Impact of polyvinyl chloride, polystyrene, and polyethylene on the organism of mice

Keywords: health effects; plastics; polyvinyl chloride; polystyrene; polyethylene; cholesterol; biochemical parameters of blood; relative mass of the organ.

Abstract

Goods of plastic, due to their durability, universality and economical properties are broadly used in all spheres of life. On the whole, polymers are inert and nontoxic, but in the process of their production, various additives are used, which on contact or introduction into an organism has a negative effect on it. In our study, we determined the impact of some types of plastic (polyvinyl chloride, polysterene and polyethylene) on the organism of laboratory animals according to changes in their body weight, indices of mass of the internal organs, and blood parameters. For the experiment, we formed four groups of white male mice at the age of 3 weeks and average body weight of 50 g. For each group, we used different litter. For group I, the litter was sawdust; and for the other groups we added plastic products in different volumes to the sawdust; for group II finely cut polyvinyl chloride, for group III cut polyethylene, and for group IV granules of polystyrene. Every 3 days, we determined the body weight of the animals, and 32 days later we determined mass of the organs, clinical and biochemical parameters of the blood. Addition of polyvinyl chloride, polyethylene, and polystyrene into the substrate for mice did not have a significant effect on tempi of growth of body weight, and also relative mass of heart and lungs. Polyvinyl chloride and polystyrene have an immune-suppressive effect, and polyvinyl chloride affects both central and peripheral organs, and polystyrene mostly harms the peripheral organs. All used types of plastic cause leukocytopenia, following which neutrophilia of band neutrophils and monocytosis takes place as a result of damage to the biological barriers. We determined the systemic toxic effect of the studied types of plastic on the internal organs, which manifested in increase in their mass (liver, kidneys), steep increase in the activity of liver enzymes (AST, ALT), simultaneous decrease in activity of alkaline phosphatase and content of cholysterol and glucose in the blood serum of the mice. Also polyvinyl chlorine, polyethylene and polystyrene cause degeneration of the epithelium of the uriniferous tubule, which is manifested in reduction of globulins and creatinine in the blood of animals from the experimental groups following increase in relative mass of the kidneys. The results of our research allow us to state that different types of plastic can cause toxic effect on animals, as well as people who are in frequent contact with them.

References

Al-Khatim, A.-S. A., & Ali, K. E.-T. (2006). Effects of chemical migrants from two widely used plastics on reproduction in mice. Journal of Health Science, 52(4), 397–405.

Andrady, A. L., & Neal, M. A. (2009). Applications and societal benefits of plastics. Philosophical Transactions of the Royal Society B: Biological Sciences, 364(1526), 1977–1984.

Boyko, A. A., & Brygadyrenko, V. V. (2017). Changes in the viability of the eggs of Ascaris suum under the influence of flavourings and source materials approved for use in and on foods. Biosystems Diversity, 25(2), 162–166.

Chen, H., Zhang, W., Rui, B., Yang, S., Xu, W., & Wei, W. (2016). Di(2-ethyl hexyl) phthalate exacerbates non-alcoholic fatty liver in rats and its potential mechanisms. Environmental Toxicology and Pharmacology, 42, 38–44.

Chiellini, F., Ferri, M., Morelli, A., Dipaola, L., & Latini, G. (2013). Perspectives on alternatives to phthalate plasticized polyvinylchloride in medical devices applications. Progress in Polymer Science, 38(7), 1067–1088.

Derraik, J. G. (2002). The pollution of the marine environment by plastic debris: A review. Marine Pollution Bulletin, 44(9), 842–852.

Dong, X., Zhang, Y., Dong, J., Zhao, Y., Guo, J., Wang, Z., Liu, M., Na, X., & Wang, C. (2017). Urinary metabolomic profiling in rats exposed to dietary di(2-ethylhexyl) phthalate (DEHP) using ultra-performance liquid chromato graphy quadrupole time-of-flight tandem mass spectrometry (UPLC/Q-TOF-MS). Environmental Science and Pollution Research, 24(20), 16659–16672.

Dudnik, A. E., Chepurnenko, A. S., & Litvinov, S. V. (2017). Determining the rheological parameters of polyvinyl chloride, with change in temperature taken into account. International Polymer Science and Technology, 44(1), 43–48.

