Histopathological evaluation of selected organs of rabbit bucks exposed to dietary di-(2-ethylhexyl) Phthalate
Abstract
This study used 45 crossbred rabbit bucks that had not yet reached puberty with an average weight of 1.37±0.24 kg to investigate the impact of di-(2-ethylhexyl) phthalate (DEHP) on certain internal organs of the rabbits that were divided into 5 different groups for their diets: T1 (control), T2, T3, T4, and T5. DEHP was added to the diets at different levels: 0, 100, 200, 300 and 400 ppm for T1, T2, T3, T4 and T5 respectively. There were 9 replicates for each treatment, with 1 rabbit assigned to each replicate, following a randomized design. After the 75-day feeding trial, histopathological evaluation was performed on 3 randomly chosen rabbits from each treatment. The rabbits were deprived of feed for a whole night and their live weights were taken. They were stunned, slaughtered and drained of blood before skinning. The liver, kidney, spleen, testis, and ileum were carefully extracted. Specific portions of these organs were sampled and immersed in 10% formalin fixative for 24 hours. After fixing, the tissue samples underwent histopathological procedures. The findings show that there was no noticeable liver damage in rabbits on T1 and T2. In T3, 50% of the rabbits experienced mild congestion in liver central veins. Meanwhile, the other 50% had moderate congestion in their portal and central veins, with severe degeneration of liver cells. Half of the bucks' livers in T4 displayed slight widespread swelling and degeneration of liver cells, while the other half showed a moderate blockage in the livers’ portal system. At T5, it was noted that all rabbits had moderate to severe infiltration of cells around the liver portal area. Furthermore, there were no notable abnormalities found in the kidneys of the rabbits on T1. Rabbits on T2 had a mild to moderate congestion in the interstitial region of their kidneys. In T3, 50% of the rabbits experienced a slight blockage in the renal cortex, while the other 50% showed protein buildup in their renal tubules. Histological evaluation showed that bucks on T4 had kidneys that exhibited widespread degeneration of glomeruli and tubular epithelial cells. However, kidneys of all bucks on T5 experienced interstitial congestion of mild to moderate extent. Meanwhile, the bucks did not show any major abnormal conditions in their spleen, testis, and ileum. The findings indicate that the livers and kidneys of male rabbits are more vulnerable to the harmful impacts of DEHP in their diet.
Full Text
Tables and figures are in the full-text PDF.
Introduction
Phthalates, which are also called phthalic acid esters, are colourless, thick, lipid-loving substances without any smell. They typically exist in a liquid state between temperatures of 25 to 50 degrees Celsius. (Kashyap and Agarwal, 2018) [9] . Phthalates such as di-(2-ethylhexyl) phthalate (DEHP), di-buthyl phthalate (DBP) and di-isononyl phthalate (DiNP) are primarily utilized in the plastics sector as plasticizers to enhance the resilience of PVC materials (ang and Qian, 2021) Qian. These chemicals, recognized as endocrine-disrupting chemicals (EDCs), have been proven to disrupt normal hormonal functions (Wang and Qian, 2021) [21] . Many consumer items, such as nutritional supplements, medications, food packaging, cosmetics and clothing contain phthalates. (Schettler, 2006) [17] . Additionally, phthalates are found in medical devices like umbilical artery catheters, (Rowdhwal, and Chen, 2018) [16] . DEHP, similar to other phthalates, can easily move from consumer items to the environment due to its lack of chemical bonding in polymers (Tran et al., 2022) [20] and it has been detected in foods (Przybylińska and Wyszkowski, 2016) [15] , meat and dairy products (Serrano et al., 2014) [18] . When ingested, DEHP is metabolized into different metabolites including di-n-butyl phthalate (DnBP), benzyl butyl phthalate (BBzP) and diethyl phthalate (DEP), (Koch et al., 2003) [10] . Reports have been made on the toxic effects of DEHP on the endocrine system of rats. Martinez-Arguelles et al. (2009) [12] discovered that when male adult rats were exposed to DEHP, their Leydig cells had reduced expression of mineralocorticoid receptors, which resulted in a decrease in testosterone production. The studies conducted by Zhao et al. (2021) [23] and Liu et al. (2021) [11] have suggested that DEHP is associated with disorders in lipid metabolism and liver damage in rodents. In zebra fish, the exposure to DEHP has caused fetal death and other indications