CHANGES IN TESTIS PROTEIN AND METABOLIC ENZYME ACTIVITIES IN RATS INDUCED BY EPICHLOROHYDRIN
HTML Full TextCHANGES IN TESTIS PROTEIN AND METABOLIC ENZYME ACTIVITIES IN RATS INDUCED BY EPICHLOROHYDRIN
K. Muthu 1, S. Thirukannan 2, K. Karthikeyan 3, P. Ilansuriyan 2 and M. Marimuthu * 3
Department of Biotechnology 1, J. J College of Arts & Science, Puthukottai - 622404, Tamil Nadu, India.
Nutraceutical Chemistry Lab 2, Department of Food Process Engineering, School of Bioengineering, SRM University, Kattankulathur - 603203, Tamil Nadu, India.
Research and Development Division 3, AquAgri Processing Private Limited, B5, SIPCOT Industrial Complex, Manamadurai, Sivaganga - 630606, Tamil Nadu, India.
ABSTRACT: In the present study, an attempt was made to evaluate the changes in testis protein and metabolic enzyme activities induced by epichlorohydrin (ECH), twenty-four albino male rats were divided randomly into four groups of six rats each. One group was left untreated as controls, and the other three groups were administered, respectively, for twelve consecutive weeks, (2) 50 mg of ECH /kg/b.wt, (3) 75 mg of ECH /kg/b.wt and (4) 100 mg of ECH /kg/b.wt. In comparison with the control group, the doses of ECH (75 mg/kg/b.wt and 100 mg/kg/b.wt) resulted in lower protein levels and higher lactate dehydrogenase (LDH) activities in the testis of male rats than in control rats. The activity of gamma-glutamyl transpeptidase (γ-GT) decreased significantly at the doses of ECH (75 mg/kg/b.wt and 100 mg/kg/ b.wt) group than in the ECH (50 mg/kg/b.wt) and control group. However, a significant reduction in the activities of Na+/K+- , Mg2+-and Ca2+-ATPases in the (75 mg/kg/b.wt and 100 mg/kg/b.wt) ECH treated animals than control rats. Therefore, these changes in testis protein and spermatogenesis-dependent enzymes undoubtedly affect the physiological functions of the testis, which may thereby cause low sperm motility.
Keywords: |
ATPases, Enzyme activities, Epichlorohydrin, Gamma-glutamyl transpeptidase, Male rats, Testis enzymes, Testis protein
INTRODUCTION: Increasing attention to recent trends in declining reproductive health, especially the alarming decrease in male fertility rate worldwide, has led to the 21st century being dubbed the century of reproductive health 1. Epichlorohydrin does not occur naturally in the environment. It is manufactured commercially from chlorine and propylene, or hydrochloric acid and natural glycerine derived from biodiesel.
It is also used in the manufacture of elastomers, glycidyl ethers, cross-linked food starch, wet strength resins for the paper industry, water-treatment resins, surfactants, ion-exchange resins, plasticizers, dyestuffs, pharmaceutical products, oil emulsifiers, lubricants and adhesives 2. Epichlorohydrin is absorbed rapidly via the skin, gastrointestinal tract, and, in vapor form, via the lungs. It is distributed widely throughout the body. In rats, most absorbed epichlorohydrin is metabolized rapidly, partly to carbon dioxide, which is excreted via the lungs, and partly to urinary metabolites, mainly conjugates 2.
Epichlorohydrin is a bifunctional alkylating epoxide 3. It causes delayed erythema, edema, papules along with burning, and itching when the liquid comes in contact with the skin 4; contact dermatitis has been reported after occupational exposure to epichlorohydrin 5. Epichlorohydrin induced antifertility effects in male rats resembling those induced by alpha-chlorohydrin after a single oral or intraperitoneal dose of 50 mg/kg body weight 6. In male rodents, exposure to epichlorohydrin induced sterility 6-9.
It is known, for example, that high doses of ECH adversely affect male reproduction function 10. Thus, an investigation not only focusing on the effects of ECH exposure on male reproduction alone but also measuring their interactive effects on the male reproductive system might prove helpful in determining potential causes of impaired reproductive functions in male rats. Previous investigations have revealed that the ECH causes lower sperm motility in male rats11and that ECH affects male reproduction through altering testis mass, cellular morphology and normal spermatogenesis 12, 13.
Protein and metabolic enzymes, such as lactate dehydrogenase (LDH) and adenosine triphosphatases (ATPases), are important for the normal function and development of the testis and sperm motility 14-17. In the present study, we investigated changes in total protein and spermatogenesis-dependent enzymes in the testis to explore possible pathways of decreased sperm motility and altered levels of serum testosterone induced by ECH 18.
