Effect
of methoxychlor on antioxidant system of goat epididymal sperm in vitro
Bindu
Gangadharan, M. Arul Murugan, P.P. Mathur
School
of Life Sciences, Pondicherry University, Pondicherry 605 014, India
Asian
J Androl 2001 Dec; 3: 285-288
Keywords:
methoxychlor;
vitamin C; epididymis; spermatozoa; antioxidants; reactive oxygen species;
goats
Abstract
Aim:
To evaluate the
effect of methoxychlor on the antioxidant system of goat epididymal sperm.
Methods: Epididymis
of adult goat was obtained from local slaughter houses and sperm were
collected by chopping the epididymis in modified Ringer's phosphate solution
(RPS). After several washings, the sperm samples were dispersed
in RPS and incubated with methoxychlor (1 mol/L, 10 mol/L
and 100 mol/L) and methoxychlor+vitamin C (100 mol/L each) for
3 h at 32.
After incubation, the sperm motility and viability were assessed. An aliquot
of sperm sample was homogenized, centrifuged and used for the assay of
superoxide dismutase, glutathione peroxidase, glutathione reductase and
lipid peroxidation. Results: In
methoxychlor-incubated sperm and in sperm co-incubated with methoxychlor
and vitamin C, the sperm motility and viability showed no significant
changes as compared to the corresponding controls. In methoxychlor-incubated
sperm the activity of superoxide dismutase, glutathione reductase and
glutathione peroxidase were decreased while lipid peroxidation was increased
in a dose-dependent manner. Co-incubation of sperm with methoxychlor
and vitamin C showed no changes in the activity of superoxide dismutase,
glutathione reductase and glutathione peroxidase and in the level of lipid
peroxidation. Conclusion: Methoxychlor
induced oxidative stress in epididymal sperm of goats by decreasing the
levels of antioxidant enzymes. Co-incubation of sperm with methoxychlor
and vitamin C, a natural antioxidant, reversed the effect of methoxychlor.
1
Introduction
There
has been an increasing concern regarding the releasing of some natural
and synthetic chemicals into the environment causing disruption of normal
sexual development, differentiation and function in animals and humans[1].
Methoxychlor, a DDT substitute chlorinated hydrocarbon pesticide, is a
labile and readily degradable compound widely used in agriculture, livestock
industry, home and gardens[2]. Although methoxychlor does not
persist long in the environment, it may enter the body of grazing animals
and humans through the food chain. Continuous exposure to methoxychlor
results in reproductive abnormalities in amphibian[3], mice[4],
rats and other animals[5]. Methoxychlor possesses estrogenic
and antiandrogenic properties in vivo and in vitro[6].
Pesticides with such properties have been shown to cause overproduction
of reactive oxygen species(ROS) in both intra and extracellular spaces,
resulting in a decline of sperm count and infertility in wildlife and
humans[7].
Many
environmental contaminants have been reported to disturb the pro-oxidant/antioxidant
balance of the cells thereby inducing oxidative stress[8].
ROS has been shown to damage macromolecules, including membrane bound
polyunsaturated fatty acids (PUFA), causing impairment of cellular function[9].
Spermatozoa are rich in PUFA and, therefore, could be highly susceptible
to oxidative stress. Several investigators have reported that vitamin
C, a powerful water-soluble antioxidant, protects against oxidative damage
caused by free radicals[10]. Previous studies in our laboratory
have shown that lindane, an environmental contaminant, alters the antioxidant
system in testis[11] and epididymis and epididymal sperm[12]
in rats. The present study was undertaken to evaluate if methoxychlor
induces oxidative stress in the epididymal sperm of goats and the effect
could be reversed by vitamin C.
2
Materials and methods
2.1
Chemicals
Methoxychlor
1,1,1-trichloro-2,2-bis
(4-methoxyphenyl) ethane was
a gift from Dr. Ute Tiemann, Research Institute for the Biology of Farm
Animals, Wilhelm Stahl Allee 2, 18196 Dummerstorf, Germany. All other
chemicals were of analytical grade and purchased from local commercial
sources.
2.2
Sperm Collection
Spermatozoa
were obtained from goat epididymis as described by Roy et al[13].
