An overview of short-term tests for the mutagenic and carcinogenic potential of pesticides

A Comprehensive, Integrated Review and Evaluation of the Scientific Evidence Relating to the Safety of the Herbicide 2,4-D

The safety of 2,4-D to farm and forestry workers, commercial applicators and the general public has been of continuing concern because certain epidemiological studies of groups potentially exposed to 2,4-D have suggested a relationship between 2,4-D use and increased risk of soft tissue sarcoma, Hodgkin's disease or non-Hodgkin's lymphoma. This review on 2,4-D is unique in that the approach taken was to integrate data from worker exposure studies, whole animals, metabolic and other relevant laboratory studies with the epidemiological findings to assess the extent to which there is scientific support for the hypothesis that 2,4-D exposure is associated with any increased risk of human cancer.

The case-control epidemiological studies that have been the source of the cancer risk hypothesis are inconclusive. Problems in assessing exposure based on patients' memories make these studies difficult to interpret. Cohort studies of exposed workers do not generally support the specific hypothesis that 2,4-D causes cancer. Taken together, the epidemiological studies provide, at best, only weak evidence of an association between 2,4-D and the risk of cancer.

Importantly, the cancer hypothesis is not supported by other data. A critical evaluation of the exposure data indicates that exposure to 2,4-D in user groups is intermittent and much lower than the doses tested chronically in long-term animal studies that have not shown evidence of tumor induction. Moreover, the structure of 2,4-D does not suggest it would be a carcinogen. 2,4-D is a simple organic acid, that is largely excreted unchanged, and there is no evidence that it is metabolized to critically reactive metabolites or accumulates in tissues. This evidence is supported by a large body of negative studies on genotoxicity, which taken together with the metabolic studies, clearly indicates that 2,4-D is highly unlikely to be a genotoxic carcinogen. Furthermore, 2,4-D has no known hormonal activity and does not induce proliferative changes in any tissue or organ, indicating that it does not possess any of the characteristics of non-genotoxic animal carcinogens. Thus the available mechanistic studies provide no plausible basis for a hypothesis of carcinogenicity.

In this review, data relating to potential neurotoxicity, immunotoxicity and reproductive toxicity also were evaluated. There is no evidence that 2,4-D adversely affects the immune system and neurotoxic and reproductive effects only have been associated with high toxic doses that would not be encountered by 2,4-D users.

Historical exposures to 2,4-D by user groups, particularly farmers, forestry workers and commercial applicators, would be higher than those sustained under present rigorous standards for application which involve the use of protective clothing and other measures to reduce exposure. Proposed label changes indicate that in the future exposures will be even further reduced. Viewed in this context, the available data indicate that the potential public health impact of 2,4-D, including the risk of human cancer, was negligible in the past and would be expected to be even smaller in the present and future.

Cytotoxicity and Genotoxicity Induced by the Pesticide Profenofos on Cultured Human Peripheral Blood Lymphocytes

Profenofos is a broad-spectrum organophosphate insecticide and acaricide used widely for agricultural and household purposes. The aim of this investigation was to determine its toxicity profile in vitro, using lymphocytes from peripheral blood samples of healthy human donors. We found the IC(50) of profenofos to be 3.5 microM as measured by Trypan blue dye exclusion method. Chromosomal analyses of the metaphase plates of the samples treated with sublethal concentrations of profenofos revealed satellite associations and chromatid breaks and gaps, indicating its effect on chromosomes. The results were further supported by comet assay, where single-strand breaks in DNA were observed as comet tail lengths. The results were statistically significant (p < 0.01, ANOVA). Hence, it may be proposed that in vitro assays like the comet assay and chromosomal aberrations test, which indicate genetic damage, could be used to study the effect of organophosphorus pesticide poisoning in humans.

Pesticide use and colorectal cancer risk in the Agricultural Health Study

We investigated the relationship between agricultural pesticides and colorectal cancer incidence in the Agricultural Health Study. A total of 56,813 pesticide applicators with no prior history of colorectal cancer were included in this analysis. Detailed pesticide exposure and other information were obtained from self-administered questionnaires completed at the time of enrollment (1993-1997). Cancer incidence was determined through population-based cancer registries from enrollment through December 31, 2002. A total of 305 incident colorectal cancers (212 colon, 93 rectum) were diagnosed during the study period, 1993-2002. Although most of the 50 pesticides studied were not associated with colorectal cancer risk, chlorpyrifos use showed significant exposure response trend (p for trend = 0.008) for rectal cancer, rising to a 2.7-fold (95% confidence interval: 1.2-6.4) increased risk in the highest exposure category. Aldicarb was associated with a significantly increased risk of colon cancer (p for trend = 0.001), based on a small number of exposed cases, with the highest exposure category resulting in a 4.1-fold increased risk (95% confidence interval: 1.3-12.8). In contrast, dichlorophenoxyacetic acid showed a significant inverse association with colon cancer but the association was not monotonic. Our findings should be interpreted cautiously since the literature suggesting that pesticides are related to colorectal cancer is limited. Nonetheless the possibility of an association between exposure to certain pesticides and incidence of colorectal cancer among pesticide applicators deserves further evaluation.

