Nahid S, Kazem P, Mehrdad S, Afshin Z, Sahar M, Mohsen F, Mohammad F, Sara A. Effect of Oxydemeton Methyl Toxin on Hormones Testosterone and Dihydrotestosterone in Adult Male Rats. Biomed Pharmacol J 2015;8(1)
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Syahmard Nahid1*, Parivar Kazem1 , Shariati Mehrdad1, Zare Afshin1 , Mohammadi Sahar2, Farzam Mohsen1 , Farzam Mohammad1, and Azhdari Sara2

1Department of Physiology, Medical School, Kazerun Branch, Islamic Azad University, Kazerun, Iran. 2Department of clinical Biochemistry,Kermanshah University of Medical Sciences,Kermanshah,Iran.   Corresponding Author Email :dr.syahmard@yahoo.com

DOI : https://dx.doi.org/10.13005/bpj/609

Abstract

Every year lots of different pesticides  through various ways go to the environment . These pesticides are distributed to the environment and transported to the remote areas . To predict the effects of these substances on the ecosystem, in addition to information on their toxicity, how to enter, play and behavior of these compounds in nature should be well known . The purpose of this study was to determine the effect of oxydemeton methyl  toxin on hormones testosterone and dihydrotestosterone  in rats . For this purpose, 40 adult male Wistar rats, weighing approximately gr  were divided into 5 groups of 8 . The groups include : Control group , sham and treatment with doses 2ppm , 5ppm , 10ppm . Poison was fed to the animals orally daily for 14 days . At the end of the experimental period, animals were weighed, blood sampling was performed , and Blood samples were centrifuged to obtain serum and until hormone measurements was performed , it was frozen at the temperature of - 20 ° C . Concentration of hormone testosterone by RIA method and dihydrotestosterone by ELISA method were measured . The results of this study showed that use of oxydemeton methyl toxin in maximum for 14 days , causes significant decrease in concentration of hormones testosterone and dihydrotestosterone P<0/05 . Probably , this toxin with effect on thyroid hormones causes secretion decrease of hormones testosterone and dihydrotestosterone .So it causes reduction in male fertility . Thus the use of this toxin must be done in accordance with Safety Tips .

Keywords

Oxydemeton methyl; Testosterone; Dihydrotestosterone; Male rat

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Nahid S, Kazem P, Mehrdad S, Afshin Z, Sahar M, Mohsen F, Mohammad F, Sara A. Effect of Oxydemeton Methyl Toxin on Hormones Testosterone and Dihydrotestosterone in Adult Male Rats. Biomed Pharmacol J 2015;8(1)

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Nahid S, Kazem P, Mehrdad S, Afshin Z, Sahar M, Mohsen F, Mohammad F, Sara A. Effect of Oxydemeton Methyl Toxin on Hormones Testosterone and Dihydrotestosterone in Adult Male Rats. Biomed Pharmacol J 2015;8(1). Available from: http://biomedpharmajournal.org/?p=1580

Introduction

Until yet more than one hundred thousands of phosphate compounds have been known that 100 species are pesticides . Among the different properties of these compounds , we can mention toxic effects to mammals, the strength of the solubility and different stability in the environment . This group of compounds have many applications in health and agriculture and it can influence through contact, ingestion and inhalation on humans and other organisms (3) .  In the last 50 years Pesticides have been an essential component of the agricultural world . Although production and distribution of pesticides improves the quality and efficiency of agricultural but the probability of unreasonable use is very high . One of the most important concerns of the World Health Organization, is the indiscriminate use of pesticides in agriculture . Contact with insecticides have been as a major health problem in many rural areas (1) . Phosphorus pesticides are the most diverse toxins (2) . Effects of organophosphate compounds are as both acute and chronic that the most important problems of organophosphates are acute problems that it causes at least some symptoms of diseases and stimulate the parasympathetic nervous system . If the contact time with these compounds is short without the appearance of any symptoms , cholinesterase levels would decrease , and occasionally headaches and flu-like symptoms can be observed that it is due to the accumulation of acetylcholine in the brain receivers (3) . Generally all organophosphate pesticides are able affect structure and function of DNA (4 and 6) . Organophosphate pesticides after sorption in body , have many reactions of biotransformation . Because Organophosphate compounds are lipophilic ,they are easily permeable in the skin . Mainly biotransformation reactions go  towards the formation of polar compounds until they can dispose through kidney . Organophosphorus compounds in biological terms, may alter to some metabolites that its toxicity is certainly changes (5) . Oxy dimethyl toxin with brand name metasystux-R , more than 85-90% are Phosphoinositide thiol that 10-15% of it is not known yet . There are different combinations of demeton  with features and various formulas (7) . Possible side effects of using this toxin can be as follow : Increased eye secretion, increased salivation, diarrhea, coughing and breathing slow (difficult breathing), vomiting, abdominal twist, anesthesia, congestion throughout the body , Bleeding in cardiac, bleeding in the stomach, intestine congestion and inflammation, pulmonary edema, pulmonary high secretion and high salivary secretion (7) . According to the above and the widespread use of these pesticides without considering their effects on changes in sex hormones (testosterone and dihydrotestosterone) and according to this fact that in relation to the effects of this toxin on changes of sex hormones testosterone and dihydrotestosterone  no study has been done , so this research project is necessary.