Briefly, epididymis was cut into 4-5 pieces with a sharp razor
blade and dispersed in a modified Ringer's phosphate solution (RPS): (NaCl
119 mM, KCl 5 mM, MgSO4
1.2 mM, glucose 10 mM, potassium phosphate 16.3 mM, penicillin 50 units/mL;
pH 6.9) with gentle stirring. The sperm obtained was washed several times
in RPS and centrifuged at 225g for 10 min. An aliquot of the sperm suspension
were homogenised for ten seconds in cold RPS medium using glass teflon
homogenizer of Potter-Elvehjem type. An aliquot was centrifuged at 800g
for 20 min at 4
. The supernatant was used for biochemical assays.
2.3
Sperm
incubation
Sperm
samples dispersed in RPS were incubated with methoxychlor (1
mol/M, 10 mol/M and 100 mol/M) and methoxychlor+vitamin
C (100 mol/M each) for 3 h at 32.
2.4
Sperm
motility and viability
After
incubation, an aliquot of sperm suspension (5 L)
was placed in the Neubauer haemocytometer. The percentage of motile sperm
was counted under light microscope at 200 magnification. The viability
of epididymal sperm was determined by eosin staining and counting under
light microscope at 200 magnification. The data were expressed
in percentage of total sperm.
2.5
Biochemical assays
After
3 hours of incubation, the biochemical assays of superoxide dismutase[14],
glutathione reductase[15], glutathione peroxidase[16]
and lipid peroxidation[17] were performed. DNA was estimated
by the method of Burton[18].
2.6
Statistical analysis
The
data were presented as meanSD, if applicable. Statistical analysis was
performed using Student's t-test. Significance of differences was
set at P<0.05.
3
Results
In
methoxychlor-incubated sperm and in the sperm co-incubated with methoxychlor
and vitamin C, the epididymal sperm motility and viability showed no significant
changes as compared to the corresponding control sperm samples (Figure
1). The specific activities of superoxide dismutase, glutathione reductase
and glutathione peroxidase were found to be decreased in methoxychlor-incubated
sperm samples while the level of lipid peroxidation was increased in a
dose-dependent manner when compared to the corresponding controls (Figure
2). When sperm samples were co-incubated with methoxychlor and vitamin
C the specific activity of antioxidant enzymes superoxide dismutase, glutathione
reductase, glutathione peroxidase and the level of lipid peroxidation
remained unchanged (Figure 3).
Figure
1. Effect of incubation of sperm with methoxychlor
and co\|incubation of sperm with methoxychlor and vitamin C on epididymal
sperm motility and viability of goat sperm. The values are expressed as
meanSD. The data were expressed in percentage of total sperm.
Figure
2. Effect of incubation of sperm with methoxychlor
on antioxidant system in goat epididymal sperm. The values are expressed
as meanSD. bP<0.05 vs control. The unit of superoxide
dismutase is expressed as nmol pyrogallol oxidized/min/109
spermatozoa at 32.
The unit of glutathione reductase and glutathione peroxidase is expressed
as nmol NADPH oxidized/min/109 spermatozoa at 32.
The unit of lipid peroxidation is expressed as mol malondialdehyde produced/15
min/109 spermatozoa.
Figure
3. Effect of co-incubation of sperm with methoxychlor
and vitamin C on antioxidant system in goat epididymal sperm. The values
are expressed as meanSD. The unit of superoxide dismutase is expressed
as nmol pyrogallol oxidized/min/109 spermatozoa at 32.
The unit of glutathione reductase and glutathione peroxidase is expressed
as nmol NADPH oxidized/min/109 spermatozoa at 32.
The unit of lipid peroxidation is expressed as mol malondialdehyde produced/15
min/109 spermatozoa.
4
Discussion
Methoxychlor
has been considered as a pro-estrogen metabolized into mono- and bis-hydroxymetabolites
which possess higher estrogenic activity than the parental compound[19].
The major metabolite of methoxychlor, HPTE (2,2-bis ( p-hydroxyphenyl
)-1,1,1-trichlo-roethane), has been shown to bind both the estrogen and
androgen receptors[20], causing estrogenic effect in the males[21].
