EFFECT OF BISPHENOL-A ON THE CARDIOVASCULAR SYSTEM IN PREGNANT RATS
HTML Full TextEFFECT OF BISPHENOL-A ON THE CARDIOVASCULAR SYSTEM IN PREGNANT RATS
Thayyuru Geetharathan 1 and Kutagolla Peera * 2
Department of Biotechnology 1, DBT - BIF Centre, Department of Zoology 2, Sri Venkateswara University, Tirupati - 517502, Andhra Pradesh, India.
ABSTRACT: Bisphenol-A (BPA) is a chemical produced in large volumes worldwide and has large market diffusion in many consumer products. BPA is used mainly as a monomer in the production of polycarbonate plastics and as a precursor of epoxy resins. So the present study was undertaken to examine the toxic effect of BPA on heart function in pregnant rat models. BPA (50 mg/kg.b.wt/day and 500 mg/kg.b.wt/day) was administered for 8th to 15th day by oral-gavage. The rats were sacrificed by cervical dislocation after last treatment. Paraffin embedded heart tissue sections were stained with hematoxylin-eosin. Significant degenerative changes were observed in H&E stained heart tissue sections of test rats. The activities of antioxidant enzymes like- superoxide dismutase, catalase and glutathione peroxidase were seen to be decreased significantly in treated rats; while, the level of malondialdehyde, a biomarker of lipid peroxidation, was increased than treated rats. Up-regulation of proapoptotic protein has been reported in heart failure and myocardial infarction, to determine whether caspase-3 protein can affect cardiac function in treated pregnant rats. In conclusion, BPA inhibits ventricular function in rat presumably by producing oxidative stress induced apoptosis and causes potential cardio toxicity.
Keywords: |
Bisphenol-A, Cardiovascular system, Antioxidant enzymes, Apoptosis, Caspase-3
INTRODUCTION: BPA is an environmental estrogenic endocrine disruptor that may have adverse health impacts on a range of tissue (or) systems. It is a monomer of epoxy resins and used extensively to manufacture polycarbonate plastic products. BPA leaches out in the aqueous medium at high temperature and acidic pH 1. Exposure to BPA occurs mainly through the ingestion of food and water from containers and dental materials made up of plastics that leach BPA. Emerging evidence also points to adverse impact of BPA on the cardiovascular system 2, 3.
Here, we examined the influence of rapid BPA exposure on antioxidant enzymes, histological changes, particularly apoptosis, in rat hearts. Among the numerous chemicals discharged into the surrounding environment, BPA have been shown to increase oxidative stress in body by disturbing the antioxidant balance of cells.
An increase in oxidative stress is considered an important pathogenic mechanism in the development of various complications like cardio vascular, cerebro-vascular and peripheral vascular diseases 4. Programmed cell death (apoptosis) has been implicated in normal biological processes and in the pathogenesis of several diseases in humans 5. Recent findings suggest a role of apoptosis in heart failure. Apoptotic cardiomyocyte nuclei have been described in pressure overload and pacing-induced heart failure in animals 6, which are associated with increased Bax and decreased Bcl-2 protein expression 7. Cardiomyocyte apoptosis also can be detected in myocardial tissue of patients with heart failure resulting from idiopathic dilated cardiomyopathy 8 and other cardiac disorders 9. Caspase-3 expression is increased in association with heart failure and apoptosis in experimental animals 10 is found in its activated form in the myocardium of end-stage heart failure patients 11 and is overexpressed in the myocardium of patients with right ventricular dysplasia, a disease associated with myocardial apoptosis, progressive cell loss, and sudden death 12 indicating relevance of caspase-3 to human heart disease.
MATERIALS AND METHODS:
Maintenance of Experimental Animals: Healthy rats of Wistar strain were purchased from authorized vendor (M/S Raghavendra Enterprises, Bangalore, India). All rats were housed in polypropylene cages (18” 10” × 8”) lined with sterilized paddy husk, and provided filtered tap water and rat food ad libitum in an air-conditioned environment (25 ± 2 °C) with a 12-h light and 12-in dark cycle. The experiments were carried out in accordance with the guidelines of the committee resolution no. 04/(i)/a/CPCSEA/ IAEC/ SVU/ KY- KPR / Dt. 28-03-2011 for the purpose of control and supervision on experiments on animals 13.
