Histopathological and Cytogenetic Effects of Hyperdoses of Vitamin D in Female Rats
Research Article
Histopathological and Cytogenetic Effects of Hyperdoses of Vitamin D in Female Rats
Ghaith Z. Hasan Al-Askari *, Eman H. Yousif Al-Taee
Department of Pathology and Poultry Diseases, College of Veterinary Medicine, University of Baghdad, Baghdad, Iraq.
Abstract | The Highlights of the present study was undertaken to investigate the toxic effects of the higher dose group (HG) (549.640 IU, i.e., 1.3741 mg/kg body weight), which represent 1/10 LD50, and the lower dose group (LG) (274.820 IU, i.e., 0.6875 mg/kg body weight), which represents 1/20 LD50 of vitamin D3. So, the objectives of this rapid review were to assess the median lethal dose (LD50) of VD in female albino rats and to assess the effects of vitamin D (VD) on the severity of acute upper or chronic vitamin D intoxication (VDI) through the study of cytogenetic effects in addition to histopathological changes in the tissues of female rats. The methods included in the first experiment, the female rats were orally administered the following lethal doses: 0.5, 1, 1.5, 2, 2.5, 3, 4, 5, 6, 7, 8, 9, 10, 11, 12, 13, 14, 15, and 16 mg/kg b.w. of vitamin D. Survival and mortality numbers were observed following 24 hours of intoxication. In the second experiment, the selected groups were divided according to the doses they received. In a cross-sectional study, 30 female rats were divided into three groups: a control group (CG: 0 mg/kg VD), a high VD group (HG: 1/10 LD50), and a low VD group (LG: 1/20 LD50). While the Results included at the dose of 1/10 LD50, the lesions were more severe than the lesions at 1/20 LD50. The characteristic histological finding in the liver is severe and generalized hepatocellular necrosis, which revealed congestion, hemorrhage, and degeneration of hepatic cells. Some sections of the kidneys show vacuolation of mesangial cells in the glomerular tuft. Muscles of treated rats revealed severe histopathological changes under stress from both doses of toxic cholecalciferol, also showing the widespread mineralization of muscle fibers. From this study concluded that both doses of vitamin D can be toxic to organisms at higher levels, so they need to be used carefully and should not be taken excessively.
Keywords | Hypervitaminosis D, Chromosome gap, Histopathological, Cytogenetic effects, Vitamin D, Median lethal dose, Mitotic index, Rats, Female rats.
Received | December 16, 2023; Accepted | January 07, 2024; Published | February 23, 2024
*Correspondence | Aalaa S. Saad, Department of Pathology and Poultry Diseases, College of Veterinary Medicine, University of Baghdad, Baghdad, Iraq; Email: ghaithalaskari@gmail.com
Citation | Al-Askari GZH, Al-Taee EHY (2024). Histopathological and cytogenetic effects of hyperdoses of vitamin d in female rats. Adv. Anim. Vet. Sci. 12(4): 703-711.
DOI | https://dx.doi.org/10.17582/journal.aavs/2024/12.4.703.711
ISSN (Online) | 2307-8316
Copyright: 2024 by the authors. Licensee ResearchersLinks Ltd, England, UK.
This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/).
