Genotoxicity of pesticides: a review of human biomonitoring studies

Pesticides constitute a heterogeneous category of chemicals specifically designed for the control of pests, weeds or plant diseases. Pesticides have been considered potential chemical mutagens: experimental data revealed that various agrochemical ingredients possess mutagenic properties inducing mutations, chromosomal alterations or DNA damage. Biological monitoring provides a useful tool to estimate the genetic risk deriving from an integrated exposure to a complex mixture of chemicals. Studies available in scientific literature have essentially focused on cytogenetic end-points to evaluate the potential genotoxicity of pesticides in occupationally exposed populations, including pesticide manufacturing workers, pesticide applicators, floriculturists and farm workers. A positive association between occupational exposure to complex pesticide mixtures and the presence of chromosomal aberrations (CA), sister-chromatid exchanges (SCE) and micronuclei (MN) has been detected in the majority of the studies, although a number of these failed to detect cytogenetic damage. Conflicting results from cytogenetic studies reflect the heterogeneity of the groups studied with regard to chemicals used and exposure conditions. Genetic damage associated with pesticides occurs in human populations subject to high exposure levels due to intensive use, misuse or failure of control measures. The majority of studies on cytogenetic biomarkers in pesticide-exposed workers have indicated some dose-dependent effects, with increasing duration or intensity of exposure.Chromosomal damage induced by pesticides appears to have been transient in acute or discontinuous exposure, but cumulative in continuous exposure to complex agrochemical mixtures.Data available at present on the effect of genetic polymorphism on susceptibility to pesticides does not allow any conclusion.     

Actual problems of genetic toxicology

The review deals with current issues of genetic toxicology and aims to develop this science at the contemporary stage. We study general approaches to assessing the genotoxic and mutagenic activity of environmental factors; to constructing a regulatory system of chemical compounds that considers the mutagenic effect in Russia and abroad; and to determining modern methods for assessing the organ specificity of mutagens, alternative methods of genetic toxicology, the mutagenic action of various factors in the survey of population, and the abilities of toxicogenomics to identify the mutagenic properties of the environment.     

Prevention of the genetic consequences of using pesticides: the reality and the necessity

The system of genetic and hygienic evaluation of pesticide preparations requires improvements as there are many mutagens among widespread chemical means of plant protection. A successful solution of the problem of the environment protection from genetic consequences of pesticide application is possible if the hygienic regulation of the pesticide application will be based not only on the results of its experimental check, but also on the ecological and genetic studies. The latter are to include identification of the environmental mutagenic background and the level of mutagenic and genotypic variability in populations.     

Cytogenetic activity of metabolites of pesticides representing different classes of chemical compounds

The cytogenetic activity of some substances formed in agricultural plants during metabolism of pesticides of four classes of chemical compounds was studied in the culture of human peripheric blood lymphocytes. Metabolites were shown either to have mutagenic properties similar to those of the initial compounds (ziramtetramethylthiourea, both being mutagens; captan-phthalimide, both possessing no cytogenetic activity) or to be considerably transformed in comparison with them as a result of deactivation (benomile-MBC) or activation (betanal-MHPC) processes. The latter variant if being determined for the genetic hazard of the pesticide necessitates to take into account data on the mutagenic character of those metabolites which really might enter the human organism.     

The effect of two chemical mutagens ENU and MMS on MR-mediated reversion of an insertion-sequence mutation in Drosophila melanogaster

The effects of two mutagens ENU and MMS characterized by different alkylation patterns have been studied on the reversion of an MR-induced singed mutation to wild-type. Reversion of this unstable singed mutation under the influence of MR is assumed to represent the removal or transposition of an insertion element. Since MR acts primarily in spermatogonia, the mutagens were fed to 1st instar larvae. Recessive lethal tests were carried out simultaneously to calibrate for the mutagenic effectiveness of the chemicals. For both powerful mutagens, it was observed that the frequency of reversion remained far below of what would have been expected on the basis of the mutagenic effectiveness, as registered in the lethal tests. Thus 1 mM ENU, 5 mM and 10 mM MMS did not affect the reversion frequency at all, and with 3 mM ENU only a doubling of the reversion frequency was observed, despite a 5-fold increase in the lethal frequency. The threshold at 1 mM EMU and the low effectiveness of 3 mM on the reversion process are taken as an indication that ENU affected the transposition process in an indirect manner, rather than the excision events themselves. The data obtained with Drosophila are consistent with the microbial observations in that mutation involving removal or transposition of an insertion element is not affected by mutagenic treatments. This finding may have consequences for the evaluation of induced genetic damage on the basis of the spontaneous load of genetic detriment in man.

An incidental observation was that non-MR Cy larvae exhibited greater sensitivity to the induction of recessive lethals by MMS than MR-individuals.     