Experimental Protocol: Female Wistar rats three months old, weighing 250 g to 300 g were used for the experiment. The status of estrous cycle stages were determined every morning between 7:00 am by collecting of vaginal secretion with a plastic pipette filled with 10 μl of normal saline (NaCl 0.9%) by inserting the tip into the rat vagina. One drop of vaginal fluid was placed on glass slides the unstained material was observed under a light microscope, without the use of the condenser lens, with 10x and 40x objective lense. Two females of pro-estrous stage were paired with a male overnight and the next morning, males were removed and females were assessed for the presence of sperm in the vaginal flush. Animals with positive sperm in the flushes are designated as day-1 of gestation. Six pregnant rats were used in each experimental group.
Treatment: BPA was given orally on 8th to 15th day of gestation period (total 8 days) of female albino rats. After that animals were sacrificed and took the serum and selected tissues were isolated for further investigations.
Reagents and Chemicals: All the reagents used were of analytical grade. Bisphenol-A (BPA) was purchased from SD Fine chemicals, Bombay and 5, 5’-dithiobis-2-nitrobenzene (DTNB), oxidized and reduced glutathione, NADPH. Na4 were procured from SRL, India. Eosin and Hematoxylin were procured from Merck, India.
Tissue Collection: After the completion of the treatment duration of 8 days, the animals were sacrificed by cervical dislocation on the 24th hour after completion of the last dose. The heart tissue was removed and a segment of the ventricle was washed in ice cold phosphate buffer solution, dried and stored in -20 ºC for further biochemical studies. The rest of the ventricle was washed in buffer and kept in Neutral buffer formalin for further histological study.
Biochemical Assay: Superoxide dismutase (SOD) activity was measured as per the protocol of Marklund and Marklund, 1974 14. 1 unit of SOD was defined as the enzyme activity that inhibits the autooxidation of pyrogallol by 50%. Catalase (CAT) activity was measured following the protocol of Sinha et al, 1972 15, with slight modifications. Glutathione reductase (GR) activity was measured according to the method of Staal et al., 1969 16. Glutathione peroxidase (GPX) activity was estimated by the method of Rotruck et al, 1973 17. The amount of Malondialdehyde (MDA) was estimated according to the protocol of Devasagayam and Tarachand, 1987 18. Protein content of ventricular tissue of heart was measured by the method of Lowry et al, 1951 19, with Bovine Serum Albumin as the standard.
Histological Study: NBF fixed and paraffin impregnated ventricular tissue sections were stained with normal hematoxylin-eosin stain according to the method of Bancroft et al, 2002 20 with slight modifications. Briefly, 5 μm paraffin section was kept sequentially in xylene and graded ethanol and stained with hematoxylin for 2 min. After removing the excess colour the slide was counterstained with eosin and then the stained slides were dehydrated with graded ethanol, cleared with xylene and mounted with DPX and were observed under the microscope (400X magnification). Images were obtained by digital SLR Olympus Camera (E-620) fitted with Olympus light microscope (CH20i).
Western Blot Analysis: Tissues collected were homogenized with ice-cold homogenizing buffer (50 mM Tris-HCl, 150 mM NaCl, 1 mM EDTA, and 0.5mM Triton X-100, pH 7.4). Heart tissue protein lysates (50 μg/well) were separated by SDS-PAGE (12.5%) under reducing conditions with bovine serum albumin as a standard and transferred to a Nitrocellulose membrane (NCM) membrane. Blocking of membranes was performed with TTBS buffer (20 mM Tris [pH 7.4], 150 mM NaCl, and 0.05% Tween 20) containing 5% non-fat dry milk for 1 h and then washed with TTBS buffer. For the detection of proteins on nitrocellulose membrane, antibodies to caspase-3 (catalog no. 9961), were diluted 1:1000 respectively. Polyclonal beta-actin antibody (catalog no. SC-9104) and monoclonal heat shock protein 60 (HSP60) antibodies (catalog no. SC-13115; Santa Cruz Biotechnology) were used at a dilution of 1:1000. Blots were exposed to horseradish peroxidase-conjugated anti-rabbit IgG (caspase-3), secondary antibodies (diluted 2000- to 5000-fold) for 1 h. The anti-rabbit IgG secondary antibody was purchased from Santa Cruz Biotechnology. The blots were rinsed, and the enhanced chemiluminescence reagent (ECL kit) was added and incubated for 1 min and then exposed to Hyper film ECL. The intensity of specific immunoreactive bands was quantified by an Image J software. All replicates from each group were run in one gel, and the proteins are expressed as a ratio of protein signal to the beta-actin signal.