Pesticides and human cancers

The potential for human carcinogenicity of almost all pesticides currently on the market has been poorly evaluated and is inadequately understood. Generating mechanistic data in both animal studies and epidemiology will play an increasingly important role in the future. Improved exposure assessment, in large prospective studies that generate reliable exposure-response data that focus on individual pesticide exposures are needed. One of the greatest opportunities to make more rapid progress will be to foster more multi-disciplinary collaborations between toxicologists and epidemiologists. Collaborations on molecular epidemiology investigations offers such opportunities to both toxicologists and epidemiologists that were not possible even a decade ago.

Modulation of the genotoxicity of pesticides reacted with redox-modified smectite clay

Pesticides are toxic agents intentionally released into the environment; their use raises public health and environmental concerns. In recent years there has been much attention to the biotic degradation of pesticides. Abiotic mechanisms in the soil can contribute to pesticide degradation yet the toxicological impact of such degradation is unclear. This study combines for the first time an investigation into abiotic mechanisms of degradation coupled with toxicological endpoints in mammalian cells. The genotoxicity of three commonly used agricultural pesticides was assessed before and after exposure to redox-modified clay minerals. The objectives of the study were to determine the genotoxicity of 2,4-dichlorophenoxy acetic acid (2,4-D), dicamba, and oxamyl, using single cell gel electrophoresis with Chinese hamster ovary (CHO) cells, and to determine the effect of the iron oxidation state in clay minerals (ferruginous smectite SWa-1) on the genotoxic potency of the pesticides. 2,4-D alone or following reaction with redox-modified clays did not induce DNA damage in CHO cells. Oxamyl alone induced a concentration-dependent increase in genomic DNA damage; however, its genotoxicity declined after reaction with reduced clay minerals. Dicamba was not genotoxic when directly analyzed. When dicamba was reacted with reduced clay, a concentration-dependent increase in genomic DNA damage was observed. This is the first reported case of a pesticide being converted into a genotoxin after exposure to redox-modified smectites. These data introduce a new paradigm on the interaction between redox-modified clays and pesticide-related environmental genotoxicity.

Cancer Incidence Among Pesticide Applicators Exposed to Chlorpyrifos in the Agricultural Health Study

BACKGROUND

Chlorpyrifos is one of the most widely used insecticides in the United States. We evaluated the incidence of cancer among pesticide applicators exposed to chlorpyrifos in the Agricultural Health Study, a prospective cohort study of licensed pesticide applicators in Iowa and North Carolina.

METHODS

A total of 54,383 pesticide applicators were included in this analysis. Detailed information on pesticide exposure and lifestyle factors was obtained from self-administered questionnaires completed at the time of enrollment (December 1993-December 1997). Poisson regression analysis was used to evaluate the association between chlorpyrifos exposure and cancer incidence after adjustment for potential confounders. All statistical tests were two-sided.

RESULTS

A total of 2070 incident malignant neoplasms were diagnosed through 2001. The rate ratio for all cancers combined among chlorpyrifos-exposed applicators compared with nonexposed applicators was 0.97 (95% confidence interval = 0.87 to 1.08). For most cancers analyzed, there was no evidence of an exposure-response relationship. However, the incidence of lung cancer was statistically significantly associated with both chlorpyrifos lifetime exposure-days (P(trend) = .002) and chlorpyrifos intensity-weighted exposure-days (P(trend) = .036). After adjustment for other pesticide exposures and demographic factors, individuals in the highest quartile of chlorpyrifos lifetime exposure-days (>56 days) had a relative risk of lung cancer 2.18 (95% confidence interval = 1.31 to 3.64) times that of those with no chlorpyrifos exposure.

CONCLUSION

Our findings suggest an association between chlorpyrifos use and incidence of lung cancer that deserves further evaluation.