Experimental work on induced mutations

The detection of changes in mutation rate in human populations remains extremely difficult. Thus estimation of genetic hazards of mutagens to man depends on extrapolation from experimental systems. Germ cells of animals show complex variations in sensitivity to mutagenic effects. Some agents predominantly affect stem cells or other immature germ cells, whereas others mainly affect later germ cell stages. Dose-response relations also vary both with the agent and with the stage or sex of germ cell treated. In man, in addition to single-gene defects and chromosome anomalies, conditions of complex or uncertain inheritance, such as congenital malformations, are clinically important. Genetic theory leaves unclear whether the incidence of these would be affected by a change in mutation rate. Recent research has shown that in mice the incidence of malformations is increased by exposure of the parents to mutagens, but the effect is small. Chromosomal non-disjunction is also clinically important. Again, recent research shows that its frequency can be changed by mutagens, but the effects vary with germ-cell stage. Thus, further research is needed to elucidate the relative contributions of different environmental mutagens to human genetic disease.     

The present status of higher plant bioassays for the detection of environmental mutagens

Higher plants provide valuable genetic assay systems for screening and monitoring environmental pollutants. They are now recognized as excellent indicators of cytogenetic and mutagenic effects of environmental chemicals and are applicable for the detection of environmental mutagens both indoor and outdoor. Comparisons between plant and nonplant genetic assay systems indicate that higher plant genetic assays have a high sensitivity (i.e. few false negatives). Two assays which are considered ideal for in situ monitoring and testing of airborne and aqueous mutagenic agents are the Tradescantia stamen hair assay for mutations and the Tradescantia micronucleus assay for chromosome aberrations. Both assays can be used for in vivo and in vitro testing. Other higher plant gentoxicity assys which have a large number of genetic markers and/or data base and are also highly suitable for testing for genotoxic agents include Arabidopsis thaliana, Allium cepa, Hordeum vulgare, Vicia faba, and Zea mays. Since higher plant systems are now recognized as excellent indicators of the cytotoxic, cytogenetic, and mutagenic effects of environmental chemicals and have unique advantages for in situ monitoring and screening it is recommended that higher plant systems be accepted by regulatory authorities as an alternative first-tier assay system for the detection of possible genetic damage resulting from pollution or the use of environmental chemicals. The results from higher platn genetic assays could meke a significant contribution in protecting the public from agents that can cause mutation and cancer. The advantages possessed by higher plant genetic assays, which are inexpensive and easy to handle, make them ideal for use by scientists in developing countries.     

Cytogenetic analysis of the action of new bifunctional alkylating compounds]

The mutagenic activity of nitrogen mustard derivatives of aminovinylketones (NP-130, NP-161, NP-163), aminovinylphosphoric acid (RVS-445, RVS-446, RVS-448, RVS-398) and ethylene imine derivatives of ethane sulphonic acid (AR, RJ) was established for the first time in the experiments with Allium fistulosum L. The mutagenic activity of aminovinylketones (NP-130, NP-160) was established for the first time in the experiments with Crepis capillaris (L.) Wallr. The effect of the compounds studied on the seedlings characterized by the high level of natural mutability of chromosomes did not alter the spectrum of structural chromosome mutations. As it is shown by the results of the analysis, the compounds studied exert their action mainly at the S stage of the cell cycle. However, the initiation of potential changes at the G1 stage that are realized into actual breaks at the S stage is not excluded. In some experiments in which high concentrations of mutagens were used no delayed effect was observed which might be explained by the action of mutagens on cells at the G2 stage or at a still later stage.     

Relationship between environmental pollution and genetic monitoring of human populations

The basis of genetic monitoring is the knowledge of laws of the spontaneous mutation process. These laws are determined for human chromosome and genome mutations by cytogenetic examination of newborns, infants with congenital defects, and the material of spontaneous abortions. Confidence intervals and all the necessary sample sizes were calculated when registering the mutagenic effects of different intensity in the general population as well as to the groups of closer contact with mutagens. Such calculations were made for controlling the spontaneous mutation process in lymphocytes of human peripheral blood on the basis of registering chromosome aberrations.     

Microsomal activation to mutagens of antischistosomal methyl thioxanthenones and initial tests on a possibly non-mutagenic analogue.

Five methylthioxanthenone and methylbenzothiopyranoindazole analogues, including lucanthone (Miracil D), are non-mutagenic for Salmonella typhimurium but are activated to mutagens by a rat liver microsome preparation. Hydroxymethyl analogues, including hycathone (Etrenol), are mutagenic in the absence of microsomes. It seems reasonable to assume that the hydroxymethyl derivatives are the more proximal mutagens and that Salmonella is unable to carry out the hydroxylation necessary for mutagen activation. During the pase 24 years, several million patients with schistosomiasis have been treated with lucanthone, and in recent years about 700 000 persons with hycanthone. The possible long-term deleterious effects of these agents for man even now remain to be determined. Our studies indicate that particular modifications in the structure of thioxanthenones drastically alter their mutagenicity. One apparently non-mutagenic thioxanthenone has been found. A number of the less mutagenic compounds also exhibit decreased acute toxicity in the mouse while retaining appreciable antischistosomal activity, suggesting that genetic and schistosomicidal activities may be dissociated from each other.     