INTRODUCTION
The vitamins are a chemically disparate group of compounds whose only common feature is that they are dietary essentials that are required in small amounts for the normal functioning of the body and maintenance of metabolic integrity (Bender., 2009; Walsh and Tang., 2019). Most vitamins are provided by food, so they are classed as ‘essential’ and are divided into two groups: fat-soluble and water-soluble (Broom and Dominiczak, 2014; Godswill et al., 2020; Rafeeq et al., 2020). Vitamin D is fat-soluble and is stored in fatty tissue (Khalfa et al., 2019; Stevens, 2021; Chen et al., 2022). The most important compound of vitamin D is cholecalciferol (vitamin D3, or VD3), which is produced in the skin following exposure to sunshine or ultraviolet light or obtained from nutritional sources, especially fatty fishes such as salmon, sardines, herring and mackerel (Kadhim and Abdul-hassan., 2017; Balwan and Saba., 2021; Javed et al., 2021), That plays a central role in metabolism and also in muscle, cardiac, immune, and neurological functions, as well as in the regulation of inflammation (Dominguez et al., 2021; Marazziti et al., 2021). Tooth mineralization and bone remodeling depend on the quantity of serum vitamin D (VD) (Khamees et al.,2023). Numerous of vitamin D compounds have been created as medications to treat a range of illnesses (Yasuda et al., 2021). Vitamin D (VD) status is a modifiable factor that may reduce risk of breast cancer BC through modulation of cell proliferation, apoptosis, invasion and metastasis via binding to a specific receptor, the vitamin D receptor (VDR) (Abboud et al., 2022). In addition, higher levels of serum vitamin D cause breast cancer women to survive twice more than those with low levels, Also, up to 78% of breast cancers cells contain vitamin D receptors which might prevent tumor growth and eradicate carcinogenic cells due to an increase in blood supply (Ahmed et al., 2020). Hypervitaminosis D, another name for vitamin D toxicity, is an uncommon but potentially dangerous illness that arises from having too much vitamin D in the body (Janoušek et al., 2022). Vitamin D consumption increases tissues concentration of vitamin D (Lim and Thadhani., 2020). High vitamin D levels inhibit cell growth and division and can lead to cell death (Karagul et al., 2020). Usually, high dosages of vitamin D supplements—rather than food or sun exposure—cause vitamin D toxicity (Marcinowska-Suchowierska et al., 2018; Galior et al., 2018). This is due to the fact that even fortified foods don’t contain significant levels of vitamin D, and the body controls how much vitamin D is created by sun exposure (Gillie, 2006; Zareef and Jackson, 2021). Supplementation may infrequently cause vitamin D intoxication (VDI), however reports of it have increased recently (Hu et al., 2023). The toxicity of non-target species was reduced, and the chance of secondary poisoning was decreased when cholecalciferol was used as a rodenticide, so, cholecalciferol, or vitamin D3, is thought to be a safe option as rodenticides (Noh et al., 2023).
MATERIALS AND METHODS
The current investigation was carried out between December 1, 2022, and March 25, 2023. 75 healthy female albino rats, weighing 180 ± 30 grams and aged 10–14 weeks, were used in the present investigation. For two weeks, the experimental rats were given conventional rat food and water and were allowed to become well-acclimated to the laboratory environment. These habituated albino rats were then employed in two experiments. In the first experiment, 45 rats were utilized in accordance with Dixon’s procedure (Dixon., 1965) to determine the lethal dose. A solution of cholecalciferol (vitamin D) was used to estimate the median lethal dose (LD50) of the experimental compounds under study. In the second experiment, thirty animals were given two different vitamin D doses over two distinct time periods. The selected groups were divided according to the doses they received. Initially, they were split into three major groups, each with ten rats. Within each group, there were two subgroups, each with five rats, representing varying dosages of vitamin D (10 individuals per group and five rats each cage). Cholecalciferol was used as a source of VD, and rats were fed a basic diet with different levels of VD in each group.
Ethics Approval
The project was approved by the Research Ethics Committee, College of Veterinary Medicine, Baghdad, Iraq. (P-G/2467, 6/11/2023). All experiments with rats were conducted in the animal house located in the College of Veterinary Medicine at the University of Baghdad.
Determination Of Ld 50 For Vitamin D By Dixon’s (Up And Down) Method
Finding the median lethal dosage (LD50) of a substance is a crucial first step in determining its potential for toxicity (Morris-Schaffer and McCoy, 2020). The experimental test compound, a stock solution of vitamin D3, was a prepared solution (0.25 mg/ml). The solution was brought to room temperature before use. 45 rats were utilized in accordance with Dixon’s (Up and Down) method in order to determine the Median Lethal Dose (LD50). Different doses quantitatively 0.5, 1, 1.5, 2, 2.5, 3, 4, 5, 6, 7, 8, 9, 10, 11, 12, 13, 14, 15 and 16 mg/kg b.w. of Vitamin D were administered to animals through a stainless-steel gavage tube to female albino rats. After 24 hours, the mortality and survival number of rats were recorded for each dose. Dixon’s (up and down) method was used (Dixon., 1965) for LD50 determination (Tables 1, 8, 9). The dose that was started depends on Özkan (Özkan et al., 2012).
