EVALUATION OF CYTOTOXICITY OF DICHLORVOS PESTICIDE IN LABORATORY MOUSE

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2013 Vol. 2 JanuaryApril, pp.5155/veena Sahai EVALUATION OF CYTOTOXICITY OF DICHLORVOS PESTICIDE IN LABORATORY MOUSE *Veena Sahai Department of Zoology, G N Khalsa College, Mumbai *Author for Correspondence ABSTRACT An assessment of cytological and cytogenetic effects was undertaken using laboratory mice as an experimental model. Dichlorvos was tested employing micronucleus test, mitotic index and chromosomal abnormalities. The frequency of polychromatic (P) and normochromatic (N) erythrocytes and presence of micro nuclei in tested animals showed that this pesticide has distinct cytotoxic effects. The results of this study suggested that dichlorvos is a genotoxic agent. Analysis of the mitotic index both in the male and the female mice corroborated the result of micro nucleus test. The invivo evaluation of bone marrow chromosomes for the presence of chromosomal aberrations indicated that the pesticide induced structural abnormalities and with such abnormalities were distinctly higher in treated animals that in controls. On the basis of these observations it has been summarized that dichlorvos should be graded as cyto and geno toxic agent. Key Words: Mouse, Dichlorvos, Mitotic Index, Chromosomal Abnormalities, Cyto and Geno Toxic INTRODUCTION Today pesticidal drugs are playing an important role in enhancing the food production. The use of pesticides substantially reduces losses of food during various stages of food production storage and distribution. These measures have contributed in increasing production ion farm animals also but pesticides have been held responsible in increasing the toxic pesticide burden in animals owing to residues. Further residues of the pesticides through the food chain are translocated into other non target organisms including man. Many constituents present in the pesticide exert deleterious effects resulting in toxicity, pathological alterations, morbidity and mortality. These may affect the various stages of cell cycle and even cause profound genetic changes. There are numerous reports on the presence of pesticidal residues in agricultural produce, animal feed, milk, egg, fish, human tissue, etc. (Agnihotri, 1983; Rangaswami, 1983 and Goel, 1986). It has been established that certain pesticides or their metabolites cross the placental barrier and reach the neonate. Therefore, a study on the effects of pesticides on animals particularly from the standpoint of genotoxic effects assumes special importance. The objective of this paper is to focus on these changes, particularly cytotoxicity and chromosomal profile. MATERIALS AND METHODS The cytological and cytogenic effects of commonly used pesticide dichlorvos were studied in laboratory mouse (Mus musculous) which was used as an experimental model. Three dose levels 5, 10, 15 ppm were injected in the animals of both sexes which formed group 1, 2, 3. The animals of the group 4 were administered EMS150 and served as positive control. The fifth group was not given and treatment and served as control. Somatic chromosomes were prepared from the flushed bone marrow of the animals which were injected colchicin to arrest the cell division at metaphase stage. Chromosomal slides were prepared following the hypnotic treatment, air drying and staining with Giemsa. Bone marrow smears of the various groups were scored for the frequency micronuclei in the polychromatic (P) and normochromatic (N). The ratio of these was established. 51

2013 Vol. 2 JanuaryApril, pp.5155/veena Sahai The good metaphase plates were carefully examined for the incidence of chromosomal aberrations. The chromosomal anomalies were duly characterized. The data have been presented on mitotic index, incidence of micro nuclei and chromosomal aberrations in the tables. RESULTS AND DISCUSSION A preliminary assessment of cytological and cytogenic effects of the dichlorvos revealed that the ratio of polychromatic and normochromatic are almost identical in all the three treated groups which received progressively higher doses of pesticide but markedly different in the positive control group which was given EMS (150 ppm).ems is a known mutagen and a cytotoxic agent. The incidence of micronuclei was observed in the polychromatic and normochromatic cell which suggests a disturbance in mitotic cycle. Table 1: Frequency Of Micronucleus In Bone Marrow Erythrocytes Of Dichlorvos Treated Mice Group Dose (ppm) Total No of p. No of N. P/N ratio MN in P MN in n Overall frequency of counted No % no % with micronucleus (%) I 5 1172 571 601 0.95 NS 3 3 3 0.49 1 II 10 1185 568 617 0.92 N S 4 0.71 2 0.32 1 III 15 1143 548 595 0.92 NS 5 0.91 2 0.34 0.61 IV EMS 150 1230 493 737 0.67 * 16 3.24 11 1.49 3.01 ** V _ 1120 577 543 6 4 0.69 1 0.18 0.45 MN: Micronucleus; ** Significant At 1 % Level; * Significant At 5 % Level; NS: Non Significant Figure 1: Micronucleus test with Dichlorvos Mitotic activity was affected as was evident from the reduction in mitotic index in dichlorovos treated groups, the effect was dose dependent. 52