Mutagens in surface waters: a review

A review of the literature on the mutagenicity/genotoxicity of surface waters is presented in this article. Subheadings of this article include a description of sample concentration methods, mutagenic/genotoxic bioassay data, and suspected or identified mutagens in surface waters published in the literature since 1990. Much of the published surface water mutagenicity/genotoxicity studies employed the Salmonella/mutagenicity test with strains TA98 and/or TA100 with and/or without metabolic activation. Among all data analyzed, the percentage of positive samples toward TA98 was approximately 15%, both in the absence and the presence of S9 mix. Those positive toward TA100 were 7%, both with and without S9 mix. The percentage classified as highly mutagenic (2500-5000 revertants per liter) or extremely mutagenic (more than 5000 revertants per liter) was approximately 3-5% both towards TA98 and TA100, regardless of the absence or the presence of S9 mix. This analysis demonstrates that some rivers in the world, especially in Europe, Asia and South America, are contaminated with potent direct-acting and indirect-acting frameshift-type and base substitution-type mutagens. These rivers are reported to be contaminated by either partially treated or untreated discharges from chemical industries, petrochemical industries, oil refineries, oil spills, rolling steel mills, untreated domestic sludges and pesticides runoff. Aquatic organisms such as teleosts and bivalves have also been used as sentinels to monitor contamination of surface water with genotoxic chemicals. DNA modifications were analyzed for this purpose. Many studies indicate that the 32P-postlabeling assay, the single cell gel electrophoresis (comet) assay and the micronucleus test are sensitive enough to monitor genotoxic responses of indigenous aquatic organisms to environmental pollution. In order to efficiently assess the presence of mutagens in the water, in addition to the chemical analysis, mutagenicity/genotoxicity assays should be included as additional parameters in water quality monitoring programs. This is because according to this review they proved to be sensitive and reliable tools in the detection of mutagenic activity in aquatic environment. Many attempts to identify the chemicals responsible for the mutagenicity/genotoxicity of surface waters have been reported. Among these reports, researchers identified heavy metals, PAHs, heterocyclic amines, pesticides and so on. By combining the blue cotton hanging method as an adsorbent and the O-acetyltransferase-overproducing strain as a sensitive strain for aminoarenes, Japanese researchers identified two new type of potent frameshift-type mutagens, formed unintentionally, in several surface waters. One group has a 2-phenylbenzotriazole (PBTA) structure, and seven analogues, PBTA-type mutagens, were identified in surface waters collected at sites below textile dyeing factories and municipal wastewater treatment plants treating domestic wastes and effluents. The other one has a polychlorinated biphenyl (PCB) skelton with nitro and amino substitution group and it was revealed to be 4-amino-3,3'-dichloro-5,4'-dinitrobiphenyl derived from chemical plants treating polymers and dye intermediates. However, the identification of major putative mutagenic/genotoxic compounds in most surface waters with high mutagenic/genotoxic activity in the world have not been performed. Further efforts on chemical isolation and identification by bioassay-directed chemical analysis should be performed.

Effect of Organophosphorus and Organochlorine Pesticides (Monochrotophos, Chlorpyriphos, Dimethoate, and Endosulfan) on Human Lymphocytes In‐Vitro

The toxicological profile of the four pesticides described herein characterizes its effects on lymphocytes from peripheral blood from healthy donors. The exposure to all pesticides was by direct interaction/incubation with varying concentrations of the pesticide with blood sample in-vitro. The dose response relationship in each case was calculated by applying log tables as LC50 values. Cytotoxicity of these pesticides on lymphocytes was measured using the trypan blue dye exclusion technique. Based on LC50 value, all the four pesticides were found to be highly toxic to lymphocyte culture, among them, monocrotophos and endosulfan were the most toxic and dimethoate was the least toxic. The genotoxicity of the pesticides was also determined by comet assay. The results revealed that the pesticides caused increase in the tail length indicating DNA damage. This study suggests that these pesticides have the capacity to alter the genetic material particularly chromosomes in mammalian cultures. The comet assay used in this study was found to be a sensitive and rapid method to detect genotoxicity of pesticide compounds.

Micronucleus formation in 3-day mouse embryos associated with maternal exposure to chlorpyrifos during the early preimplantation period

Chlorpyrifos, an organophosphate pesticide, was evaluated for its ability to induce cytogenetic damage in preimplantation embryos after maternal exposure. Pregnant female mice were intraperitoneally (i.p.) administered a single dose of chlorpyrifos (40 or 80 mg/kg) at 10:00 h on Day 0 of pregnancy. On Day 3 of gestation, blastocysts were collected and evaluated for gross morphology, micronucleus (MN) frequency, and cell number. A significant increase in MN frequency indicating cytogenetic damage was observed in the treatment groups in comparison to control. The MN frequency revealed a clear dose-dependent increase. There was also a significant decrease in the embryo cell number in the 80 mg/kg treated group. A simultaneous decrease in the cell number and increase in MN frequency may reflect an embryonic developmental disadvantage resulting from maternal treatment with chlorpyrifos.

Detection of DNA damage in mouse peripheral blood leukocytes by the comet assay after oral administration of monocrotophos

The objective of this study was to determine if single/double strand DNA breaks could be induced by monocrotophos (organophosphorus pesticide) in mice in vivo using the comet assay. Mice were dosed orally with 0.046, 0.093, 0.186, 0.373 and 0.746 mg/kg body weight of monocrotophos, and the assay was performed on whole blood after 24, 48 and 72 h. A significant increase in mean comet tail length indicating DNA damage was observed at 24 and 48 h post-treatment with monocrotophos when compared to controls. A decrease in the mean tail length was observed at 72 h post-treatment indicating repair of the damaged DNA. The mean tail length showed a dose-related increase and time dependent decrease. The study reveals that comet assay is a sensitive and rapid method to detect genotoxicity of monocrotophos.