Determination Of Residual Amount Of Cholecalciferol
Tissue residues were quantified using the protocol outlined by Kennedy (Kennedy, 1986).
Cytogenetic Study
The metrics used in the cytogenetic analysis followed Dutta (2022) methodology.
Histopathology
At the end of the exposure period of 45 and 90 days, rats were taken from each plastic cage. Tissues like the liver, kidney, and muscles were isolated from normal and experimental rats. The samples were initially fixed in a 10% formalin buffer for 24 hours and then processed and embedded in paraffin for block (56–58 °C) preparation. The sections were cut at 5–6 microns and stained with hematoxylins and eosin (Nagpal et al., 2023). The slides were examined under a light microscope and photographed for histopathological study.
Table 1: Pilot study shows the dead and survived animals after 24 hours from treating with Vitamin D, by using different doses for LD50 determination.
Dose (mg/kg) |
Animals, number |
Survived animals |
Dead animals |
0.5 |
2 |
0 |
2 |
1 |
2 |
0 |
2 |
1.5 |
2 |
0 |
2 |
2 |
2 |
0 |
2 |
2.5 |
2 |
0 |
2 |
3 |
2 |
0 |
2 |
4 |
2 |
0 |
2 |
5 |
2 |
0 |
2 |
6 |
2 |
0 |
2 |
7 |
2 |
0 |
2 |
8 |
2 |
0 |
2 |
9 |
2 |
0 |
2 |
10 |
2 |
1 |
1 |
11 |
2 |
1 |
1 |
12 |
2 |
1 |
1 |
13 |
2 |
1 |
1 |
14 |
2 |
2 |
0 |
15 |
2 |
2 |
0 |
16 |
2 |
2 |
0 |
Statistical Analysis
The results were subjected to statistical analysis in order to identify the differences between the different results. Using the Windows SPSS (Version 19) statistical program, the sample methods were evaluated using the ANOVA test, and the mean (mean ± S.D.) was found. P ≤0.05 values were considered significant (Kim, 2017).
RESULTS
Clinical Signs
In this study, both groups (HG and LG) of rats were observed to have vitamin D toxicity symptoms. Clinically, vitamin D3-treated rats were dull, off-feed, and showed anorexia, severe diarrhea, severe dehydration, excessive thirst, weakness, rigidity of limbs, and significant progressive emaciation. There were also changes in body weight.
Determination Of Ld 50
The LD 50 for VD was measured according to Dixon’s calculation.
LD50 = xf + kd
= 13 + (0.741) × 1
= 13 + 0.741
= 13.741 mg/kg
Applying this calculation, LD50 came out to be 13.741 mg/kg b. wt. for Vitamin D
The Residual Concentration
The residual concentration showed insignificant increases in kidney and liver during both periods (45 days and 90 days) Tables (2) and Table (3). For the muscle, there was a significant increasing which reach to (4.051±0.436 in group 2, and 4.191±0.52 in group 3 after 45 days. In addition to (4.854±0.867 in group 2, and 4.949±0.848 in group 3 after 90 days) Table (4).
Cytogenetic Study
The result of cytogenetic study showed presence of cytogenetic effects for vitamin D, especially in the high VD group (1.3741 mg/kg. bw VD) at 1/10LD50 as compared with low VD group (0.6875 mg/kg. bw VD) 1/20LD50, that showed a significant increase in Mitotic Index (MI) reaching (6.891±1.093 in group 2 (1/10 LD50) after 45 days., 6.832±0.635 in group 3 (1/20 LD50) after 45 days) with insignificant increase reaching 7.364±1.237 in group 2 (1/10 LD50) after 90 days., 7.304±1.202 in group 3 (1/20 LD50) after 90 days), in addition to significant increase in Micronuclei (MN) in both groups and after both periods as compared with the control group Table (5). (Fig. 1) and (Fig. 2).