of harm such as tissue damage and abnormal tail shape (Rowdhwal and Chen, 2018) [16] . Furthermore, rats that were given a diet containing DEHP have experienced long-lasting alterations in their thyroid structure. These changes are marked by continued over activity caused by an increased number and size of lysosomes, as well as an enlargement of the Golgi apparatus (Price et al., 1988) [14] . Jia et al. (2016) [8] also observed a disruption in the thyroid endocrine system of zebra fish when exposed to DEHP. Based on the findings of Herreros et al., in the year 2013 [5] , ewes that were cycling and were exposed to DEHP had a shorter ovulatory cycle due to a reduction in the size and lifespan of corpora lutea. However, the ewes showed an increase in progesterone levels in their bloodstream, suggesting that DEHP influenced metabolism of steroid. According to Olatundun and Ogunlade (2020) [13] , there was a notable decrease in red blood cells (RBC), platelets, albumin, thyroid stimulating hormone (TSH), and testosterone, as well as a notable increase in aspartate aminotransferase (AST) and creatinine, in male rabbits exposed to 400 ppm DEHP compared to those on the control diet. Histopathological findings in the spleen tissue of quail exposed to DEHP revealed an increase in cell gap and changes in the corpuscular border of spleen (Yu et al., 2019) [22] . Testicular toxicity of DEHP in mice and rats has been documented. According to David (2006) [3] , DEHP has been discovered to disrupt the regular process of sexual development in male rodents due to a decrease in testosterone production. However, the current information regarding the impact of DEHP on certain organs such as the liver, kidney, spleen, testis, and ileum of rabbits is not extensive. Hence, this research was conducted to evaluate the influence of a diet containing DEHP on specific organs of male rabbit.
Materials and Methods
Experimental site
The research was conducted at the Rabbitry Unit located in the Teaching and Research Farm of Ekiti State University in Ado Ekiti, Nigeria. The site can be found at a latitude of 7 o 37 1 15 1 N and Longitude 05 o 13 o 28 o E. The temperature at the site typically varies between 21 and 28 degrees Celsius.
Formulation of experimental diets
A high-quality analytical standard with a purity of more than 99.5% of Di-(2-ethylhexyl) phthalate was purchased from Sigma-Aldrich, based in the USA, through Bristol Scientific Company located in Lagos, Nigeria. This standard was utilized in the study at specific levels of inclusion. Treatment 1 was the control diet, containing no DEHP, while Treatments 2, 3, 4 and 5 contained 100, 200, 300 and 400 ppm DEHP respectively.
Experimental rabbits and design
A total of 45 young male rabbits that had not yet reached puberty were bought from trusted rabbit breeders in the Nigerian States of Oyo and Ekiti. These rabbits had an average weight of 1.37±0.24 kg when they were initially acquired. During the acclimatization period, which lasted for 2 weeks, all the rabbits were given the control diet and had unrestricted access to water. After this period, the rabbits were weighed and randomly assigned to 5 different treatments. Five diets were created, one of which was the control diet (T1). This diet had a crude protein content of 17.99%, crude fiber content of 11.33%, and a digestible energy content of 2,789 kcal/kg (Table 1). All diets contained the same amount of nitrogen and calories. The dietary treatments T2, T3, T4, and T5 had the exact same ingredients as the control diet, but they also had DEHP added at levels of 100, 200, 300, and 400 ppm respectively. There were 9 replicates for each treatment, consisting of one rabbit per replicate, in a design that was completely randomized. At the conclusion of the 75-day feeding trial, three male rabbits were chosen at random from each group to undergo Histopathological evaluation. The rabbits were deprived of food for one night and their weights were measured. After that, they were then stunned, slaughtered and bled properly before skinning. The liver, kidney, spleen, testis, and ileum were collected. Then, small sections of these organs were extracted and preserved in 10% formalin fixative, which was about ten times the volume of the samples. The preservation process lasted for 24 hours. After fixing the tissue samples, they underwent additional histopathological procedures as outlined by Slaoui and Fiette in 2011 [19] . No significant lesion was seen in the liver of experimental rabbit bucks on the control diet (Plate 1) and those in 100 ppm diet (Table 2) (Plate 2). In 200 ppm diet (Plate 3), 50% of the bucks had mild central venous and sinusoidal congestion, while in the remaining 50% there was a combination of mild to moderate blockage in the portal and central veins, along with a severe widespread deterioration of liver cells in the form of vacuolar degeneration. The liver of half of the rabbit bucks on 300 ppm diet (Plate 4) had a mild widespread swelling and damage to liver cells, while the liver of the remaining half had a slight congestion in the portal, along with a mild infiltration of cells surrounding the portal. In the 400 ppm diet, it was noticed that all of the male rabbits had a significant and noticeable infiltration of cells in the liver, specifically around the portal areas (Plate 5). No significant lesion was seen in the kidney of experimental rabbit bucks on the control diet (Plate 6). In 100 ppm diet, it was also discovered that 100% of the bucks had mild to moderate interstitial congestion in their kidneys (Plate 7). In 200 ppm diet, 50% showed a very mild interstitial congestion at the renal cortex, while 50% had many of their renal tubules showing small sized protein casts in the lumen (Plate 8). In 300 ppm diet, histological examination revealed that 100% of the bucks had moderate diffuse degeneration of glomeruli and tubular epithelial cells in their kidneys (Plate 9) while 400 ppm DEHP in the diet of the bucks induced 100% mild to moderate interstitial congestion in their kidneys (Plate 10). The various dietary DEHP levels failed to induce significant pathological lesions in the spleen, testis and ileum of the experimental rabbit bucks
Discussion
The findings from the histological evaluation of tissue samples of certain organs in rabbits involved in the experiment showed that there were no notable lesions found in the liver of male rabbits in the control group and those given a diet with 100 ppm of DEHP. However, rabbits given diets with 200, 300, and 400 ppm of DEHP exhibited mild to severe pathological abnormalities in the liver. Based on these findings, it appears there is evidence to support the rise in serum liver enzyme levels and the relative weight of the liver in rabbits exposed to DEHP-contaminated diets (Olatundun and Ogunlade, 2020) [13] . The outcomes align with the discoveries made by Jarosova et al. (2009) [7] , that the liver is the organ most frequently affected by acute toxicity from DBP and DEHP. George et al. (2017) [4] noted that when fish were exposed to DEP, they displayed signs of liver cell death, the presence of small fluid-filled sacs in their cells, and a densely stained nucleus. Ikele et al. (2011) [6] found that the liver of Clarias gariepinus, when exposed to DEP, exhibited congested (cirrhotic) conditions, reduction in filament, enlarged sinusoids, and necrotic areas. Dietary DEHP elicited various degrees of pathological abnormalities on the kidney of the rabbits across the treatment groups. The nephrotoxicity and nephropathy effects of DEHP and other phthalates have been documented (George et al., 2017) [4] . Elevated levels of urea and creatinine in the bloodstream, as observed in a study conducted by Olatundun and Ogunlade (2020) [13] , indicate decline in kidney function caused by DEHP exposure.
Conclusion
DEHP is both hepatotoxic and nephrotoxic because of histologic lesions found in the liver and kidney of the rabbits at inclusion level above 100 ppm
Conflict of Interest Not available
Financial Support
References
- Centers for Disease Control and Prevention (CDCP). Phthalates Factsheet; 2021. Available from: https://www.cdc.gov/biomonitoring/Phthalates_FactSheet .html. Accessed February 2024.
- David RM, Moore MR, Finney DC, Guest D. Chronic toxicity of di-(2-ethylhexy) phthalate in mice. Toxicol Sci. 2001;58:377-385.
- David RM. Proposed mode of action for in utero effects of some phthalate esters on the developing male reproductive tract. Toxicol Pathol. 2006;34(3):209-219. DOI: 10.1080/01926230600642625.
- George KR, Gokul GN, Malini NA. Effects of different sub-lethal concentrations of plasticizer-diethyl phthalate on freshwater murrel, Channa striatus (Bloch). J Appl Nat Sci. 2017;9(1):476-481. DOI: 10.31018/jans.v9i1.1217
- Herreros MA, Bulnes GA, Nunez IS, Solis CI, Ros JM, Encinas T. Toxicokinetics of di(2-ethylhexyl) phthalate (DEHP) and its effects on luteal function in sheep. Reprod Biol. 2013;13(1):66-74. DOI: 10.1016/j.repbio.2013.01.177
- Ikele C, Mgbenka B, Oluah BO, Ndubu S. Histopathological effects of diethyl phthalate on Clarias gareipinus juveniles. Anim Res Int. 2011;8(3):14311438.