Genotoxicity of selected pesticides in the mouse bone-marrow micronucleus test and in the sister-chromatid exchange test with human lymphocytes in vitro

Selected pesticides (aldicarb, 1,3-dichloropropene, methidathion, parathion, triadimefon, vinclozolin) were tested for their clastogenic and aneugenic activities in the mouse bone-marrow micronucleus (MN) test in vivo and for their sister-chromatid exchange-inducing activities in human lymphocytes in vitro in the presence and absence of an exogenous metabolizing system from rat-liver S9. 1,3-Dichloropropene significantly increased the frequencies of micronucleated polychromatic erythrocytes (PCE) in bone-marrow cells of female mice from 3.3 MN/1000 PCE to 15.3 MN/1000 PCE (187 mg per kg body weight). 1,3-Dichloropropene (100 microM) induced 16.0 SCE/metaphase after 24 h of incubation as compared with the basal rate of 11.2 SCE/metaphase (-S9) and of 15.4 SCE/metaphase as compared with 10.5 SCE/metaphase of the control (+S9). These values were statistically significantly different from each other. The other pesticides tested did neither increase the rate of micronuclei significantly in polychromatic erythrocytes in male nor in female animals. Aldicarb and methidathion induced a significant increase in SCEs in human lymphocytes in vitro only without the metabolic activating system: aldicarb, 5 microM, 24 h incubation: 15.5 SCE/metaphase; control: 12.6 SCE/metaphase; methidathion, 100 microM, 24 h incubation: 15.8 SCE/metaphase, control: 11.1 SCE/metaphase. Parathion, triadimefon and vinclozolin did not have any SCE-inducing effects.

Genotoxicity of the Ganges water at Narora (U.P.), India

Water samples were collected from the river Ganga at Narora (U.P.). High performance liquid chromatography analysis of water samples by the liquid extraction procedure indicated the presence of several pesticides such as DDT, alpha-BHC, aldrin, endrin and dieldrin at concentrations of 1.36, 1.38, 0.95, 0.61 and 0.41 ppb, respectively. The organophosphorus pesticides such as dimethoate and methyl parathion also appear to be present at concentrations of 0.20 and 0.41 ppb, respectively. The XAD water concentrates and liquid-liquid extracted water samples were assayed for mutagenic potential by the Ames Salmonella/microsome test. The test samples exhibited a significant degree of mutagenicity with TA102, TA100 and TA98 strains both in the presence and absence of DNA repair defective mutants, recA, lexA and polA of E. coli was observed as compared to their wild-type counterpart in the presence of XAD water concentrates.

Mutagenic activity of the Ganges water with special reference to the pesticide pollution in the river between Kachla to Kannauj (U.P.), India

Water samples from Ganga river were collected from 3 different locations viz. Kachla, Fatehgarh and Kannauj (U.P.). High performance liquid chromatography analysis of samples by liquid-liquid extraction procedure showed the presence of some pesticides like DDT, alpha-BHC, aldrin, dieldrin etc. DDT, alpha-BHC, DDD, aldrin and dieldrin were present at concentration ranges of 3.33-5.33 ppb, 1.73-3.01 ppb, 0.88-2.41 ppb, 1.17-2.81 ppb and 0.49-4.11 ppb, respectively. The organophosphorus pesticides like dimethoate and methyl parathion were also detected at the concentration levels of 0.41-0.56 ppb and 0.16-0.50 ppb, respectively. The organic substances in the test samples were extracted by XAD-resin and liquid-liquid extraction procedures, and the extracts were assayed for mutagenic potential by the Ames Salmonella/microsome test. The test samples exhibited a remarkable degree of mutagenicity with TA98, TA100 and TA97a strains with the probable role of contaminating pesticides in the river water.

Genetic safety evaluation of pesticides in different short-term tests

Cyanazine, cyhexatin, dicamba and DNOC are pesticides commonly and broadly used in agriculture pest control. However, there is little information on their toxicity and mutagenicity in human cells and in whole animals. Therefore, UDS assay and SCE assay in human peripheral lymphocytes, and chromosome aberration analysis in bone marrow of rats have been used to assess the DNA-damaging activity of the above pesticides. Cyanazine proved non-genotoxic in all the test systems. Cyhexatin showed only weakly positive results for SCE induction in human lymphocytes, providing no concern for genotoxicological hazard. While dicamba did not show clastogenic effects in rodents, DNOC gave significant dose-related increases of structural chromosome aberrations in rat bone marrow cells. Female animals showed increased sensitivity to the toxic effects by DNOC at the highest dose. The results provide further information on the intrinsic genotoxic activity of the tested pesticides, which may contribute to the toxicological assessment of the risk associated with human exposure.

Genotoxicity assay of five pesticides and their mixtures in Saccharomyces cerevisiae D7

Four organophosphorus pesticides (azinphos-methyl, diazinone, dimethoate, and pirimiphos-methyl), and one carbamate (benomyl) were tested for cytotoxicity, reverse mutation and gene conversion in Saccharomyces cerevisiae D7, with and without the S9 metabolic system. Furthermore, two mixtures of the above compounds, namely benomyl + pirimiphos-methyl (6/1 ratio) and dimethoate + diazinone + azinphos-methyl (10/4/6 ratio) were tested in the same experimental model. Azinphos-methyl, benomyl, and pirimiphos-methyl alone did not induce any genotoxic effect, whereas azinphos-methyl and diazinone were active in inducing reversion and gene conversion. The benomyl + pirimiphos-methyl mixture did not show any genotoxic activity. The dimethoate + diazinone + azimphos-methyl mixture was genotoxic, although an antagonistic effect between the components was observed. The addition of S9 post-mitochondrial liver fraction decreased the activity of both single and mixed genotoxic agents.