Table 2: Shows the residual concentration of vitamin D in kidneys after 45 days and after 90 days of experiment
Kidney/Groups |
Before 45 days |
After 45 days |
P Value |
Sign. |
Before 90 days |
After 90 days |
P Value |
Sign. |
Control Group I |
A,a 4.803±0.628 |
B,a 4.357±0.559 |
0.468 |
Non Sign. |
A,a 5.025±0.543 |
AB,a 5.21±0.324 |
0.546 |
Non Sign. |
Group II Vit.D 1/10 |
A,a 4.803±0.628 |
A,a 5.178±0.383 |
0.436 |
Non Sign. |
A,a 5.025±0.543 |
AB,a 5.197±0.597 |
0.705 |
Non Sign. |
Group III Vit.D 1/20 |
A,b 4.803±0.628 |
A,a 5.459±0.303 |
0.0011 |
Sign. |
A,a 5.025±0.543 |
A,a 5.503±0.583 |
0.541 |
Non Sign. |
P-Value |
0.0062 |
0.0036 |
||||||
LSD |
0.530865 |
0.619874 |
Table 3: Shows the residual concentration of vitamin D in livers after 45 days and after 90 days of experiment.
Liver /Groups |
Before 45 days |
After 45 days |
P Value |
Sign. |
Before 90 days |
After 90 days |
P Value |
Sign. |
Control Group I |
A,a 4.803±0.628 |
A,a 4.713±0.525 |
0.355 |
Non Sign. |
A,a 5.019±0.685 |
A,a 5.153±0.343 |
0.308 |
Non Sign. |
Group II Vit.D 1/10 |
A,a 4.599±0.584 |
A,a 5.045±0.38 |
0.438 |
Non Sign. |
A,a 5.019±0.685 |
A,a 4.847±0.608 |
0.709 |
Non Sign. |
Group III Vit.D 1/20 |
A,a 4.599±0.584 |
A,a 4.962±0.299 |
0.216 |
Non Sign. |
A,a 5.019±0.685 |
A,a 5.108±0.666 |
0.430 |
Non Sign. |
P-Value |
0.00046 |
0.008 |
||||||
LSD |
0.473691 |
0.58208 |
Table 4: Shows the residual concentration of vitamin D in muscles after 45 days and after 90 days of experiment
Muscles/Groups |
Before 45 days |
After 45 days |
P Value |
Sign. |
Before 90 days |
After 90 days |
P Value |
Sign. |
Control Group I |
A,a 3.166±0.77 |
AB,a 3.561±0.571 |
0.522 |
Non Sign. |
A,a 5.025±0.543 |
AB,a 5.21±0.324 |
0.546 |
Non Sign. |
Group II Vit.D 1/10 |
A,a 3.166±0.77 |
A,b 4.051±0.436 |
0.0006 |
Sign. |
A,a 5.025±0.543 |
AB,a 5.197±0.597 |
0.705 |
Non Sign. |
Group III Vit.D 1/20 |
A,a 3.166±0.77 |
A,b 4.191±0.52 |
0.0014 |
Sign. |
A,a 5.025±0.543 |
A,a 5.503±0.583 |
0.541 |
Non Sign. |
P-Value |
0.00062 |
0.0036 |
||||||
LSD |
0.681356 |
0.619874 |
Table 5: Shows the Micronuclei (MN), and Mitotic Index (MI) after 45 days and after 90 days of experiment.