2013 Vol. 2 JanuaryApril, pp.5155/veena Sahai Table 2: Mitotic Index of Bone Marrow Cells of Mice Treated With Dichlorvos Drug Sex Group dose No of Mitotic index counted Dichlorvos Female I 5 2000 19 NS II 10 2000 18.15 NS III 15 2000 17.75 ** IV EMS 150 2000 10 ** V Untreated 2000 19.55 Male I 5 2000 18.85 NS II 10 2000 17.15 * III 15 2000 17.00 ** IV EMS 150 2000 9.75 ** V untreated 2000 19.65 ** Significant At 1% Level; * Significant At 5% Level; NS: Non Significant Figure 2: Mitotic index for dichlorvos treated mice The types of chromosomal abrasions which were scored included chromatid gaps, chromatid breaks, isochromatic breaks, acentric fragments,centromeric breaks and multiple gaps. Figure 3: chromosomal aberration test with dichlorvos 53

2013 Vol. 2 JanuaryApril, pp.5155/veena Sahai Table 3: frequency of chromosomal aberrations in dichlorvos treated mice group Dose Cell Total Type of chromosomal aberrations Sex (ppm) counted aberration CG CB ICG ICB ACF PULV POLY Female Male * Significant in 1% level I 5 200 II 10 200 III 15 200 IV EMS 150 200 V Untreated 200 I 5 200 II 10 200 III 15 200 IV EMS 150 200 V Untreated 200 6.5 NS (13) 7.5 NS (15) 8.0 NS (16) 67.00 ** (134) 3.5 (7) 7.0 NS (14) 7.5 NS (15) 8.5 NS (17) 7 ** (141) 5.0 (10) 4.0 (8) 5.5 (11) 35.5 (71) 3 (65) CENT B 1 (23) 9.0 (18) MULT GAP 1 (21) 16.5 (33) 54

2013 Vol. 2 JanuaryApril, pp.5155/veena Sahai The pesticide affects and cellular processes. However, the changes may remain imperceptible for a long time. It has been reported that certain pesticides on entering the body suppressed the mitotic activity of the. The decrease in the proliferation is sometimes dose dependent (Fahrig, 1974; Bruin, 1976; Manna and Vardhan, 1977 and Manna, 1986). The dichlorvos also exerted a mitoinhibitory effect on the bone marrow of the mice.the micro nucleus test is a vital indicator in the screening of cytogenetic effects (Doller and Schmid, 1970; Degraebe et al., 1979). Both polychromatic and normochromatic erythrocytes of the bone marrow exhibit the presence of the micronuclei. It was also established that micronuclei are legging fragments of the chromosomes affected by mutagen during erythropiosis. The publications on the damage to the morphology of the chromosomes as a result of the pesticide exposure are numerous. The frequency and type of abrasion presumably depends on the dose level and duration of exposure to the pesticide. (Hardel, 1979; Hardell and sandstorm, 1979; Czeizel et al., 1975) The presence of chromosomal abrasions affirms the clastogenic effect of dichlorvos. This study makes an endeavor to use multiple tests to assess the genotoxicity of dichlorvos. This approach is likely to surmount the possibility of false positive or false negative result encounteres when only one test system is used. REFERENCES Agnihotri NP (1983). Monitoring of pesticides residues in the environment. Pesticides Information 8 6480. Boller K and Schmid W (1970). Humangnetik 11 3554. Bruin A De (1976). Metabolism of organic agrochemicals in: biochemical technology of environmental agents. Elxevier/North Holland Biomedical Press 3. Czeizel A, Kiraly J and Ruzicska P (1975). Mutation Research 29 279. Degraeve N, Moutschen J, Moutschen DM, GilotDelhalle J, Colizzi Houbrechts N and Cholett MC (1979). Mutation Research 64 131. Fahrig R (1974). Chemical Carcinogenesis essays. Montessano R and Tomalis L Edition. International Agency for Research on Cancer 10 161181. Goel SC (1986). Introductory Remarks. Proceedings of Symposium in Pesticides Residency and Environmental Pollution Muzzarfarnagar 14. Hardell L and Sandstrom A (1979). British Journal of World Environment and Health 4 137150. Manna GK and Vardhan S (1977). Chromosome aberration in mice by the anifungal antibiotic nystatin. Experientia 33 306308. Manna GK (1986). Mouse bone marrow as a means of testing clastogenic agents. The Nucleus 29 141168. Rangaswami G (1983). Biodegradation of Pesticides. Pesticide Information 9 5563. 55