Eriksen, M., Lebreton, L. C. M., Carson, H. S., Thiel, M., Moore, C. J., Borerro, J. C., Galgani, F., Ryan, P. G., & Reisser, J. (2014). Plastic pollution in the world's oceans: More than 5 trillion plastic pieces weighing over 250,000 tons afloat at sea. PLoS One, 9(12), 1–15.

Final report on the safety assessment of polyethylene (2007). International Journal of Toxicology, 26, 115–127.

Foster, P. M. D. (2006). Disruption of reproductive development in male rat offspring following in utero exposure to phthalate esters. International Journal of Andrology, 29(1), 140–147.

Frederiksen, H., Skakkebaek, N. E., & Andersson, A.-M. (2007). Metabolism of phthalates in humans. Molecular Nutrition and Food Research, 51(7), 899–911.

Gillum, N., Karabekian, Z., & Sarvazyan, N. (2009). Clinically relevant concen trations of di (2-ethylhexyl) phthalate (dehp) uncouple cardiac syncytium. Biophysical Journal, 96(3), 624a.

Halden, R. U. (2010). Plastics and health risks. Annual Review of Public Health, 31(1), 179–194.

Ho, S.-M., Tang, W.-Y., Belmonte de Frausto, J., & Prins, G. S. (2006). Develop mental exposure to estradiol and bisphenol A increases susceptibility to pros tate carcinogenesis and epigenetically regulates phosphodiesterase Type 4 Variant 4. Cancer Research, 66(11), 5624–5632.

Ikezuki, Y., Tsutsumi, O., Takai, Y., Kamei, Y., & Taketani, Y. (2002). Determi nation of bisphenol A concentrations in human biological fluids reveals significant early prenatal exposure. Human Reproduction, 17(11), 2839–2841.

Indumathi, D., Jayashree, S., Selvaraj, J., Sathish, S., Mayilvanan, C., Akilavalli, N., & Balasubramanian, K. (2013). Effect of bisphenol-A on insulin signal transduction and glucose oxidation in skeletal muscle of adult male albino rat. Human and Experimental Toxicology, 32(9), 960–971.

Jayashree, S., Indumathi, D., Akilavalli, N., Sathish, S., Selvaraj, J., & Balasubra manian, K. (2013). Effect of bisphenol-A on insulin signal transduction and glucose oxidation in liver of adult male albino rat. Environmental Toxicology and Pharmacology, 35(2), 300–310.

Knight, J. (2012). Approaches to understanding economic growth. In: Knight, J., & Ding, S. (Eds.). China’s Remarkable Economic Growth. Oxford Scholarship Online, Oxford. Pp. 11–23.

Koch, H. M., & Calafat, A. M. (2009). Human body burdens of chemicals used in plastic manufacture. Philosophical Transactions of the Royal Society B: Biological Sciences, 364(1526), 2063–2078.

Kuruto-Niwa, R., Tateoka, Y., Usuki, Y., & Nozawa, R. (2007). Measurement of bis phenol A concentrations in human colostrum. Chemosphere, 66(6), 1160–1164.

Lamontagne, N. D. (2012). Plastics and human health. Plastics Engineering, 68(10), 24–31.

Landon-Lane, M. (2018). Corporate social responsibility in marine plastic debris governance. Marine Pollution Bulletin, 127, 310–319.

Lieshchova, M. A., Tishkina, N. M., Bohomaz, A. A., Gavrilin, P. M., & Brygady renko, V. V. (2018). Combined effect of glyphosphate, saccharin and sodium benzoate on rats. Regulatory Mechanisms in Biosystems, 9(4), 591–597.

Liu, X., Cao, Y. F., Ran, R. X., Dong, P. P., Gonzalez, F. J., Wu, X., Huang, T., Chen, J. X., Fu, Z. W., Li, R. S., Liu, Y. Z., Sun, H. Z., & Fang, Z. Z. (2016). New insights into the risk of phthalates: Inhibition of UDP-glucuronosyl transferases. Chemosphere, 144, 1966–1972.

Mullainadhan, V., Viswanathan, M. P., & Karundevi, B. (2017). Effect of Bisphenol-A (BPA) on insulin signal transduction and GLUT4 translocation in gastrocnemius muscle of adult male albino rat. The International Journal of Biochemistry and Cell Biology, 90, 38–47.