Groups |
MN % After 45 days |
MN % After 90 days |
MI % After 45 days |
MI % After 90 days |
Group Control (CG) |
C 5.483±0.625 |
C 6.391±0.923 |
B 5.723±0.778 |
C 6.413±0.775 |
Group 2 (HG) 1/10 LD50 |
AB 7.983±0.799 |
A 8.46±1.09 |
A 6.891±1.093 |
BC 7.364±1.237 |
Group 3 (LG) 1/20 LD50 |
AB 7.537±0.704 |
A 8.238±1.403 |
A 6.832±0.635 |
BC 7.304±1.202 |
LSD |
0.907049 |
1.064587 |
1.017477 |
1.342605 |
In addition to the changes in chromosomal aberration (which appear 0.439±0.2026 Deletion %., 0.344±0.1319 Dicentric %., 0.348±0.1475 Acentric %., 0.3944±0.1359 Ring %., 0.3417±0.1241 Chromatid Gap %., 0.3961±0.1438 Chromosome Gap %., 0.3961±0.1438 Chromatid break %., 0.4464±0.1233 Chromosome break % in high dose group (HG) after 45 days., while in low dose group (LD) the result was 0.3497±0.1453 Deletion %., 0.5005±0.1955 Dicentric %., 0.251±0.252 Acentric %., 0.2957±0.1013 Ring %., 0.3454±0.1292 Chromatid Gap %., 0.2952±0.2029 Chromosome Gap %., 0.401±0.298 Chromatid break %., 0.3454±0.1292 Chromosome break % after 45 days) Table (6). (Fig. 3) and (Fig. 4), in the period of 90 days the results for the Group 2 (HG) 1/10LD50, the results were 0.4382±0.183 Deletion %., 0.3924±0.1239 Dicentric %., 0.3468±0.1381 Acentric %., 0.3468±0.1381 Ring %., 0.3924±0.1239 Chromatid Gap %., 0.4936±0.1688 Chromosome Gap %., 0.4981±0.1854 Chromatid break %.,
Table 6: Shows the Chromosomal aberration after 45 days of experiment.
Groups |
Dele-tion % |
Dice-ntric % |
Acen-tric % |
Ring % |
Chro-matid Gap % |
Chromo-some Gap % |
Chro-matid break % |
Chromo-some break % |
Total % |
Group Control (CG) |
A 0.2181± 0.1524 |
A 0.261± 0.1762 |
A 0.2208± 0.162 |
A 0.338± 0.198 |
A 0.1778± 0.1144 |
B 0.1439± 0.1463 |
B 0.1853± 0.1399 |
B 0.2144± 0.0743 |
B 1.759± 0.606 |
Group 2 (HG) 1/10LD50 |
A 0.439± 0.2026 |
A 0.344± 0.1319 |
A 0.348± 0.1475 |
A 0.3944± 0.1359 |
A 0.3417± 0.1241 |
A 0.3961± 0.1438 |
AB 0.3961± 0.1438 |
A 0.4464± 0.1233 |
A 3.106± 0.422 |
Group 3 (LG) 1/20LD50 |
A 0.3497± 0.1453 |
A 0.5005± 0.1955 |
A 0.251± 0.252 |
A 0.2957± 0.1013 |
A 0.3454± 0.1292 |
AB 0.2952± 0.2029 |
AB 0.401± 0.298 |
AB 0.3454± 0.1292 |
A 2.784± 0.7 |
LSD |
0.197235 |
0.215699 |
0.224377 |
0.179413 |
0.920742 |
Table 7: Shows the Chromosomal aberration after 90 days of experiment.
Groups |
Dele-tion % |
Dice-ntric % |
Acen-tric % |
Ring % |
Chro-matid Gap % |
Chromo-some Gap % |
Chro-matid break % |
Chromo-some break % |
Total % |
Group Control (CG) |
A 0.2587± 0.1093 |
A 0.2617± 0.2098 |
A 0.3307± 0.1644 |
A 0.3307± 0.1644 |
B 0.2189± 0.1515 |
A 0.2953± 0.1082 |
C 0.2277± 0.1633 |
A 0.2216± 0.1578 |
B 2.218± 0.579 |
Group 2 (HG) 1/10LD50 |
A 0.4382± 0.183 |
A 0.3924± 0.1239 |
A 0.3468± 0.1381 |
A 0.3468± 0.1381 |
AB 0.3924± 0.1239 |
A 0.4936± 0.1688 |
AB 0.4981± 0.1854 |
A 0.4975± 0.1821 |
A 3.46± 0.501 |
Group 3 (LG) 1/20LD50 |
A 0.408± 0.228 |
A 0.361± 0.231 |
A 0.2546± 0.1787 |
A 0.2546± 0.1787 |
AB 0.355± 0.227 |
A 0.405± 0.29 |
ABC 0.4076± 0.1365 |
A 0.4605± 0.1171 |
AB 3.058± 0.568 |
LSD |
0.220606 |
0.208468 |
0.916095 |
0.4975±0.1821 Chromosome break %., in the Group 3 (LG) 1/20LD50, the results were 0.408±0.228 Deletion %., 0.361±0.231 Dicentric %., 0.2546±0.1787 Acentric %., 0.2546±0.1787 Ring %., 0.355±0.227 Chromatid Gap %., 0.405±0.29 Chromosome Gap %., 0.4076±0.1365 Chro matid break %., 0.4605±0.1171Chromosome break %. Table (7). (Fig. 5) and (Fig. 6).
