Indian Journal of Experimental Biology Vol. 44, July 2006, pp. 580-583 Erythrocyte antioxidant enzymes in toxicological evaluation of commonly used organophosphate pesticides Mohan Singh, Rajat Sandhir & Ravi Kiran* Department of Biochemistry, Panjab University, Chandigarh, 160 014, India Received 18 November 2005; revised 13 April 2006 Erythrocytes are excellent models for the study of interactions of xenobiotics with biomembranes. Present work is designed to study the in vitro effects of some organophosphates (ethion, chlorpyrifos, dimethoate and monocrotophos) on rat erythrocytes. Treatment of erythrocytes with organophosphates resulted in decreased erythrocyte glucose-6-phosphate dehydrogenase (G-6-PD) activity, whereas activities of glutathione-s-transferase (GST) and glutathione reductase (GR) were increased. Reduced Glutathione (GSH) content of RBCs was decreased after treatment with the pesticides. Increased activities of GST and GR were due to induction of natural defense mechanism of erythrocytes against the toxicity of the pesticides. Membrane bound enzymes like acetylcholinesterase (AChE), Na+-K+-ATPase and Ca2+-ATPase were also inhibited. Altered activities of these enzymes along with decreased GSH content indicate increased oxidative stress in erythrocytes after treatment with organophosphates. Keywords: Acetylcholinesterase, Erythrocytes, Glucose-6-phosphate dehydrogenase, Glutathione reductase, Glutathiones-transferase. Pesticides are used worldwide in agriculture in vast amounts each year. The more commonly used organophosphate pesticides are ethion, dimethoate, monocrotophos and chlorpyriphos. The widespread use of synthetic organic pesticides over decades has led to their frequent exposure in the environment1. Also, acute and chronic exposures of humans to pesticides occur during their commercial production and their application2. Synthetic pesticides are deliberately sprayed on crops or agricultural land to increase food production but these agrochemicals are not very selective in producing their effects3,4. They are toxic to many non-target species and contaminate the environment. Putative detrimental effects on life caused by pesticides should be known and minimized, most especially because of the extensive environmental distribution of these xenobiotics. Exposure to organophosphates leads to change in membrane permeability of erythrocytes5. To assess the detrimental effect of commonly used pesticides, antioxidant enzymes like glucose-6-phosphate dehydrogenase (G-6-PD), glutathione-s-transferase (GST), glutathione reductase (GR), ______________ *Correspondent author Phone: (0172) 2534133 Fax: (0172) 2541022 E-mail: [email protected] acetylcholinesterase (AChE), Na+-K+ and Ca2+ATPases and reduced glutathione content of RBCs have been studied in male Wistar rats. Materials and Methods Ethion, dimethoate, monocrotophos and chlorpyriphos (technical grade) were gifted by Punjab Pesticides Industrial Co-operative Society, Kharar (Punjab). Most of the biochemicals used in the study were purchased from Sigma Chemical Company, St. Louis, MO, USA or Sisco Research Laboratories Pvt Ltd., Bombay, India. All other chemicals used were of analytical grade obtained locally. Male albino rats (Wistar Strain) weighing 105120g were procured from the Central Animal House of the University. The blood was drawn from the tail vein of the animals. Blood samples from 6 animals were used to test the action of each pesticide and same number of matched controls were used. All the experiments performed were according to guidelines for use and care of laboratory animals and were approved by the ethical committee of the University. Preparation of erythrocyte hemolysate–– Erythrocyte hemolysate was prepared by the method of Lohr and Waller6. Blood (0.5 ml) was taken from the tail vein of rat into a graduated centrifuge tube containing 0.5 ml of anticoagulant. Tube was centrifuged at 1000 g, the buffy coat was removed SINGH et al.: ANTIOXIDANT ENZYMES IN TOXICOLOGICAL EVALUATION and the cells were washed twice with 5ml physiological saline. The sediment obtained was suspended in 1ml physiological saline and was properly mixed by rotation; 1ml of erythrocyte suspension was pipetted into a centrifuge tube and was mixed with 1ml double distilled water, 0.7 ml triethanolamine buffer (pH 7.5) and 0.3 ml digitonin solution (1g/100ml). The mixture was allowed to stand for 15 min in a refrigerator at 4°C and was then centrifuged at 1000 g for 15 min. The insoluble material was discarded. Glucose-6-phosphate dehydrogenase (G-6-PD), glutathione-s-transferase (GST) and glutathione reductase (GR) were assayed by the standard methods. Reduced Glutathione (GSH) content was measured by the method of Jollow et al7. Erythrocyte membranes were prepared by hemolysing the erythrocytes in distilled water and centrifuging at 20,000 g. Post hemolytic residue was washed twice with 1 mM Tris EDTA (pH 7.4). Erythrocyte membranes were kept frozen at -80°C. Acetylcholinesterase(AChE)8, Na+-K+ and Ca2+ATPases9 activities were assayed in the membrane preparation. Protein content was measured by the method of Lowry et al10. Statistical