substantial contamination and mutagenic hazards, the risk of adverse effect (e.g., mutation, cancer) in humans or terrestrial biota is difficult to quantify.     

Principles of covalent binding of reactive metabolites and examples of activation of bis-electrophiles by conjugation

Mechanisms of toxicity continue to be important in developing rational strategies to deal with chemicals present in the environment. Understanding and predicting toxicity have also become a critical step in the process of drug development. Covalent binding of chemicals to macromolecules is one aspect of toxicity, and the principles and outcomes of the process are considered. Two examples of chemicals for which several aspects of metabolism and reactions are understood are aflatoxin B(1) and polyhalogenated olefins. Ethylene dibromide is a compound that is activated to genotoxic half-mustards by conjugation with glutathione or the DNA repair protein O(6)-alkylguanine DNA alkyltransferase (AGT). The AGT reaction is unusual, in that crosslinking of the protein to DNA increases mutagenicity. One of the involved mechanisms is formation of N(7)-guanyl crosslinks and depurination to produce G-->T transversions; other reactions appear to yield the additional mutagenic events. The phenomenon of thiol conjugation to increase mutagenicity is widespread among bis-electrophiles.     

Genotoxic activity of organic chemicals in drinking water

The information summarized in this review provides substantial evidence for the widespread presence of genotoxins in drinking water. In many, if not most cases, the genotoxic activity can be directly attributed to the chlorination stage of drinking water treatment. The genotoxic activity appears to originate primarily from reactions of chlorine with humic substances in the source waters. Genotoxic activity in drinking water concentrates has been most frequently demonstrated using bacterial mutagenicity tests but results with mammalian cell assay systems are generally consistent with the findings from the bacterial assays. There is currently no evidence for genotoxic damage following in vivo exposures to animals. In some locations genotoxic contaminants of probable industrial and/or agricultural origin occur in the source waters and contribute substantially to the genotoxic activity of finished drinking waters. The method used for sample concentration can have an important bearing on study results. In particular, organic acids account for most of the mutagenicity of chlorinated drinking water, and their recovery from water requires a sample acidification step prior to extraction or XAD resin adsorption. Considerable work has been done to determine the identity of the compounds responsible for the mutagenicity of organic concentrates of drinking water. Recently, one class of acidic compounds, the chlorinated hydroxyfuranones, has been shown to be responsible for a major part of the mutagenic activity. Strategies for drinking water treatment that have been evaluated with respect to reduction of genotoxins in drinking water include granular activated carbon (GAC) filtration, chemical destruction, and the use of alternative means of treatment (i.e., ozone, chlorine dioxide, and monochloramine). GAC treatment has been found to be effective for removal of mutagens from drinking water even after the GAC is beyond its normal use for organic carbon removal. All disinfectant chemicals appear to have the capacity of forming mutagenic chemicals during water treatment. However, the levels of mutagenicity formed with the alternative disinfectants have been generally less than those seen with chlorine and, especially in the case of ozone, highly dependent on the source water.(ABSTRACT TRUNCATED AT 400 WORDS)     

Activation of mutagens by hepatocytes and liver 9000 X g supernatant from human origin in the Salmonella typhimurium mutagenicity assay. Comparison with rat liver preparations

The mutagenicity of 10 known genotoxic compounds, of several chemical classes, was measured in Salmonella typhimurium mutagenicity assays comprising isolated human hepatocytes or human liver 9000 X g supernatant (S9) from 4 different individuals, as activating system. The mutagenic activity of several compounds as determined with the Salmonella/hepatocyte suspension assay showed obvious differences when compared with the values obtained in the Salmonella/S9 plate assay. For instance, the mutagenic activity of BZ, DMN and DEN appeared to be much higher in the hepatocyte assay than in the S9 assay. However, 2-AF and 2-AAF were activated more effectively into mutagens in the S9 assay than in the hepatocyte assay. 2-AF was slightly more mutagenic than 2-AAF in the hepatocyte assay, whereas it was far more mutagenic than 2-AAF in the S9 assay. DMN was found more mutagenic than DEN in the hepatocyte assay, whereas in the S9 assay DEN appeared to be slightly more mutagenic. Furthermore, great interindividual differences in the metabolic activation of certain compounds, e.g. BZ and DMN, were observed in the hepatocyte suspension assay, whereas these variations were less evident in the S9 plate assay. Comparison of the mutagenicity data obtained with the human liver preparations, with those obtained with rat liver preparations, showed great interspecies differences in the capacity to activate certain chemicals into mutagens. The use of human liver preparations, in particular isolated human hepatocytes, may be of great value in studies on inter- and intraspecies variations in metabolic activation of genotoxic agents.     