Fluoranthene, a volatile mutagenic compound, present in creosote and coal tar

Creosote, a coal-tar distillation product, contains mutagens which are volatile at 37 degrees C. After distillation of creosote we found that these volatile mutagens were present in the distillation fraction with the highest boiling range (greater than 360 degrees C). The "volatile mutagenic activity" was connected with the presence of fluoranthene, a polycyclic aromatic hydrocarbon. Commercially available fluoranthene was positive in the so-called "taped-plate assay" (the test system used for the detection of volatile mutagens) towards the strains TA98 and TA100 in the presence of S9 mix. The tested creosote and coal tar contained fluoranthene in concentrations of 5.2 and 2.2%, respectively.     

The capacity of Drosophila for detecting relevant genetic damage

For the detection and study of mutagenic agents, Drosophila offers many advantages. It is a higher organism with a short generation time that is cheap and easy to breed in large numbers. The simple genetic testing methods provide unequivocal answers about the whole spectrum of relevant genetic damage. A comparison of the detection capacity of assays sampling different kinds of genetic damage revealed that various substances are highly effective in inducing mutations, but do not produce chromosome breakage effects at all, or only at much higher concentrations than those required for mutation induction. Of the different assay systems available, the classical sex-linked recessive lethal test thus deserves priority, in view of its superior capacity to detect mutagens. Of practical importance is also its high sensitivity, because a large number of loci in one-fifth of the genome is tested for newly induced forward mutations, including small deletions.Drosophila is capable of carrying out the same metabolic activation reactions as the mammalian liver. An additional advantage, in this respect, is the capacity of Drosphila for detecting short-lived activation products, because intracellular activation occurs within the spermatids and spermatocytes. These properties make the test for recessive sex-linked lethals a useful tool for verifying results obtained in the pre-screening of potential mutagens with fast microbial assay systems.In studies on non-disjunction, detailed genetic analysis of the induced changes is possible, and these may shed light on the mechanisms involved.A new adaptation of the bithorax transvection method by Mendelson permits the recovery of high yields of chromosome aberrations in a fast one-generation test.     

Vaginal contents show in vitro mutagenic activity

In Millipore filtrate of some vaginal douching, mutagens were readily detected by means of the Ames Salmonella test. Among 521 subjects, the samples of 76 cases (14.6%) were mutagenic in Salmonella typhimurium TA98 or/and TA100 in the presence or absence of S9 mixture. Dichloromethane and chloroform were found to extract the mutagens satisfactorily.     

The interrelation of the antimutagenic action of mannitol to its effect on cellular metabolic processes]

The mannitol influence on mutagenesis of ionizing radiation and cyclophosphate has been studied in albino mongrel rats using the methods of genetic and biochemical analysis. N correlation is determined between antimutagenic action of this preparation and a decrease of malondialdehyde content in cells and free fractions of matrix lysosomes (beta-galactosidase; N-acetyl-beta-D-glucosaminidase) and firmly membrane-structurized microsomal (glucose-6-phosphatase) enzymes, whose level increases under the influence of mutagens. It is shown that, one of the way of antimutagenic actions of mannitol is connected with mutagenesis correction at the stage of origin of mutagenic products and their transport to chromosome DNA.     

New approaches to assessing the effects of mutagenic agents on the integrity of the human genome

Heritable genetic alterations, although individually rare, have a substantial collective health impact. Approximately 20% of these are new mutations of unknown cause. Assessment of the effect of exposures to DNA damaging agents, i.e. mutagenic chemicals and radiations, on the integrity of the human genome and on the occurrence of genetic disease remains a daunting challenge. Recent insights may explain why previous examination of human exposures to ionizing radiation, as in Hiroshima and Nagasaki, failed to reveal heritable genetic effects. New opportunities to assess the heritable genetic damaging effects of environmental mutagens are afforded by: (1) integration of knowledge on the molecular nature of genetic disorders and the molecular effects of mutagens; (2) the development of more practical assays for germline mutagenesis; (3) the likely use of population-based genetic screening in personalized medicine.     