Niaounakis, M. (2017). Degradation of plastics in the marine environment. In: Niaounakis, M. (Ed.). Management of Marine Plastic Debris. Elsevier Inc. Pp. 127–142.

North, E. J., & Halden, R. U. (2013). Plastics and environmental health: The road ahead. Reviews on Environmental Health, 28(1), 1–8.

Peng, L. (2015). Mice brain tissue injury induced by diisononyl phthalate exposure and the protective application of vitamin E. Journal of Biochemical and Molecular Toxicology, 29(7), 311–320.

Piringer, O. G., & Baner, A. L. (Eds.). (2008). Plastic Packaging: Interactions with food and pharmaceuticals. Wiley-VCH GmbH & Co.

Posnack, N. G. (2014). The adverse cardiac effects of di(2-ethylhexyl)phthalate and bisphenol A. Cardiovascular Toxicology, 14(4), 339–357.

Prins, G. S., Tang, W.-Y., Belmonte, J., & Ho, S.-M. (2008). Perinatal exposure to oestradiol and bisphenol A alters the prostate epigenome and increases susceptibility to carcinogenesis. Basic and Clinical Pharmacology and Toxicology, 102(2), 134–138.

Sathyanarayana, S. (2008). Phthalates and children’s health. Current Problems in Pediatric and Adolescent Health Care, 38(2), 34–49.

Seth, P. K. (1982). Hepatic effects of phthalate esters. Environmental Health Perspectives, 45, 27–34.

Silva, M. J., Barr, D. B., Reidy, J. A., Malek, N. A., Hodge, C. C., Caudill, S. P., Brock, J. W., Needham, L. L., & Calafat, A. M. (2004). Urinary levels of seven phthalate metabolites in the U.S. population from the National Health and Nutrition Examination Survey (NHANES) 1999-2000. Environmental Health Perspectives, 112(3), 331–338.

Singh, S., & Li, S. S. L. (2012). Bisphenol A and phthalates exhibit similar toxicogenomics and health effects. Gene, 494(1), 85–91.

Skakkebæk, N. E., Rajpert-De Meyts, E., & Main, K. M. (2001). Testicular dys genesis syndrome: An increasingly common developmental disorder with environmental aspects: Opinion. Human Reproduction, 16(5), 972–978.

Stahlhut, R. W., van Wijngaarden, E., Dye, T. D., Cook, S., & Swan, S. H. (2007). Concentrations of urinary phthalate metabolites are associated with increased waist circumference and insulin resistance in adult U.S. males. Environmental Health Perspectives, 115(6), 876–882.

Sun, Y., Irie, M., Kishikawa, N., Wada, M., Kuroda, N., & Nakashima, K. (2004). Determination of bisphenol A in human breast milk by HPLC with column-switching andfluorescence detection. Biomedical Chromatography, 18(8), 501–507.

Vandenberg, L. N., Maffini, M. V., Sonnenschein, C., Rubin, B. S., & Soto, A. M. (2009). Bisphenol-A and the great divide: A review of controversies in the field of endocrine disruption. Endocrine Reviews, 30(1), 75–95.

Vom Saal, F. S., & Hughes, C. (2005). An extensive new literature concerning low-dose effects of bisphenol A shows the need for a new risk assessment. Environmental Health Perspectives, 113(8), 926–933.

Yamada, H., Furuta, I., Kato, E. H., Kataoka, S., Usuki, Y., Kobashi, G., Sata, F., Kishi, R., & Fujimoto, S. (2002). Maternal serum and amniotic fluid bisphenol A concentrations in the early second trimester. Reproductive Toxicology, 16(6), 735–739.

Zahra, N. M., Siswanto, & Widiyanti, P. (2018). The role of chitosan on polyvinyl chloride (PVC)-glycerol biocomposites for blood bag application. Journal of Biomimetics, Biomaterials and Biomedical Engineering, 37, 94–106.

Published
2019-03-17
How to Cite
Lieshchova, M. A., Brygadyrenko, V. V., Tishkina, N. M., Gavrilin, P. M., & Bohomaz, A. A. (2019). Impact of polyvinyl chloride, polystyrene, and polyethylene on the organism of mice . Regulatory Mechanisms in Biosystems, 10(1), 50-55. https://doi.org/10.15421/021908

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