MATERIALS AND METHODS:
Experimental Animals: Twelve-week-old adult albino male rats weighing between 150-200 g, along with supplies of their standard diet, were obtained from animal house center of “Jawaharlal Nehru Institute of Post Graduate Medical Educations and Research” (JIPMER), Pondicherry.
Establishment of Animal Model: As in our recent reports 11, 19 twenty-four of the above male rats were randomly divided into four groups of six rats each: (a) a control group, which was given distilled water and clean air; (b) a ECH group, to which 50 mg/kg/b.wt was administered in their drinking water; (c) a ECH group, to which 75 mg/kg/b.wt was administered in their drinking water and (d) a ECH group, to which 100 mg/kg/b.wt was received in their drinking water. All rats were maintained on standard diets, water ad libitum under standard temperature (22-25 °C), 12/12-hr light/dark cycle, ventilation, and hygienic conditions. At the end of the weeks, each group was sacrificed for further study.
Assay of Protein and Enzymes Activities in Testis: After twelve weeks, the experimental rats were sacrificed by cervical dislocation, and the right tests were quickly collected, weighed, and then homogenized with 1:9 (w/v) 0.9% saline solution at 0- 4 °C. Total protein content and the activity of the gamma-glutamyl transpeptidase (γ-GT), lactate dehydrogenase (LDH), and ion-activated adenosine triphosphatases (ATPases) in testis tissues were determined by Vivek laboratories, Nagarkovil, Tamil Nadu, India and with the enzyme reagent kit provided by the Nanjing Jianchen Biological Institute, China.
RESULTS: In the present study, an attempt was made to investigate the effect of epichlorohydrin, on testis of adult albino male rats. The protein level was significantly (p<0.05 p<0.01) decreased in testis after the treatment of epichlorohydrin (75 mg/kg/b.wt and 100 mg/kg/b.wt) when compared to the control rats. No significant variations were observed in epichlorohydrin (75 mg/kg/b.wt) treated groups as compared to control groups Table 1 and Fig. 1. At the end of ECH (75 mg/kg/b.wt and 100 mg/kg/b.wt) treatment, the activities γ-GT activity significantly (p<0.05 p<0.01) decreased in testis than control rats. But, did not observe any significant changes in the epichlorohydrin (50 mg/kg/b.wt) treated patients when compared to control rats Table 1 and Fig 1.
The significantly (p<0.05, p<0.01) increased in the LDH activity in testis after epichlorohydrin (75 mg/kg/b.wt and 100 mg/kg/b.wt) treated rats as compared to control. But, did not observe any significant variations in the epichlorohydrin (50 mg/kg/b.wt) treated animals Table 1 and Fig 1. The data showed significant (p<0.05; p<0.01) reduction in testis in the activities of Na+/K+ -ATPases, Ca2+-ATPases and Mg2+ -ATPases by epichlorohydrin (50 mg/kg/b.wt, 75 mg/kg/b.wt and 100 mg/kg/b.wt) treatment when compared to control rats Table 1 and Fig 1.
TABLE 1: TOTAL PROTEIN CONTENT AND ACTIVITIES OF Γ-GT, LDH, AND ATPases IN TESTIS TISSUES OF MALE RATS AFTER ECH TREATMENTS (n=6, mean ± SD)
Groups | Total protein
(g /L) |
γ – GT
(U/g protein) |
LDH
(U/g protein) |
Na+/K+ -ATPase
(μmol Pi/mg protein/hr) |
Ca2+ -ATPase
(μmol Pi/mg protein/hr) |
Mg2+-ATPase
(μmol Pi/mg protein/hr) |
Control | 0.71 ± 0.03 | 0.62 ± 0.09 | 10.27 ± 0.35 | 6.01 ± 0.70 | 2.50 ± 0.23 | 2.14 ± 0.19 |
ECH
(50mg/kg /b.wt) |
0.59 ± 0.03* |
0.69 ± 0.06 |
10.58 ± 0.38 |
4.40 ± 0.52* |
1.84 ± 0.21* |
1.58 ± 0.09* |
ECH
(75mg/kg /b.wt) |
0.57 ± 0.05* |
0.58 ± 0.03 |
11.32 ± 0.89 |
4.19 ± 0.11† |
1.57 ± 0.21† |
1.53 ± 0.19* |
ECH
(100mg/kg /b.wt) |
0.56 ± 0.03* |
0.47 ±0.04* |
14.27±1.67* |
3.69 ± 0.21† |
1.79 ± 0.19† |
1.36 ± 0.16† |
Note: *P<0.05; †P<0.01 compared with the control group.