Bacterial mutagenicity investigation of epoxides: drugs,drug metabolites,steroids and pesticides

Although it has been observed that many epoxides are ultimate mutagens, surprisingly little is known about epoxides to which man may be extensively exposed, e.g., physiological compounds, drugs, drug metabolites and pesticides. We have now investigated 35 such and related epoxides for mutagenicity, using reversion of his^?Salmonella typhimurium TA98 and TA100 as biological end-point. None of the tested steroids (12 compounds), vitamin K epoxides (3 compounds) and pesticides (dieldrin, endrin, HEOM (1,2,3,4,9,9-hexachloro-6,7-epoxy-1,4,4a5,6,7,8,8a-octahydro-1,4-methanonaphthalene), heptachlor epoxide) showed any mutagenic activity. Negative results were also obtained with the antibiotics oleandomycin, anti-capsin and asperlin, the cardiotonic drug resibufogenin, the widely used parasympatholytic drugs butylscopolamine and scopolamine, the sedatives valtratum, didovaltratum and acevaltratum, the tranquilizer oxanamide as well as with the drug metabolites carbamazepine 10,11-oxide and diethylstilbestrol α,β-oxide. Three barbiturate epoxides, formed by metabolism of allobarbital, alphenal and secobarbital, caused weak but reproducible mutagenic effects at high concentrations. The cytostatic agent ethoglucide was the only drug having substantial mutagenic activity. Its mutagenic potency was similar to those of the control epoxides styrene 7,8-oxide, p-bromostyrene 7,8-oxide and m-bromostyrene 7,8-oxide, but much lower than those of benzo[a]pyrene 4,5-oxide, benzo[e]pyrene 4,5-oxide and 7,12-dimethylbenz[a]-anthracene 5,6-oxide.Some epoxides were also tested in other Salmonella typhimurium strains or in the presence of rat-liver S9 mix. Positive results were only obtained with compounds that had already been detected as mutagens in the direct test with strain TA100.     

Further mutagenicity studies on pesticides in bacterial reversion assay systems

A total of 228 pesticides (88 insecticides, 60 fungicides, 62 herbicides, 12 plant-growth regulators, 3 metabolites and 3 other compounds) was tested for mutagenicity in bacterial reversion-assay systems with 5 strains (TA100, TA98, TA1535, TA1537 and TA1538) of Salmonella typhimurium and a strain (WP2 hcr) of Escherichia coli. 50 pesticides (25 insecticides, 20 fungicides, 3 herbicides, 1 plant-growth regulator and 1 other compound) were found to be mutagenic. 5 of them required metabolic activation (S9 mix) for their activities. Among various chemical groups, organic phosphates, halogenated alkanes and dithiocarbamates showed higher ratios of mutagens. Although 22 of the pesticides tested have been reported to be carcinogenic, 7 of them, i.e., captain, DBCP, EDB, EDC, ETU, HEH and nitrofen, were detected as mutagens in the present assay. Most of the other 15 non-mutagenic carcinogens were organochlorine pesticides such as alpha-BHC, chlorobenzilate, p,p'-DDT, dieldrin and quintozene.     

Antimutagenicity profiles of some natural substances.

Selected antimutagenicity listings and profiles have been prepared from the literature on the antimutagenicity of retinoids and the carotenoid beta-carotene. The antimutagenicity profiles show: (1) a single antimutagen (e.g., retinol) tested in combination with various mutagens or (2) antimutagens tested against a single mutagen (e.g., aflatoxin B1). Data are presented in the profiles showing a dose range for a given antimutagen and a single dose for the corresponding mutagen; inhibition as well as enhancement of mutagenic activity is indicated. Information was found in the literature on the testing of selected combinations of 16 retinoids and carotenoids vs. 33 mutagens. Of 528 possible antimutagen-mutagen combinations, only 82 (16%) have been evaluated. The most completely evaluated retinoids are retinol (28 mutagens), retinoic acid and retinol acetate (7 mutagens each), and retinal and retinol palmitate (6 mutagens each). beta-Carotene is the most frequently tested carotenoid (15 mutagens). Of the remaining retinoids and carotenoids, 8 were evaluated in combination with a single mutagen and the other 2 were tested against only 2 or 3 mutagens. Most of the data on antimutagenicity in vitro are available for S. typhimurium strains TA98 and TA100. Substantial data also are available for sister-chromatid exchanges in vitro and chromosome aberrations in vitro and in vivo. This report emphasizes the metabolic as well as the antimutagenic effects of retinoids in vitro and in vivo.     

Higher plant assays for the detection of chromosomal aberrations and gene mutations-a brief historical background on their use for screening and monitoring environmental chemicals.

Higher plants are recognized as excellent indicators of cytogenetic and mutagenic effects of environmental chemicals and are applicable for the detection of environmental mutagens both indoor and outdoor. They are highly reliable bioassays with a high sensitivity for monitoring and testing for genotoxins. A brief review of major steps in the development of higher plant genotoxic assays is given.