Materials and Methods

This study experimentally and is completely random. All ethic about laboratory animals have been done . 40 Wistar male rats weighing 190 ± 10% gr and age of 2/5-3 month were provided from the breeding center of laboratory animals of islamic azad university of Kazeroon branch . Rats were placed in animals house in Kazeroon islamic azad university for 14 days in laboratory conditions including temperature of 20 ± 5 ° C and cycle of 12 hours light and 12 hours dark . The Rats were kept in cages with metal mesh doors and were using standard diet (pellete) . water with especial glass bottles were giving to them . Cage 3 times a week was disinfected with 70% alcohol . Method of preparation and administration of the oxydemeton methyl is as follow . Main solvent is water and in this research preferably used distilled water and were prescribed orally (8 , 9 , 10) . Therefore, each animal was considered a dark glass container . In order to reduce the error probability , poison were weighed daily and with 2 ml of distilled water was poured into a glasses . Toxin was fed to the animals with especial needle . The rats were divided randomly into 5 groups of 8 that include.

  1. Control group (A) , includes 8 animals that did not receive any treatment , but all conditions were similar to other groups .
  2. Injection group (B) , includes 8 animals thatdaily2 mlof distilled waterreceived orally .
  3. Experimental group with the minimum amount of toxin (C1) , including 8 animals that daily 2 ppm oxydemeton methyl toxin dissolved in distilled water with the final volume 2 ml received orally .
  4. Experimental groupwitha moderate amount oftoxin (C2) , including 8 animals that daily 5 ppm oxydemeton methyl toxin dissolved in distilled water with the final volume 2 ml received orally .
  5. Experimental group with a maximum amount of toxin (C3) , including 8 animals that daily 10 ppm oxydemeton methyl toxin dissolved in distilled water with the final volume 2 ml received orally .

After 14 days period , rats of all groups after weighing were anesthetized by ether and from their heart by 5 cc syringe blood samples were collected and after separation of blood serum , concentration of hormones testosterone by RIA method and dihydrotestosterone by ELISA method in laboratory of  medical science university of Kazeroon was performed . One-way ANOVA for comparison between treatments and followed by t-test and Duncan test was used for multiple comparisons between groups . (P<0.05) was significant level . Data analysis and statistical testing was performed using SPSS, version 17 .

Results

Mean testosterone concentrations with standard errors for the different groups is shown in (Table 1) . Also it shows changes in hormone concentrations with standard errors in various groups . The mean concentration of hormone testosterone in the experimental groups with the average ,  minimum , and maximum of toxin did not show a significant increase in the level of P<0.05 compared to control group. The mean concentration of hormone testosterone in experimental group with the maximum of toxin shows significant increase in the level of P<0.05 compared to control group (Table 1) . The mean concentration of hormone DHT with standard errors for different groups shows in table (1) . Also it shows mean concentration of hormone DHT with standard errors in different groups . The mean concentration of hormone DHT in maximum dose shows significant increase in the level of P<0.05 compared to control group (table 1) .

Table 1 : Mean concentrations of hormones testosterone and dihydrotestosterone in different experimental groups

Hormone dihydrotestosterone (ng/dL) Hormone testosterone (nmol/L)
31/57±2/48 3/21±0/252 Control
32/23±1/50 3/28±0/42 Sham
30/28±2/12 3/01±0/527 The minimum amount of toxin

2ppm

2/44±1/15 2/91±0/329 The moderate amount of toxin

5ppm

*21/14±1/03 *1/56±0/127 The maximum amount of toxin

10ppm

 

Significant difference is P<0.05 level and the number of samples in each group is n=8 . The sign of * indicate a significant difference with the control group .

Discussion

According to Table 1, the mean concentration of testosterone in control and injection sham groups did not show significant difference . Probably injection of distilled water has no effect on serum concentration of hormone testosterone . Moreover, according to Table 1, the mean concentration of hormone testosterone in the experimental groups with minimum and moderate amount of toxin , did not show significant decrease compared to control group . But , with the maximum amount of toxin it shows significant decrease compared to control group . This decrease is consistent with the results of some researchers (11-16) and Significant differences can probably be explained by the following reasons . This toxin causes damage or reduction of various liver enzymes that some function of enzymes involved in synthesis of androgens especially testosterone , with consumption of this toxin would reduce . Oxydemeton methyl can decreases level of synthesis of hormone thyroxine and it  increases  clearance of hormone thyroid (17 , 18) . Decrease in thyroid hormones, would  cause decrease the basic level of testosterone . This effect is due to these reasons : decrease production of testosterone by testis tissue in response to GnRH and hCG , decrease response of “Testicula interstitial cells ‘ to the gonadotropins ,and decrease production of CAMP and calcium entry into the cells (19 , 20) . Since the mechanism of peptide hormones such as LH and FSH activates adenylate cyclase and increase CAMP in target cells (21) , decrease of thyroid hormones would causes decrease of testosterone . According to Table 1, the mean concentration of hormone DHT between control and sham groups did not show significant differences , and this is because injection of distilled water did not has any effect on serum concentration of DHT compared to control group . Since DHT is the main metabolite of testosterone, it can be reduced due to decrease of  testosterone  that  its mechanism described above.