Methoxychlor at a dose of 20 g/kg has been considered the No Observed
Adverse Effect Level (NOAEL) for humans[22]. The dosages selected
in the present study (1, 10 and 100
mol/L) were below the NOAEL and these doses did not significantly
decrease the sperm motility and viability when compared to the controls.
A
few toxicological studies have reported that exposure to environmental
contaminants generates ROS and causes adverse effects on male reproduction[23].
In
spermatozoa, several antioxidant defence systems, namely, glutathione
peroxidase[24], superoxide dismutase[25] and catalase[26]
are known to operate. Superoxide dismutase generally dismutases the superoxide
anion radical into hydrogen peroxide[27]. The hydrogen peroxide
produced during the reactions is removed by catalase or glutathione peroxidase/reductase
system[24]. It has been reported that increase in ROS can cause
the destruction of all cellular structures including membrane lipid[23].
Hence in the present study lipid peroxidation is used as an index of oxidative
stress. Malondialdehyde, a lipid peroxidation product generated in tissues
by free radical injury is measured by thiobarbituric acid reactivity and
has been considered as sensitive index of free radical generation[23].
The
present study indicated that graded doses of methoxychlor induced oxidative
stress thereby decreasing the activities of antioxidant enzymes in goat
epididymal sperm. In conclusion, induction of oxidative stress by methoxychlor
could be reversed by the antioxidant, vitamin C, in the epididymal sperm
of goats.
Acknowledgements
The
authors thank Dr. Ute Tiemann for the generous gift of methoxychlor and
the staff of Bioinformatics Center, Pondicherry University, Pondicherry
for providing various facilities. The authors also acknowledge the receipt
of financial support from the Population Council, New York, USA
(Grant Nos. B 99.047P-9/ ICMC and B99.048R/ ICMC).
References
[1]
Colborn T, Clement C. Chemically
induced alterations in sexual and functional development: the wildlife/
human connection. Princeton, NJ: Princeton Scientific Publishing; 1992.
[2] Metcalf RL. Model ecosystems for environmental studies of estrogens.
In: McLachlan JA, editor. Estrogens in the environment. New York: Elsevier/
North Holland; 1980. p 203-11.
[3] Pickford DB, Morris ID. Effects of endocrine-disrupting contaminants
on amphibian oogenesis: methoxychlor inhibits progesterone-induced maturation
of Xenopus laevis oocytes. Environ Health Perspect 1999; 107: 285-92.
[4] Welshons WV, Nagel SC, Thayer KA, Judy BM, Vom Saal FS. Low-dose bioactivity
of xenoestrogens in animals: fetal exposure to low doses of methoxychlor
and other xenoestrogens increases adult prostate size in mice. Toxicol
Ind Health 1999; 15: 12-25.
[5] Gray LE, Ostby J, Cooper RL, Kelce WR. The estrogenic and antiandrogenic
pesticide methoxychlor alters the reproductive tract and behavior without
affecting pituitary size or LH and prolactin secretion in male rats. Toxicol
Ind Health 1999; 15: 38-47.
[6] Maness SC, McDonnell D, Gaido KW. Inhibition of androgen receptor-dependent
transcriptional activity by DDT-isomers and methoxychlor in HepG2 human
hepatoma cells. Toxicol Appl Pharmacol 1998; 151: 135-42.
[7] Sharpe RM, Skakkebaek NE. Are oestrogens involved in falling sperm
counts and disorders of the male reproductive tract? The Lancet 1993;
341: 1392-5.
[8] Harris C, Lee E, Hiranruengchok R, McNutt TL, Larson SJ, Akeila S,
Thorsrud BA. Characteristics of glutathione redox and antioxidant status
in post implantation rat embryos: response to oxidative stress. Toxicologist
1996; 30: 2.
[9] Lenzi A. Lipoperoxidation damage of spermatozoa polyunsaturated fatty
acids (PUFA): Scavenger mechanisms and possible scavenger therapies. Front
Biosc 2000; 5: 1-15.
[10] Chakraborty S, Nandi A, Mukhopadhyay M, Mukhopadhyay C, Chatterjee
IB. Ascorbate protects guinea pig tissues against lipid peroxidation.