DISCUSSION:
Effect of ECH on Testis Protein Metabolism of Male Rats: Earlier studies have reported that a dose-dependent decrease in protein level in the spermatozoa and reproductive organs of ECH-treated animals 14, 17, 20-24. In this study, the total protein levels in the testis of male rats were significantly (P<0.05) decreased in the ECH (75 mg/kg/b.wt) Group after 12 weeks of ECH treatment when compared to control rats. The mean total protein content over the entire 12-week period was slightly lower in the ECH (50 mg/kg/b.wt) group but was drastically (P<0.05) decreased in the ECH (100 mg/kg/b.wt) groups. These results clearly suggest that the ECH leads to lower testis protein content than the control group.
FIG. 1: TOTAL PROTEIN (g/L) CONTENT AND ACTIVITIES OF γ-GT (U/g protein), LDH (U/g protein), AND ATPases (μmol Pi/mg protein/hr) IN TESTIS TISSUES OF MALE RATS AFTER ECH TREATMENTS. EACH COLUMN REPRESENTS THE MEAN ± SE. *P<0.05; **P<0.01; COMPARED WITH CONTROLS
Gamma-glutamyl transpeptidase (Gamma-glutamyltransferase, γ-GT), is the key enzyme in the γ-Glutamyl cycle, and plays a vital role in the absorption, transport, and synthesis of amino acids and proteins 25. The activity of γ-GT decreased significantly (P<0.05) in ram semen with ingestion of 20 to 200 μmol NaF/L has been reported 17. In the present study, γ-GT activity in the ECH group decreased significantly in the (75 mg/kg/b.wt) treated group and then dramatically (P<0.05) decreased in the (100 mg/kg/b.wt) treated group when compared to control rats. Nevertheless, it can be concluded that both protein metabolism and synthesis in testis of male rats is affected by ECH (75 mg/kg/b.wt + 100 mg/kg/b.wt) treated rats and the influence of ECH on the γ-glutamyl cycle may be responsible for a reduction in testis protein of male rats. The reduction in testis proteins may also be due to the interference of ECH with the binding of the aminoacyl-t-RNA adducts to the ribosomal RNA template, which would then inhibit biosynthesis of protein in testis 14.
Effect of ECH on Testis Metabolic Enzyme Activities of Male Rats: Lactate dehydrogenase (LDH) and ion-activated adenosine triphosphatases (ATPases) are important for spermatogenesis and testicular metabolism 15, 16. Many studies have indicated that the activity of these enzymes decreases in testes of ECH-treated animals 14, 17, 20. In our study, LDH activities increased in the ECH (75 mg/kg/b.wt + 100 mg/kg/b.wt) treated groups for 12 weeks. These results are in accord with those obtained by Zakrzewski et al., 17 when they went from lower to higher concentrations of ECH in treating rat sperm samples 23. Furthermore, the mean values for the entire 12-week period were significantly (P<0.05) increased in the three treatment groups when compared to control rats. These findings indicate that the interaction of ECH can result in higher LDH activity than control animals.
On the other hand, our observations over time show that the activities of Na+/K+- ATPase, Ca2+-ATPase, and Mg2+-ATPase at week 12 in the three treatment groups all decreased significantly (P<0.05) as compared to control rats. It has been reported that the toxic effect of ECH on reproduction is due to the inhibition of many enzymes, particularly those whose cofactor is the cation of a bivalent metal 18. It is likely, therefore, that some of the deceased enzyme activity found in the present study is the result of damaged testis tissue 26. However, others have reported that a lower dose ECH can increase enzymes activity by a positive feedback mechanism 23. Alternatively, the changes in testis metabolic enzyme activities of male rats may be related to both the dose and duration of ECH intoxication. Likewise, ECH, which are in-vivo metabolic products of alkylating agent/ chlorinated hydrocarbon inhalation, can inhibit or activate the activity of certain enzymes by inducing the production of free radicals 27. In any case, it is evident that with exposure to ECH various types of lesions were likely to result. It should be noted, however, that LDH, which is regarded as a marker of carbohydrate metabolism of germ-cell production and differentiation 15 plays a key role in the process of energy supplementation for spermatozoa motility 17.