Gross Pathological Examination
All samples were collected after 45 days and after 90 days of experimental periods from anesthetized rats. Post-mortem examination of rats poisoned with cholecalciferol has shown congestion and hemorrhages in all visceral organs.
Histopathological Study
The histopathological study of tissues affected by toxic cholecalciferol exhibited varying stages of mild to severe degenerative changes and necrosis of the tissues.
LIVER
The lesions after 45 days showed simple histopathological changes in the liver, which were represented by congestion of the hepatic sinusoids and central vein (Fig. 7: A). In addition to cellular swelling and congestion of blood vessels (Fig. 7: B). At dose 1/20LD50 (274.820 IU, i.e., 0.6875 mg/kg body weight), lesions appear milder than at dose 1/10LD50 (549.640 IU, i.e., 1.3741 mg/kg body weight).but it can progress more severely in the period of 90 days, that shows severe inflammation as represented by pericentral necrosis and marked infiltration of inflammatory cells (Fig. 7: C). In the lower toxic dose (1/20LD50), besides congestion of the central vein, there was slight fibrosis in pericentral necrotic areas due to cholecalciferol toxicity (Fig. 7: D).
KIDNEY
Histological descriptions of kidneys reveal renal injury of variable intensity, congestion with inflammation, and toxic tubular necrosis. The severity of the lesion was noted in the 45th day, which is less severe than the lesion in the 90th days, which was characterized by the infiltration of inflammatory cells along with the presence of hyaline cast with sloughing in the epithelial lining of urinary tubules (Fig. 7: E), In the period of 90 days, in group II (HG), severe infiltration of inflammatory cells in interstitial tissue (Fig. 7: F, G, H, and J), in addition to necrosis, was also observed (7: I). In group III (LG), there is sloughing of the epithelium lining urinary tubules (Fig. 7: K) and hyaline casts were also present with dilation of Bowman space (Fig. 7: L), and glomerular congestion with vacuolation was observed in renal tubules (Fig. 7: M). Along with the degenerative changes (swelling) of varying severity in the renal tubular epithelium and infiltration of inflammatory cells (Fig. 7: N).
MUSCLES
In the muscle, the lesions were very staggering and became more severe as the dose increased or the period increased. In the 45th day (1/10 LD50) (549.640 IU, i.e. 1.3741 mg/kg body weight), There was fragmentation in addition to the presence of necrosis (Fig. 7: O), The severity of inflammation increased with the period of 90 days. At the 90th day (1/20LD50), edema causes separation of the muscle’s fibers besides infiltration of inflammatory cells, in addition to the presence of fragmentation and necrosis (Fig. 7: P). All these changes are clearly evident, especially at the dose (1/10 LD50) (549.640 IU, i.e., 1.3741 mg/kg body weight), where they lead to lesions in the muscle, in addition to lesions varying in doses or periods.