Mutagenic and carcinogenic pesticides used in the agricultural environment of Gaza Strip

More than 100 metric tons of formulated pesticides (about 75 pesticides) are used annually in Gaza Strip. It was found that 19 of these pesticides, that have been used, are internationally suspended, cancelled and banned pesticides. About 1100 cases of cancer have been registered in Gaza Strip (1979-1983). The distribution of cancer types among those patients are lymphoma and hematological malignancy, breast, head and neck, gastrointestinal malignancy, reproductive system, urinary system, soft tissue tumors, brain tumors and others. Consequently, the introduction and heavy use of pesticides and other toxic substances in the Gaza Strip environment is suspected to correlate with the growing incidence of cancer and other abnormalities in the nation. Precise determination of the effects of chronic exposure is, therefore, urgently needed.

Cytogenetic effects of pesticides. IV. Cytogenetic effects of the insecticides Gardona and Dursban

The cytogenetic effects of the insecticides Gardona and Dursban were investigated. The toxicity and ability of both insecticides to induce chromosome aberrations and sister-chromatid exchange in vitro was tested in a primary culture of mouse spleen cells, in order to assess the potential mutagenicity of both insecticides. The concentrations 10(-7)-10(-3) M were used for testing the toxic effects of the insecticides. Both Gardona and Dursban were toxic to spleen cell cultures and the percentage of viable cells decreased as the concentration of the insecticide was increased. It reached 76.8% and 77.8% of control after treatment with the highest concentration tested (10(-3) M) of Gardona and Dursban respectively. Gardona at 0.25, 0.50, 1.0 and 2.0 micrograms/ml, and Dursban at 0.50, 1.0, 2.0 and 4.0 micrograms/ml were tested for the induction of chromosome aberrations and sister-chromatid exchanges. All of the tested concentrations of both insecticides induced a high percentage of metaphases with chromosomal aberrations in cultured mouse spleen cells after 4-h treatment. The frequency of SCEs/cell increased with increasing concentration of the insecticides. It reached 11.92 +/- 0.14/cell and 13.40 +/- 0.20/cell after treatment with Gardona (2 micrograms/ml) and Dursban (4 micrograms/ml), respectively, compared with 8.2 +/- 0.19/cell and 7.6 +/- 0.15/cell in the solvent control. The presented results indicate that both Gardona and Dursban in the tested concentrations are mutagenic in mouse spleen cell cultures.

Hepatic and extra hepatic glutathione depletion and glutathione-S-transferase inhibition by monocrotophos and its two thiol analogues

Effect of monocrotophos (MCP) and its thiol analogues (coded as RPR-2 and RPR-5) on hepatic and extra-hepatic glutathione (GSH) depletion and glutathione-S-transferase (GST) inhibition was studied at 0.96, 1.23 and 3.0 mg/kg respectively 24 h after medication in rats. All the three compounds caused tissue specific depletion of GSH from hepatic and extra-hepatic tissues. Cytosolic GST activity was significantly inhibited in all the tissues, MCP being the most potent inhibitor. Both in vitro and in vivo data indicate that hepatic GST inhibiting potential of the three compounds lies in the order MCP greater than RPR-5 greater than RPR-2. In vitro effect of 3 compounds on GSH activation kinetics of GST demonstrate competitive inhibition by MCP and non-competitive inhibition by the two analogues. However, CDNB activation kinetics of the enzymes revealed mixed inhibition by all 3 compounds. The present study suggests that monocrotophos and its thiol analogues may bring about physiological upsets by altering GSH and GST dependent events in different tissues of exposed organisms.

Mutagenic evaluation of the organophosphorus insecticides methyl parathion and triazophos in Drosophila melanogaster

The possible genotoxic effects of the organophosphorus insecticides methyl parathion and triazophos were evaluated by their ability to induce gene and chromosome mutations in male germ cells of Drosophila melanogaster. Sex-linked recessive lethal (SLRL), total and partial sex-chromosome losses (SCL), and non-disjunction (ND) assays were conducted. The routes of administration included adult feeding, injection, and larval feeding. Methyl parathion was unable to induce point mutations or chromosome mutations, although a small increase in the frequency of non-disjunction was detected after larval treatment. Triazophos induced point mutations when assayed in the SLRL test and induced a weak increase in the non-disjunction frequency, but gave negative results in the SCL test.

Genotoxicity of metacid established through the somatic and germ line mosaic assays and the sex-linked recessive lethal test in Drosophila

The mutagenic potential of metacid (methyl parathion), an anticholinesterase organophosphate pesticide, has been studied in the Drosophila eye, wing and female germ line assays and the sex-linked recessive lethal tests. Larvae 24 h, 48 h and 72 h old, heterozygous for various recessive genetic markers on the first and third chromosomes, were exposed to the LD50 and half of this dose for different periods of time. The eyes and wings were checked for the presence of mosaic spots and eggs laid by the females for germ line mosaicism. The M-5 technique was used to detect the induction of sex-linked recessive lethals. It is concluded that metacid is mutagenic in somatic and germ line cells of Drosophila and induces sex-linked recessive lethals in immature male germ cells.