CONCLUSION: ATPases, including Na+/K+-, Ca2+-, and Mg2+-ATPase, play a key role in the exchange of metabolites between Sertoli and developing germ cells and are markers of the metabolic state of germinal epithelium 28. The changes in these enzymes will undoubtedly affect physiological function in the testis, which may cause a significant decline in sperm motility 10. Nevertheless, the exact alterations in testis physiological function caused by ECH are not clear, and histological and ultra-structural studies are called for to illuminate this aspect. In conclusion, both ECH treatments alter testis protein and the activity of some enzymes in male rats, and these changes may be one of the pathways that lead to low sperm motility.
ACKNOWLEDGEMENT: Authors are wishing to thank the Management of J. J. College of Arts and Science, Pudukottai for providing the facilities.
CONFLICT OF INTEREST: Nil
REFERENCES:
- Zhang Y Environmental pollution threatens human fertility. Environ Rev 2003; 22: 20.
- Gardiner TH, Waechter JM and Stevenson DE: Patty’s Industrial Hygiene and Toxicology, New York 1993.
- Shram RJ, Cherna M, Fernandez SI, Kochisova I, Kodytkova I, Novakova J, Roessner B, Siskova A and E Topinkova: Mutat Res 1981; 85: 287-288.
- Laskin S, Sellakumar AR, Kuschner M, Neson N, Mendola LA, Ruch GM, Katz GV, Dulak NC and Albert RE: Natl Cancer Inst 1980; 65: 751.
- HSE (Health and Safety Executive): AIDS and the work place. 1990: 30.
- Jones AR, Davies P, Edwards K and Jackson H: Nature (Lond.) 1969; 83: 224.
- Hahn JD: Nature (Lond.) 1970; 87:
- Esch GJ and Van: National Institute of Public Health 1981.
- John JA, Quast JF, Murray FJ, Calhoun LG and RE: Toxicol Appl Pharmacol 1983; 68:
- Toth GP, Zenick H and SH Smith: Fund Appl Toxicol 1989; 13: 16.
- Zhang JH, Liang C, Ma JJ, Niu RY and JD: Fluoride 2006; 39: 126-31.
- Cooper ERA, Jones AR and Jackson H: J Reprod Fert 1974; 38: 379-386.
- Kluwe WM, Gupta BN and Lamb JC: Toxicol Appl Pharmacol 1983; 70: 67.
- Chinoy NJ and Sharma AK: Environ Sci 1999; 7(1): 29-38.
- Kaur P and Bansal MP: Asian J Androl 2004; 6: 227.
- Bertoni JM, Sprenkle PM, Hanifin JP, Stetson MH and Brainard GC: Biol Reprod 1992; 47: 509.
- Zakrzewska H, Udala J and Blaszczyk: Fluoride 2002; 35: 153-60.
- Venable JR, McClimans CD, Flake RE and Dimick DB: J Occup Med 1980; 22(2): 87-91.
- Zhan XA, Xu ZR, Li JX and M: Fluoride.2005; 38: 157-61.
- Doull J, Boekelheide K and Farishian BG: The National Academies Press 2006.
- Chinoy NJ: Fluoride 1998; 31(4): 203-16.
- Chinoy NJ, Sorathia HP and DD Jhala: Fluoride 2005; 38(2): 109-14.
- Joshi AR, Ahmed RN, Pathan KM and Manivannan B: Ind J Exp Biol 1996; 34: 1091-1094.
- Krishnamurthy P and Muthu K: African Journal of Biotech 2011; 10(66): 15017-15019.
- Niemi M and Setchell BP: Biol Reprod 1986; 35: 385.
- Rao MV and KD: Ind J Exp Biol 1998; 36: 775.
- Meng ZQ and W: Chin J Public Health 2003; 19: 1213-5.
- Dixit VP, Lohiya NK and M: Fertil Steril 1975; 26: 781-785.
How to cite this article:
Muthu K, Thirukannan S, Karthikeyan K, Ilansuriyan P and Marimuthu M: Changes in testis protein and metabolic enzyme activities in rats induced by epichlorohydrin. Int J Pharmacognosy 2015; 2(6): 296-00. doi: 10.13040/IJPSR.0975-8232.2(6).296-00.
This Journal licensed under a Creative Commons Attribution-Non-commercial-Share Alike 3.0 Unported License.
Article Information
4
296-300
658
1252
English
IJP
K. Muthu, S. Thirukannan, K. Karthikeyan, P. Ilansuriyan and M. Marimuthu *
Research and Development Division, AquAgri Processing Private Limited, Manamadurai, Sivaganga, Tamil Nadu, India.
marimtu@gmail.com
30 April 2015
24 June 2015
28 June 2015
10.13040/IJPSR.0975-8232.IJP.2(6).296-00
30 June 2015