analysis––Data presented in this study was statistically evaluated by Student’s t test. Differences between two comparable sets of results were considered significant when P≤0.05. Results and Discussion AChE activity is useful as an indicator of the inhibition by organophosphates and in vitro treatment of organophosphates in the present study resulted in significant decrease in the erythrocyte AChE activity. Treatment of dimethoate, chlorpyrifos, ethion and monocrotophos resulted in approximately 90% decrease in AChE activity in each case (Table 1). The decrease was found to be statistically significant (P≤0.001).The inhibition in the activity of AChE in vitro may be due to direct interaction of pesticide with the enzyme as is known in the case of ethion, chlorpyrifos, dimethoate and monocrotophos. In vitro inhibition of AChE by pesticides is well documented11-13. There are cases of in vitro inhibition of AChE from four marine species by organophosphates14. Results of in vitro treatment of various organophosphates on Na+-K+-ATPase have been presented in Table 1. In vitro treatment of rat erythrocytes with all the four organophosphates resulted 581 582 INDIAN J EXP BIOL, JULY 2006 in decreased activity of Na+-K+-ATPase. A decrease ranging from 12 to 75% in the enzyme activity was observed in case of different pesticides. The decrease was found to be statistically significant for dimethoate, chlorpyrifos and ethion. Earlier work from our laboratory showed that in vivo administration of various pesticides decreases the activity of Mg2+-ATPase15,16. In the case of Ca2+-ATPase 22 to 57 % decrease was observed in the enzyme activity by dimethoate, monocrotophos, chlorpyrifos and ethion treatment (Table 1). All the results were found to be statistically significant (P≤0.001). Yang et al.17 reported the inhibition of Ca2+-ATPase in the muscle cells following dimethoate exposure. It has been shown that Ca2+-ATPase of human erythrocytes is inhibited with various compounds of toxicological significance mostly chlorides18. The results of various organophosphates treatment on erythrocyte G-6-PD activity have been presented in Table 1. Dimethoate, ethion, chlorpyrifos and monocrotophos treatment resulted in 26 to 40 % decrease in G-6-PD activity. The decrease was found to be statistically significant (P≤0.001). G-6-PD is an important enzyme of hexose monophosphate shunt and its function in the mature RBCs is to generate NADPH, which is required for the conversion of oxidized glutathione to reduced glutathione, that in turn is necessary for membrane integrity of erythrocyte membranes19. This might be the possible reason for the increased fragility of erythrocytes upon treatment with different organophosphates as reported during the earlier work done in our laboratory that in vivo administration of various pesticides results in decrease in the activity of G-6-PD15, 16. The data presented in Table 1 demonstrated the effect of various organophosphates on GR activity of rat erythrocyte hemolysate. It was observed that the administration of dimethaote, chlorpyrifos, ethion and monocrotophos resulted in 16 to 46% increased activity of erythrocytes GR. The increase was statistically significant, for dimethoate, chlorpyrifos and ethion. Thus increased activity of this enzyme appears to be defense against pesticide toxicity in erythrocytes. Earlier work showed that in vivo administration of various pesticides results in decrease in the activity of GR15, 16. The results presented in Table 1 depict the effect of the in vitro treatment of various organophosphates on erythrocyte GST activity. It is clear from the data that [ treatment with all the pesticides results in increased GST activities. The increase was statistically significant in the case of chlorpyrifos and dimethoate. GSH and glutathione dependent enzyme systems provide major protection against toxic agents20. Among them GST is the most important phase II drug metabolizing enzyme21. Effects of administration of various organophosphates on erythrocyte GSH content has been presented in Table 1. In vitro treatment of erythrocytes with dimethoate, chlorpyrifos, ethion and monocrotophos resulted in decreased GSH content in all the cases. Decreased GSH content might be attributed to the decrease in G-6-PD activity of the erythrocytes observed in the present study. Decrease G-6-PD activity results in the decreased synthesis of NADPH, which in turn results in the low levels of GSH. It is well documented in literature that in vivo administration of various xenobiotics results in decrease in GSH content of erythrocytes22-23, but not many reports are available about in vitro effects of pesticide on glutathione content of erythrocytes. Based on our results it is concluded that the organophosphates tested exert differential effect on the activity of antioxidant enzymes, glutathione and membrane bound enzymes which may be useful in their toxicological evaluation. References 1 2 3 4 5 6 7 Barbash JE & Resek EA, Pesticides in ground water: Distributions, trends, and governing factors (CRC Press, Boca Raton, FL)1996, 588. 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