Genotoxic effects of some organophosphorus pesticides. II. In vivo chromosomal aberration bioassay in bone marrow cells in rat

The genotoxic effects of 4 organophosphorus pesticides, i.e., ekatin, fenitrothion, methylparathion and phorate, were assessed employing in vivo chromosomal aberration bioassay in bone marrow cells in rat. Methylparathion and phorate were found to be mutagenic while ekatin was weakly mutagenic. The frequency of chromosomal aberrations induced by fenitrothion did not differ significantly from that observed in negative control.

Lack of induction of nuclear aberrations by captan in mouse duodenum

The fungicide, captan, is known to induce point mutations in vitro. In extremely high doses, technical grade captan leads to duodenal tumors in mice. In short-term in vivo assays for genotoxicity, equivocal results have been obtained with captan. In this study, the genotoxicity of captan was studied in vivo in the proximal small intestine of the mouse, the site of its oncogenicity. Orally administered captan up to 4,000 mg/kg body weight failed to induce a response in the small intestine nuclear aberration assay in a wide range of doses under a variety of experimental conditions, including pretreatment of animals with L-buthionine-S, R-sulfoximine (an inhibitor of glutathione biosynthesis). 1,2,3,6-Tetrahydrophthalimide and bis (trichloromethyl)disulfide, two compounds that have been identified as impurities in technical grade captan, also failed to produce positive results in this assay.

Indication for weak mutagenicity of the organophosphorus insecticide dimethoate in Drosophila melanogaster

The organophosphorus insecticide dimethoate was tested for induction of genetic damage in male germ cells of Drosophila melanogaster. Sex-linked recessive lethals, sex-chromosome loss and non-disjunction induction were studied following different routes of administration: adult feeding, injection and larval feeding. Our results show that, after injection, dimethoate induces a slight but significant increase in the frequency of point mutations.

Structure-genotoxic activity relationships of pesticides: comparison of the results from several short-term assays

The Computer-Automated Structure Evaluation (CASE) program has been applied to the analysis of the genotoxic activity of 54 pesticides (31 insecticides, 15 herbicides and 8 fungicides) in 5 different short-term test systems measuring gene mutation and DNA damage. The database contains compounds presenting diverse structures including carbamates, thiocarbamates, organophosphates, halo-aromatics and other functionalities. Some significant relationships between common structural features and the genotoxic activity displayed by these chemicals have been found. Among the most relevant fragments, automatically selected by the program, a methoxyphosphinyl and a chlorovinyl group appear as the common structural subunits responsible for the activities detected in the battery composed of the Salmonella typhimurium histidine reversion assay, the mouse lymphoma gene mutation assay and recombination in the yeast Saccharomyces cerevisiae.

Genotoxic potential of acephate technical: in vitro and in vivo effects

The genotoxic potential of acephate technical (AT) in vitro and in vivo has been studied in bioassays detecting primary DNA damage, chromosomal alterations, and gene mutation. Results from in vitro assays have ranged from negative to weakly positive; AT is apparently a direct-acting agent in these tests. However, expressed in terms of molar potency, AT has generally been at least 100-1000 times less potent than known positive mutagens tested in vitro. Following in vivo exposure at maximum tolerated doses, AT did not induce chromosomal aberrations, sister chromatid exchange, or micronuclei in mouse bone marrow cells; a dominant lethal study in mice was also negative. In a supplemental study, no induced chromosomal aberrations or sister chromatid exchange could be detected in lymphocytes from a pair of cynomolgus monkeys following exposure to AT at a low dose level for 20 days. At dose levels limited by toxicity, no positive results were observed for induction of sex-linked, recessive lethality in D. melanogaster. Acephate technical (ORTHENE) appears to present little or no genetic hazard to in vivo mammalian systems.

Genotoxic effects of some organophosphorous pesticides. I. Induction of micronuclei in bone marrow cells in rat

The genotoxic effects of 4 organophosphorous pesticides, i.e. ekatin, fenitrothion, methylparathion and phorate, were examined employing the micronucleus test in bone marrow cells of the rat. Methylparathion and phorate were found to be mutagenic, while ekatin was weakly mutagenic. The frequency of micronuclei induction by fenitrothion did not differ significantly from that noticed in negative control.