Statistical Analysis: The mean, standard deviation (SD), percent change and one way analysis of variance (ANOVA) (Steel and Torrle) were performed using the Statistical Package for Social Sciences (SPSS) Package programming techniques on “Intel Core 2 Duo Processor” personnel computer. Probability values less than 0.05 were considered significant (Snedecor and Cochron, 1967) 21.
RESULTS:
Biochemical Study: The activities of antioxidant enzymes were seen to be decreased in a duration dependant manner in 9 days exposure durations. The activity (µ moles/mg of tissue/h) of Super oxide dismutase, Catalase, Glutathioneperoxidase, were decreased significantly in both durations than the respective vehicle control group. The production of MDA, a biomarker of lipid peroxidation, was increased significantly in a duration dependant manner in 9 days exposure group of rats Fig. 1.
FIG. 1: SUPEROXIDE DISMUTASE, CATALASE, GLUTATHIONE PEROXIDASE, MALONDIALDEHYDE ACTIVITY LEVELS IN DIFFERENT HEART TISSUE SAMPLES OF ALBINO RATS EXPOSED TO BPA. *Values are significantly different and # Values are significantly elevated at p<0.05 from control to experimental.
Histological Study: We found distinguishable degenerative changes in ventricular tissues of the hematoxylin-eosin stained ventricular tissue sections of treated rats Fig. 2A-2C. Numerous lacunae were seen in the matrix of stained ventricular tissue section. Moreover, the size of the nucleus of the myocytes was enlarged and the shape became rounded in BPA treated group than the vehicle control group.
Western Blot Analysis: Various degrees of active caspase-3 expression in the heart tissues of all groups (BPA treated and untreated control rats) were detected by Western blotting analysis Fig. 3. Image and statistical analyses showed that there was a significant difference in relative expression levels of active caspase-3 between the control and 50 and 500 mg BPA/kg/day. In the 50 and 500 mg BPA/kg/day rat groups, expression levels of active caspase-3 were increased when compared to corresponding controls. Moreover, expression of active caspase-3 was significantly increased with the increasing BPA dose and normal level of expression in untreated rats.
FIG. 2: HEMATOXYLIN AND EOSIN STAINED VENTRICULAR SECTION OF CONTROL AND BPA TREATED RATS. 2A) HISTOLOGY OF THE VENTRICULAR TISSUE OF THE VEHICLE CONTROL GROUP OF RATS OF 8 DAYS DURATION, 2B) HISTOLOGY OF THE VENTRICULAR TISSUE OF THE BPA TREATED RATS OF LOW DOSE (50 mg/kg/d.b.wt), 2C) HISTOLOGY OF THE VENTRICULAR TISSUE OF THE BPA TREATED RATS OF (500 mg/kg/d.b.wt). Arrows in sections of tissues indicate the changes in morphology of nucleus of ventricular myocytes. Images were obtained by digital SLR Olympus Camera (E-620) fitted with Olympus light microscope (CH20i), (400 X magnifications)
DISCUSSION: The results of the present study revealed that, tissue antioxidant capacity was significantly decreased in BPA treated groups (heart tissue sample) 22, normal level of antioxidant capacity was seen in control group. The activities of antioxidant enzymes SOD, CAT, and GPx were decreased significantly, while the levels of H2O2 generation and lipid peroxidation increased in the animals treated with BPA. Similar results were reported by Kabuto et al, 2003 23. Some free radicals are generated as byproduct of metabolism and are extremely reactive. However, biological systems have evolved endogenous defence mechanisms against these free radical induced cell damage. SOD, CAT and GPX are the primary antioxidant enzymes which directly eliminate reactive oxygen species via hydroxyl radical, superoxide radical, hydrogen peroxide etc.
The stress conditions depend on the degree of production or inactivation of these antioxidant enzymes 24. From our study it is suggested that BPA might induce the oxidative stress in ventricular myocytes by inhibiting the activities of antioxidant enzymes as a result of the accumulation of reactive oxygen species (ROS) in ventricular myocytes. The accumulated ROS in turn induces lipid peroxidation in the biological membranes 25, as revealed by the increase in MDA level in our study. In order to study the oxidative stress induced ventricular tissue damage we have observed the degenerative changes in the ventricular tissue in histological sections of ventricle of heart in BPA treated animals. The sizes of the nuclei were enlarged and the shapes were rounded in BPA treated rats. Numerous lacunae were also seen in the matrix of the ventricle 26.