- Jarosova A, Harazim J, Suchy P, Kratka L, Stancova V. The distribution and accumulation of phthalates in the organs and tissues of chicks after the administration of feedstuffs with different phthalates concentrations. Vet Med. 2009;54(9):427-434. DOI: 10.17221/2/2009VETMED
- Jia PP, Ma YB, Lu CJ, Mirza Z, Zhang W, Jia YF, et al. The effects of disturbance on hypothalamus-pituitarythyroid (HPT) axis in zebrafish larvae after exposure to DEHP. PLoS One. 2016;11(5):e0155762. DOI: 10.1371/journal.pone.0155762
- Kashyap D, Agarwal T. Concentration and factors affecting the distribution of phthalates in the air and dust: A global scenario. Sci Total Environ. 2018;635:817-827. DOI: 10.1016/j.scitotenv.2018.04.158
- HM, Drexler H, Angerer J. An estimation of the daily intake of di(2-ethylhexyl) phthalate (DEHP) and other phthalates in the general population. Int J Hyg Environ Health. 2003;206(2):77-83. DOI: 10.1078/14384639-00205
- Liu RJ, He YJ, Liu H, Zheng DD, Huang SW, Liu CH. Protective effect of Lyceum barbarum polysaccharide on di-(2-ethylhexyl) phthalate-induced toxicity in rat liver. Environ Sci Pollut Res Int. 2021;28:23501-23509. DOI: 10.10007/s11356-020-11990-8
- Arguelles MDB, Culty M, Zirkin BR, Papadopoulos V. In-utero exposure to di-(2-ethylhexyl) phthalate decreases mineralocorticoid receptor expression in the adult testis. Endocrinology. 2009;150(12):5575-5585. DOI: 10.1210/en.2009-0847
- Olatundun BE, Ogunlade JT. Haematology, serum biochemistry and hormone profile of rabbit bucks fed dietary Di-(2-ethylhexy) phthalate. EC Vet Sci. 2020;5(10):76-83.
- Price SC, Chescoe D, Grasso P, Wright M, Hinton RH. Alterations in the thyroids of rats treated for long periods with di-(2-ethylhexyl) phthalate or with hypolipidaemic agents. Toxicol Lett. 1988;40(1):37-46. DOI: 10.1016/0378-4274(88)90181-6
- Przybylinska PA, Wyszkowski M. Environmental contamination with phthalates and its impact on living organisms. Ecol Chem Eng S. 2016;23(2):347-356. DOI: 10.1515/eces-2016-0024
- Rowdhwal SS, Chen J. Toxic effects of di-2-ethylhexyl phthalate: An overview. Biomed Res Int. 2018;2018:110. DOI: 10.1155/2018/1750368
- Serrano SE, Braun J, Trasande L, Dills R, Sathyanarayana S. Phthalates and diet: a review of the food monitoring and epidemiology data. Environ Health. 2014;13:43. DOI: 10.1186/1476-069X-13-43
- Slaoui M, Fiette L. Histopathological Procedures: From tissue sampling to histopathological evaluation. Methods Mol Biol. 2011;692:69-82. DOI: 10.1007/978-1-60761849-2_4
- Tran HT, Lin C, Bui X, Nguyen MK, Cao NT, Mukhtar H, et al. Phthalates in the environment: Characteristics, fate and transport, and advanced wastewater treatment technologies. Bioresour Technol. 2022;344B. DOI: 10.1016/j.biortech.2021.126249
- Wang Y, Qian H. Phthalates and their impacts on human health. Healthcare. 2021;9(5):603-610. DOI: 10.3390/healthcare9050603
- Yu L, Li H, Guo J, Huang Y, Wang H, Talukder M, Li J. Di (2-ethyl hexyl) phthalate (DEHP)-induced spleen toxicity in quail (Coturnix japonica) via disturbing Nrf2mediated defense response. Environ Pollut. 2019;251:984-989. DOI: 10.1016/j.envpol.2019.05.061
- Zhao Y, Bao R, Zhu S, Talukder M, Cui J, Zhang H, et al. Lycopene prevents DEHP-induced hepatic oxidative stress damage by crosstalk between AHR-Nrf2 pathway. Environ Pollut. 2021;285:117080. DOI: 10.1016/j.envpol.2021.117080
How this paper connects to the literature. Drag to explore, click any node to open that paper.