Conclusion

According to the results, it can be stated that probably this toxin with effect on hormone thyroid and effect on adenylate cyclase system and increase of CAMP in target cells , it would cause decrease of testosterone and the reduction of testosterone is bound to decrease of dihydrotestosterone . This is because this hormone is precursor of testosterone.

References

  1. Najafi GH, Salame S, Karimi A. Effects of diazinon on adult mouse testis in rats: histopathological study. Medical Journal of Urmia, 2010; 20 (4): 313- 319.
  2. Rakhshani E, Talebi AA, Taheri AH. Principles oftoxicology agricultural. Publicationsdictionary; 2006; 156- 177. [ text in persian ].
  3. Brealy CY,Walker GH, Bladwin BC. Esterases activities in relation on the
  4. Janusz B, Pawel J, Andrzej T, Krzysztof S. In vitro studies on the genotoxicity of the organophosphorus insecticide malathion and its two analogues. Genetic Toxicology and Environmental Mutagenesis, 1999; 445 (2): 275-283.
  5. Jokanovic M. Biotransformation of organophosphorus compounds.toxicology, 2001;166(3):139-160.
  6. Dutta HM, Maxwell LB. Diazinon induced  endocrine  disruption  in  bluegill, sunfish, Lepomis macrochirus. Ecotoxicology and environmental safety, 2003; 60: 21-27.
  7. 7 . Arjangi s . Guide the use of pesticides and chemical principles of safety against pests and plant diseases. Of parks and green space , 1391 ; s 1-5 .
  8. Meyer, DC. Eadens, DJ.1985. The role of endogenous serotonin in phasic LH release, 15, P:283-286.
  9. Khodam , r. 1382. The generic drugs, Didavr Press, Third edition, Tehran , s:310-330 .
  10. Katzong , terror. 1381. Basic and Clinical Pharmacology, Tamerlane Publisher , s:420-487
  11. Gromo,U J. Weinbauer, GF. Sinioni, M. Nieschldg, E. 1993. Effects of antiandrogens and ethane dmethane sulphonate (EDS) on gene expression, free subunits, bioactivity and secration of pituitary gonadotrophins in male rats, Mol. Cell. Endocrinol. 9, P:119-125.
  12. Mahoudeau, JA. Corvot, P. Valcke, JC. Menard, J. Bricaire, H.2001. Antiandrogenic effect of Oxydemeton methyl, Endocrinol. 37, P:57-58.
  13. Sabbieti, MG. Marchetti, L. Menghi, G. Yamamoto, K. Kihuyama, S. Vaudry, H. Polzonetti-Magrii, A.2003. Occurrence of beta-endorphin binding sites in the pituitary of the frog Rana esculenta: effect of beta-endorphin on luteinizing hormone secretion Gen. Co. Endocrinol. 132, P:391-398.
  14. Sciarra, F. Toscano, V. Concolino, G. Di Silverio, F.1999. Antiandrogens: clinical applications, J. Steroid. Biochem. Mol. Biol. 20, P:349-
  15. Shen, R. Lin, MC. Sadeghi, F. Swerdloff, RS. Rajfer, J. Gonzalez-Cadavid 1996. Androgens are not major down-regulators of androgen receptor levels during growth of the immature rat penis J.Steroid. Biochem. Mol. Biol.;57, P:301-13.
  16. Subhedar, NK.2005. Androgenetic Alopecia in men and women: an overview of cause and treatment, Endocrine, 28, P: 165-170.
  17. Ronald, M. Lechan, T. 2004. Functional anatomy of the hypothalam us and pituitary, P:150-158.
  18. Lagu, SK. Bhavsar, NG. Sharma, RK. Ramachandran, AV.2005. Neonatal hypothyroidislm- induced changes in rattestis size, dependence on temperature, Neuro. Endocrinol. Leti.28,P:780-788.
  19. Przekop, F.Tomaszewska-Zaremba, D. Mateusiak, K. 2007. The involvement of GABA(A) receptors in the control ofGnRH and beta-endorphin release, and catecholaminergic activity in the ventromedial-infundibular region of hypothalamus in anestrous ewes, 52, P:489-500
  20. Simpkins, JW. Kalra, SP. Kalra, PS.1998. Variable effects of testosterone on dopamine activity in several microdissected regions in the preoptic area and medial basal hypothal amus, Endocrinology, 112, P: 665-669.
  21. Shohn, EH. Wolden-Hanson, T. Matsumoto, AM.2002. Testosterone (T)-induced changes in arcuate nucleus cocaine-amphetamine-regulated transcript and NPY mRNA are attenuated in old compared to young male brown Norway rats: contribution of T to age-related changes in cocaine-amphetamine-regulated transcript and NPY gene Expression Endocrinology, 143, P:954-663.
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