Free Rad Biol Med 1994; 16: 417-26.
[11] Sujatha R, Chitra KC, Latchoumycandane C, Mathur PP. Effect of lindane
on testicular antioxidant system and steroidogenic enzymes in adult rats.
Asian J Androl 2001; 3: 135-8.
[12] Chitra KC, Sujatha R, Latchoumycandane C, Mathur PP. Effect of lindane
on antioxidant enzymes in epididymis and epididymal sperm of adult rats.
Asian J Androl 2001; 3: 205-8.
[13] Roy N, Majumder GC, Chakraborty CK. Occurrence of specific glycoprotein
factor(s) in goat epididymal plasma that prevent adhesion of spermatozoa
to glass. Andrologia
1985; 17: 200-6.
[14] Marklund S, Marklund G. Involvement of superoxide anion radical in
antioxidation of pyrogallol and a constituent assay for superoxide dismutase.
Eur J Biochem 1974; 47: 469-74.
[15] Carlberg I, Mannervik BJ. Purification and characterization of the
flavo enzyme glutathione reductase from rat liver. J Biochem 1975; 250:
5474-80.
[16] Mohandas J, Marshall JJ, Duggin GG, Horvath JS, Tiller DJ. Low activities
of glutathione-related enzymes as factors in the genesis of urinary bladder
cancer. Cancer Res 1984; 44: 5086-91.
[17] Ohkawa H, Ohishi N, Yagi K. Assay for lipid peroxidation in animal
tissues by thiobarbituric acid reaction. Anal Biochem 1979; 95: 351-8.
[18] Burton K. A study of the conditions and mechanism of the diphenylamine
reaction for the colorimetric estimation of deoxyribonucleic acid. Biochem
J 1956; 60: 316-20.
[19] Bulger WH, Muccetelli RM, Kupfer D. Studies on the in vivo
and in vitro estrogenic activities of methoxychlor and its metabolites:
role of hepatic mono\|oxygenase in methoxychlor activation. Biochem Pharmacol
1978; 27: 2417-23.
[20] Waller LW, Oprea CW, Chea K, Park D, Korach KS, Laws SC, et al.
Ligand-based identification of environmental estrogens. Chem Res Toxicol
1996a; 9: 1240-8.
[21] Gaido KW, Leonard LS, Maness SC, Hall JM, McDonnell DP, Saville B,
Safe S. Differential interaction of the methoxychlor metabolite 2,2-bis-
(p-hydroxyphenyl)-1,1,1-trichloroethane with estrogen receptors
and . Endocrinology 1999; 140: 5746-53.
[22] ATSDR. Toxicological profile for methoxychlor. Agency for toxic substances
and disease registry, US Department of Health and Human Services, Atlanta,
GA. 1994.
[23] Ichikawa T, Oeda T, Ohmori H, Schill WB. Reactive oxygen species
influence the acrosome reaction but not acrosin activity in human spermatozoa.
Int J Androl 1999; 22: 37-42.
[24] Alvarez JG, Storey BT. Role of glutathione peroxidase in protecting
mammalian spermatozoa from loss of motility caused by spontaneous lipid.
Gamete Res 1989; 23: 77-90.
[25] Mennela MRF, Jones R. Properties of spermatozoal superoxide dismutase
and lack of involvement of superoxides in metals ion\|catalyzed lipid
peroxidation reactions in semen.
Biochem J 1980; 191: 289-97.
[26] Jeulin C, Soufir JC, Weber P, Martin DL, Calvayrae R. Catalase activity
in human spermatozoa and seminal plasma. Gamete Res 1989; 24: 185-96.
[27] Nissen HP, Kreysel HW. Superoxide dismutase in human semen. Klinische
Wochenschrift. 1983; 61: 63-5.
home
Correspondence
to: Dr.
P.P. Mathur, School of Life Sciences, Pondicherry University, Pondicherry
605 014, India.
Tel:+91-413-655
212,
Fax:+91-413-655 211
E-mail: ppmathur@hotmail.com
Received 2001-10-16 Accepted 2001-11-26
|