Table 8: Shows the doses of Vitamin D by using Dixon’s method for LD50 determination. Survived (O) and dead (X) Result was (OOOXOXO)
Dose (mg/kg) |
Survived and dead animals |
11 |
O |
12 |
O |
13 |
O |
14 |
X |
13 |
O |
14 |
X |
13 |
O |
Table 10: List of the abbreviations
Abbreviations |
Full name |
bw |
body weight |
°C |
centigrade |
CG |
CG control group |
HG |
High VD group |
i.e. |
That is |
IU |
International Units |
LD50 |
Median Lethal Dose |
LG |
Low VD group |
mg/kg |
milligram/kilogram |
MI |
Mitotic Index |
MN |
Micronuclei |
SD |
Standard Deviation |
VDI |
Vitamin D Intoxication |
VDR |
Vitamin D Receptors |
VD |
Vitamin D |
VD3 |
Vitamin D3 |
DISCUSSION
Median Lethal Dose (LD50) came out to be 13.741 mg/kg b. wt. for Vitamin D; this value disagrees with previous studies such as (Özkan et al., 2012; Singla and Kaur., 2015). This difference may be due to the uneven pharmacological purity among suppliers’ origins, the individual variation among numbers of rats, or perhaps the altered surroundings. The results show a significant decline in daily change in body weight, in both dosed groups during the dosing period, which concurs with the research that Marcinowska conducted (Marcinowska-Suchowierska et al., 2018). Higher oxidative stress can promote the acceleration of cell death, while lower oxidant levels may promote slower cell death. That is why higher vitamin D toxicity (VDT) is severer than lower vitamin D toxicity (VDT), which also agrees with Nicotera (Nicotera and Orrenius., 1994). Since the target tissue organs of vitamin D are the kidney, liver, and muscle, that is why vitamin D toxicity (VDT) killed cells of these tissues, which also agrees with the other researchers (Wimalawansa, 2019). Microscopic lesions were seen in the kidneys of both dosed rats killed at the end of the first and second periods, which agrees with the study conducted by Abbas and Al-Shaha (2021).A hyperdose of vitamin D led to congestion of blood vessels with degeneration in hepatocytes that is showing fibrosis; this agrees with previous studies (Chavhan et al., 2011; Lim and Thadhani., 2020). The groups II and III were characterized by highly aggregation of inflammatory cells, which concurs with the research that Qaisi conducted (Al-Qaisi, 2000). Histopathological examination showed infiltration of the nuclear cell, which agrees with the findings of Ahmed and Mohammed’s research (Ahmed and Mohammed.,2022). The histopathological examination of the kidney shows congestion of blood vessels and infiltration with neutrophils in the lumen, which concurs with Saffar’s research findings (AL-Saffar, 2012). Glomerular lesions in groups II and III were found, characterized by dilation of glomeruli, which showed lipid accumulation, which is consistent with Ibrahim Mustafa’s and Elkhadragy’s research (Ibrahim Mustafa., 1996; Elkhadragy et al., 2022). The results indicated that cholecalciferol significantly increased the micronucleus in groups II and III, which concurs with the research that Qaisi conducted (Al-Qaisi, 2000).
CONCLUSION
Vitamin D consumption increases tissue levels of vitamin D supplements (1/10 LD50 and 1/20 LD50) compared with a control group. From the results of this study, it can be concluded that oral intake of lethal dose of cholecalciferol (vitamin D3) by rats led to their toxicity in the form of mineralization in the vital organs and resulted in the mortality of rats. This preliminary study shows that both doses of vitamin D can be toxic to organisms at higher levels, so they need to be used carefully and should not be taken excessively.
ACKNOWLEDGEMENTS
The author would like to thank all who supported the study, particularly the staff of the department of pathology and poultry and the laboratory staff in the college. Also, I’d like to register my great thanks to all participants of the study hoping to them and their baby’s good health and fine life.
RECOMMENDATIONS
Study of vitamin D intoxication influence in the brain and bones. More study is needed to know the effect of different doses of vitamins on human and animal health.
NOVELTY STATEMENT
In recent years, there has been a renaissance in the study of vitamin D actions as evidence continues to accumulate about its role in the etiology of chronic diseases such as infection response, autoimmune disease, cardiovascular disease, diabetes mellitus, and cancer. The novelty of the study is focusing on cytogenetic, histopathological, and residual concentrations of vitamin D hyperdoses that influence tissues (livers, kidneys, and muscles) due to their pathological toxic effects.
AUTHORS CONTRIBUTION
Both of these authors contributed equally.
CONFLICT OF INTEREST
The authors have declared no conflict of interest.
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