Evaluation of the genotoxic potential of certain pesticides used in Pakistan

The mutagenicity of fifteen insecticides, five fungicides, four herbicides, and an acaricide commonly used in Pakistan was evaluated by employing thirteen short-term bioassays. The genetic endpoints used included point or gene mutation, primary DNA damage, and chromosomal effects. Initially, all pesticides were tested in a "core" battery of four in vitro bioassays. A carefully selected group among these chemicals was retested in higher level test systems to confirm the results obtained in the initial phase. Of the pesticides tested, only a small portion consistently displayed mutagenicity across test systems. The Saccharomyces cerevisiae bioassays detected mutagenicity for the largest number of pesticides. The Salmonellaces typhimurium strain, TA100, was able to detect genetic activity in all of the pesticides that produced positive results in this bioassay. The cytogenetic effects observed from the Vicia faba root assay were consistent with those obtained in mammalian cells in culture. All pesticides which displayed mutagenicity were not carcinogenic in animal bioassays but, in general, mutagenicity in a battery of short-term bioassays was a reliable indicator of the carcinogenic potential in animals. A simple test battery is proposed for evaluating the genetic potential of agricultural pesticides.

Mutagen testing of agricultural chemicals with yeast

The microorganism Saccharomyces cerevisiae is frequently used to test chemical agents in short-term mutagenicity tests. Advantages of yeast are its eukaryotic character and the numerous genetic endpoints which can be tested. A disadvantage is the lower sensitivity towards compounds which, when compared with the Salmonella Ames test, need to be metabolized in order to be active. However, the sensitivity of yeast tests can be improved by using cells from the logarithmic phase and by growing them under conditions which increase the activity of metabolizing enzymes, such as the cytochrome P-448/P-450 complexes. Furthermore, we discuss which information can be drawn from the shape of the survival and mutation frequency curves, and which parameters from the mutant yield curves can be used to compare the mutagenic efficiencies of various agents or the mutabilities of various test systems. Also, the qualitative yeast assay results are compiled for insecticides and herbicides in agricultural usage in Third World countries (Pakistan, for example).

The use of short-term tests and limited bioassays in carcinogenicity testing

A brief discussion is given of the use of short-term in vivo and in vitro tests in carcinogenicity testing. Data are presented on the performance of nine such tests and five limited bioassays, as measured in terms of their sensitivity, specificity, accuracy, and predictive value. It is concluded that tests are available which, when used in combinations such as have been proposed by various authors, are capable of correctly identifying carcinogens and noncarcinogens with high confidence. A discussion of the statistics of batteries of tests is given. This is followed by a semiquantitative graphical representation and a discussion of how, on proceeding through a testing scheme such as that proposed by J. H. Weisburger and G. M. Williams (1981, Science 214, 401-407), the cumulative cost and the probability of correctly identifying a carcinogen or a noncarcinogen change as results become available from each of the stages of such a testing scheme.

Cytogenetic effects of paraoxon and methyl-parathion on cultured human lymphocytes: SCE, clastogenic activity and cell cycle delay

Paraoxon and methyl-parathion (Wofatox), frequently used organophosphate pesticides, were tested for cytogenetic effects in lymphocytes of persons with different phenotypes of paraoxonase activity. Sister chromatid exchanges (SCE), chromosome breaks, and cell cycle traverse were studied in ten individuals. Paraoxon showed no significant effects whereas methyl-parathion showed a dose-dependent increase in the SCE and a definite delay in the cell cycle as assessed by fluorescence plus Giemsa technique. No significant clastogenic effects and no difference in response were observed among individuals with different phenotypes of paraoxonase.

Mutagenicity and chemical characterization of two petroleum distillates

To investigate if the Salmonella/microsome assay could reliably screen complex petroleum samples for their carcinogenic potential, two high boiling (700-1070 degrees F) petroleum distillates with known activity in a dermal carcinogenesis bioassay were fully characterized with respect to their hydrocarbon composition and polynuclear aromatic hydrocarbon (PNA) content and assayed for mutagenic activity. Mutagenicity assays were also carried out on the aromatic hydrocarbon aggregates separated from these oils by adsorption chromatography. The composition of the distillates differed substantially, and reflected the fact that they were derived from crude oils that were extremely divergent in hydrocarbon character. Both the distillate and aromatic samples consistently induced a very slight increase in revertant TA98 and TA100 colonies; however, an increase of 2-4-fold over background was observed when the S-9 concentration was increased 5-10 times that of the standard assay. The maximal response was less than that expected from the samples' known PNA content and observed potency in the dermal carcinogenesis bioassay. In the Salmonella/microsome assay, all samples inhibited the mutagenic activity of added benzo[a]pyrene. Discordance between the magnitude of the samples' mutagenic activity and their known PNA content may be related to direct or indirect inhibition of sample PNAs by other components of the complex petroleum fractions. Observed inhibitory effects support the use of elevated S-9 concentration in the in vitro assays assessing the carcinogenic potential of petroleum-derived materials.

Genotoxicity of methyl parathion in short-term bacterial test systems

Genotoxicity of the insecticide methyl parathion was investigated in Salmonella typhimurium and Escherichia coli bacterial test systems for the detection of back mutations and DNA-damage. Methyl parathion was mutagenic to S. typhimurium strain TA100 after activation with rat liver microsomal and cytosolic enzymes. In DNA repair tests, methyl parathion was effective in inducing damage to the S. typhimurium strain TA1538 which lack excision repair compared to the strain TA1978 which is proficient in excision repair mechanisms. Normal laboratory light conditions had no effect on the mutagenicity tests, however, exposure of methyl parathion in the petri dish containing the tester strain TA100 and rat liver microsomal and cytosolic enzymes reduced the mutagenic activity and increased the toxic effects of methyl parathion.