The present study of results revealed that, an increase in apoptosis in heart tissue, thereby strongly inhibiting catalase activity, resulting in an increase in hydrogen peroxide, and that the oxidative stress elicited by excess H2O2 might activate caspase-3, which induces DNA fragmentation, leading to apoptosis, this is agreement with Kashiwagi et al., 1999 27. BPA administration has been shown to enhance oxidative stress and lipid peroxidation promoting apoptosis in treated tissues and disrupt cell-to-cell communication, because BPA can act as a pro-oxidant induces the formation of reactive oxygen species 28 are generated the free radicals. Free radicals are cytotoxic agents that lead to significant oxidative damage after causing covalently bind to oxidize cellular macromolecules such as DNA, protein and lipid lead to cell death. Similar to our results, Hassan et al., 2012 29 demonstrated that 50 mg/kg of BPA generate ROS, but reduce antioxidant content and activity (glutathione, superoxide dismutase, glutathione peroxidise). Then BPA induces over production of hydrogen peroxide, it is easily converted to hydroxy radicals 30 which causes oxidative stress in cells leads to cell death and raises apoptosis in treated tissues.
The induction of apoptosis is correlated with the activation of caspases, which have proteolytic activity and are able to cleave proteins to result in cell shrinkage, chromatin condensation and DNA fragmentation. We observed the significant increases in the activity of caspase-3 in BPA-treated rats when compared to the corresponding control group, suggesting that apoptosis is Caspase dependent. Caspase-3, a key molecular marker of apoptotic signaling, is activated by either mitochondria dependent or death receptor dependent apoptotic pathways. Previous researches reported that BPA induced mitochondria dysfunction in the isolated rat hepatocytes 31 and human HepG2 cell 32, which led us to study the role of mitochondria played in liver cell apoptosis induced by BPA. Consistent with the change of caspase-3 activity in heart tissues of BPA-treated rats indicated an involvement of a caspase dependent apoptotic pathway of apoptosis. It is evident from our study that expression of the caspase dependent apoptotic pathway could indirectly explain the observed effects of BPA on heart tissues of BPA-treated rats.
ACKNOWLEDGEMENT: Authors are thankful to UGC - New Delhi for providing necessary financial support through RGNF fellowship and DBT New Delhi for providing BIF Computer lab facility to carry out this research work.
CONFLICT OF INTEREST: Authors doesn’t any conflict of Interest.
REFERENCES:
- Kang JH, Kito K and Kondo F: Factors influencing the migration of bisphenol A from cans. J Food Prot 2003; 66: 1444-1447.
- Lang IA, Galloway T S, Scarlett A, Henley W E, Depledge M and Wallace RB: Association of urinary bisphenol A concentration with medical disorders and laboratory abnormalities in adults, JAMA 2008; 300: 1303.
- Melzer D, Rice NE, Lewis C, Henley WE and Galloway TS: Association of urinary bisphenol A with heart disease: evidence from NHANES 2003/06. PLoS One 2010; 5: e8673.
- Ramani G, Kavitha G, Priya KD and Mary RA: Oxidative stress and its association with cardiovascular risk in acute renal failure, Int J Pharm Bio Sci, 2011; 2(3): B-329-B- 334.
- Steller H: Science 1995; 267: 1445-1449.
- Li Z, Bing OH, Long X, Robinson KG and Lakatta EG: Am. J. Physiol. 1997; 272: H2313-H2319.
- Condorelli GL, Morisco C, Stassi G, Roncarati R, Farina F, Trimarco B and Lembo G: Circulation 1999; 23: 3071-3078.
- Narula J, Haider N, Virmani R, DiSalvo TG, Kolodgie FD, Hajjar RJ, Schmidt U, Semigran MJ, Dec GW and Khaw BA: N Engl J Med 1996; 335: 1182-1189.
- James TN: Coron. Artery Dis. 1997; 8: 599-616.
- Sabbah HN, Sharov VG, Gupta RC, Todor A, Singh V and Goldstein S: J Am. Coll Cardiol 2000; 36: 1698-1705.
- Narula J, Pandey P, Arbustini E, Haider N, Narula N, Kolodgie FD, Dal Bello B, Semigran, MJ, Bielsa-Masdeu A and Dec GW: Proc Natl Acad Sci USA 1999; 96: 8144-8149.
- Mallat Z, Tedgui A, Fontaliran F, Frank R, Durigon M and Fontaine GN: Engl. J. Med. 1996; 335: 1190-1196.
- Behringer MP: Laboratory care of vertebrates, In: Techniques and materials in biology. McGraw Hill. Inc., New York 1973; 171-174.