Genotoxicity and mutagenicity of iron and copper in mice

The toxicity of trace metals is still incompletely understood. We have previously shown that a single oral dose of iron or copper induces genotoxic effects in mice in vivo, as detected by single cell gel electrophoresis (comet assay). Here, we report the effect of these metals on subchronic exposure. Mice were gavaged for six consecutive days with either water, 33.2 mg/kg iron, or 8.5 mg/kg copper. On the 7th day, the neutral and alkaline comet assays in whole blood and the bone marrow micronucleus (MN) test were used as genotoxicity and mutagenicity endpoints, respectively. Particle induced X-ray emission was used to determine liver levels of the metals. Females showed a slightly lower DNA damage background, but there was no significant difference between genders for any endpoint. Iron and copper were genotoxic and mutagenic. While copper was more genotoxic in the neutral version, iron was more genotoxic in the alkaline version of the comet assay. Copper induced the highest mutagenicity as evaluated by the MN test. Iron was not mutagenic to male mice. Iron is thought to induce more oxidative lesions than copper, which are primarily detected in the alkaline comet assay. Treatment with iron, but not with copper, induced a significant increase in the hepatic level of the respective metal, reflecting different excretion strategies.     

Differential mutagenic activity of IQ (2-amino-3-methylimidazo[4,5-f]quinoline) in Salmonella typhimurium strains in vitro and in vivo, in Drosophila, and in mice

IQ, a heterocyclic aromatic amine which is formed during the frying of meat, was prepared by chemical synthesis. Its genotoxic potential was studied in bacteria, Drosophila and in mice. A mutagenic effect of IQ (frameshift induction) was detected in Salmonella typhimurium in experiments without metabolic activation; this effect was several orders of magnitude lower than that observed in the presence of an activation system. Ames tests with liver-homogenate S9 fraction from PCB-induced mice and rats confirmed the high mutagenic potency of IQ metabolites (Kasai et al., 1980a). Comparative studies on diagnostic Salmonella strains revealed that the high frameshift-inducing activity is independent of the plasmid pkM101; it is, however, greatly reduced by an intact excision-repair system for DNA lesions. The mutagenic activity of the metabolite(s) formed in vitro by S9 mix has a half-life of ca. 14 min. In the fruit fly, Drosophila melanogaster, IQ induced when used at sublethal concentrations, X-chromosomal recessive lethal mutations in male germ cells in a dose-dependent manner. In mice, tests were performed to detect somatic mutations: chromosomal anomalies (micronuclei) in bone marrow, and gene mutations (affecting coat pigmentation) in mice exposed to IQ in utero. No genotoxic effects were observed in these assays. However, the formation of mutagenic metabolites in the liver of IQ-treated mice was unequivocally demonstrated in host-mediated assays using Salmonella as mutagen probes in mice. The data demonstrate genotoxic activity of IQ in prokaryotic and eukaryotic organisms. The possible reasons for the different response of mammalian systems in vivo and the Salmonella system are discussed.     

A negative test for mutagenic action of microwave radiation in Drosophila melanogaster.

Microwave radiation (2450 MHz CW) was tested for mutagenicity in Drosophila melanogaster. Embryos in water were exposed to the electromagnetic field with a mean specific absorption rate of 100 W/kg. A sensitive somatic test system was used, in which mutagenicity was measured as the frequency of somatic mutations for eye pigmentation. With the test system used, microwaves did not show any mutagenic activity.