In vivo induction of sister-chromatid exchange in Umbra limi by the insecticides endrin, chlordane, diazinon and guthion

Central mudminnows, Umbra limi, were exposed to the insecticides endrin, chlordane, diazinon and guthion at concentrations of 5.4 X 10(-12) M to 5.4 X 10(-9) M in the aquaria water. Endrin, chlordane and diazinon caused significant increase in the frequencies of SCE. The results of these tests in part are in contrast to previous work which did not find endrin to be mutagenic. Our results suggest that the in vivo SCE test is an efficacious method of detecting mutagenic pesticides in water.

Cytokinetic and cytogenetic effect of agricultural chemicals on human lymphoid cells in vitro. II. Organochlorine pesticides

Human lymphoid cells of LAZ-007 cell line, incubated with 10(-4) to 10(-6) molar of eight different organochlorine pesticides had dose related cytotoxicity, mitotic depression and cell cycle traverse inhibition. In cultures incubated with 10(-4) M concentrations, M1 metaphases were as high as 13% (Dicofol) as compared to less than 1% in the controls. The frequency of M3 metaphases in cultures incubated with 10(-6) M concentrations ranged from 11% (Chlordane) to 15% (Endosulfan) compared to 17% in control cultures. Statistically significant increase in SCE frequency was seen in cells exposed to Chlordane, Dicofol, Endosulfan and Toxaphene. On metabolic activation with rat liver microsomal S-9 enzymes, Chlordane, Dicofol and Tetradifon induced SCE frequency was higher than that of nonactivated cultures.

Cytokinetic and cytogenetic effects of some agricultural chemicals on human lymphoid cells in vitro: organophosphates

In the present study, cytotoxic, cytostatic and cytogenetic effects of a number of organophosphate pesticides on human lymphoid cells (LAZ-007) in culture have been examined. Cytotoxic effects were dose related and often led to extensive cell kill. The pronounced effects of various organophosphates on the cell-cycle traverse were shown in data based on the enumeration of M1 and M3 metaphases after incubation of cells with BrdU. In cells incubated with 20 micrograms/ml of the various chemicals, the number of M1 metaphases ranged from 6% (R-1303) to 18% (Azodrin) compared to no M1 metaphases in control cultures. The number of M3s in cultures treated with 20 micrograms/ml of the various chemicals tested varied from 0% (Phosdrin) to 7% (parathion) as compared to 17% in control cultures. 11 out of the 14 organophosphates tested, significantly increased the SCE frequency. Of the 9 chemicals tested after metabolic activation by liver microsomal S9 preparation, significant increases in SCE frequency were seen in diazinon-, dimethoate-, Dursban- and Phosdrin-treated cells.

An evaluation of the genotoxic properties of insecticides following plant and animal activation

Commercial and technical grades of 10 insecticides were evaluated for genotoxicity with Salmonella typhimurium and Saccharomyces cerevisiae directly and following plant and animal activation. Field-grade formulations of each insecticide were also tested for mutations at the waxy (wx) locus in Zea mays in situ. Carbofuran, chloropyrifos, curacron, metham and phorate were negative in all assays. Ethoprop and terbufos were each positive in 1 assay, and chlordane, fonofos and heptachlor were each positive in 2 assays. Fonofos and terbufos were positive directly and following animal activation while chlordane and heptachlor were positive following both plant and animal activation. Chlordane, ethoprop, and heptachlor were positive in Z. mays.

Induction of sister-chromatid exchanges and cell cycle delay in cultured mammalian cells treated with eight organophosphorus pesticides

Induction of sister-chromatid exchanges (SCE) and cell cycle delay in Chinese hamster cell line V79 after treatment with 8 organophosphorus pesticides (OPP) were studied. In addition, these effects were also studied using 1 of the 8 OPP in 2 human lymphoid cell lines. In V79 cells, 6 of the 8 OPP induced significant increase of frequencies of SCE and all the OPP induced various degrees of cell cycle delay. The 6 OPP in decreasing order of SCE induction are methylparathion, demeton, trichlorfon, dimethoate, malathion and methidathion. The 2 OPP that had no effect on SCE are diazion and disyston. The extents of induced cell cycle delay are generally related to the OPP concentrations but does not necessarily correlate with the extent of induction of SCE among the OPP studied. The results of studies on the effect of methyl-parathion on SCE and cell cycle delay in 2 human cell lines showed that both lines had significant and dose-dependent increase of SCE frequencies similar to those observed in V79 cells. In contrast to V79 cells, however, cell cycle delay was not as prominent in the human lines at comparable doses. These studies indicated that 5-bromodeoxyuridine labeling for analyzing SCE and cell cycle delay is a very sensitive method in assessing mutagenic potential of environmental compounds especially those that are highly toxic to and rapidly degradable in mammalian cells such as OPP.