- Marklund S and Marklund G: Involvement of the superoxide anion radical in the autoxidation of pyrogallol and a convenient assay for superoxide dismutase, European J Biochem 1974; 47: 469-474.
- Sinha KA: Colorimetric assay of catalase, Anal Biochem, 1972; 47: 389-394.
- Staal GEJ, Visser J and Veeger C: Purification and properties of glutathione reductase of human erythrocytes, Biochem Biophys Acta 1969; 185: 39-48.
- Rotruct JT, Pope AL, Ganther HE and Swanson AB: Selenium: Biochemical roles as a component of glutathione peroxidase, Science 1973; 179: 588-590.
- Devasagayam TPA and Tarachand U: Decreased lipid peroxidation in the rat kidney during gestation, Biochem Biophys Res Commun 1987; 56: 836-842.
- Lowry OH, Rosbrough NJ, Farr AL and Randall RJ: Protein measurement with the folin fenol reagent. Biological Chemistry 1951; 193(1): 265-275.
- Bancroft JD and Gamble M: Theory and practice of histological techniques, Edinburgh Churchill Livingstone Pub 2002; 5: 172-175 & 593-620.
- Snedecor GW and WG: Cochran. Statistical Methods (6th). 1967; Ames: Iowa State University Press.
- Melzer D, Rice NE, Lewis C, Henley WE and Galloway TS: Association of Urinary Bisphenol A Concentration with Heart Disease: Evidence from NHANES 2003/06. PLoS ONE 2010; 5: 1. e8673.
- Kabuto H, Hasuike S, Minagawa N and Shishibori T: Effects of bisphenol A on the metabolisms of active oxygen species in mouse tissues. Environ Res 2003; 93(1): 31-35.
- Krutz F, Sohn YH, Gloe T, Zahler S, Riexinger T, Schiele MT, Becker FB, Theisen K, Klauss V and Pohl U: NAD(P)H oxidase-dependent platelet superoxide anion release increases platelet recruitment, Blood 2002; 100: 917-924.
- Ji LL: Antioxidants and oxidative stress in exercise, Proc Soc Exp Biol Med 1999; 22: 283-292.
- Munir B, Qadi A and Tahir M: Negative effects of bisphenol A on testicular functions in albino rats and their abolitions with Tribulus terristeris Braz. J. Pharm. Sci. 2017; 53(3): 1-9. e00104.
- Kashiwagi A, Hanada H and Yabuki M: Thyroxine enhacement and the role of reactive oxygen species in tadpole tail apoptosis. Free Radical Biol Med 1999; 26: 1001-1009.
- Jemec A, Tisler T, Erjavec B and Pintar A: Antioxidant responses and whole-organism changes in Daphnia magna acutely and chronically exposed to endocrine disruptor bisphenol A. Ecotoxicol Environ Saf 2012; 12: 147-6513.
- Hassan ZK, Elobeid MA and Virk P: Bisphenol A induces hepatotoxicity through oxidative stress in rat model. Oxid Med Cell Longev 2012; 1-6.
- Kabuto H, Hasuike S, Minagawa N and Shishibori T: Effects of bisphenol A on the metabolisms of active oxygen species in mouse tissues. Environ Res 2003; 93(1): 31-35.
- Nakagawa Y and Tayama S: Metabolism and cytotoxicity of bisphenol A and other bisphenols in isolated rat hepatocytes. Toxicol. 2000; 74: 99-105.
- Huc L, Lemarie A, Gueraud F and Helies-Toussaint C: Low concentrations of bisphenol A induce lipid accumulation mediated by the production of reactive oxygen species in the mitochondria of HepG2 cells. Toxicol in-vitro 2012; 26: 709-717.
How to cite this article:
Geetharathan T and Peera K: Effect of bisphenol-a on the cardiovascular system in pregnant rats. Int J Pharm Sci & Res 2018; 9(11): 4690-95. doi: 10.13040/IJPSR.0975-8232.9(11).4690-95.
All © 2013 are reserved by International Journal of Pharmaceutical Sciences and Research. This Journal licensed under a Creative Commons Attribution-NonCommercial-ShareAlike 3.0 Unported License.
Article Information
20
4690-4695
417
868
English
IJPSR
T. Geetharathan and K. Peera *
Department of Zoology, Sri Venkateswara University, Tirupati, Andhra Pradesh, India.
drkutagollapeera2014@gmail.com
18 March, 2018
31 July, 2018
03 August, 2018
10.13040/IJPSR.0975-8232.9(11).4690-95
01 November, 2018