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. 2023 Sep 19;11(9):791.
doi: 10.3390/toxics11090791.

Toxic Kidney Damage in Rats Following Subchronic Intraperitoneal Exposure to Element Oxide Nanoparticles

Affiliations

Toxic Kidney Damage in Rats Following Subchronic Intraperitoneal Exposure to Element Oxide Nanoparticles

Yuliya V Ryabova et al. Toxics. .

Abstract

Chronic diseases of the urogenital tract, such as bladder cancer, prostate cancer, reproductive disorders, and nephropathies, can develop under the effects of chemical hazards in the working environment. In this respect, nanosized particles generated as by-products in many industrial processes seem to be particularly dangerous to organs such as the testes and the kidneys. Nephrotoxicity of element oxide particles has been studied in animal experiments with repeated intraperitoneal injections of Al2O3, TiO2, SiO2, PbO, CdO, CuO, and SeO nanoparticles (NPs) in total doses ranging from 4.5 to 45 mg/kg body weight of rats. NPs were synthesized by laser ablation. After cessation of exposure, we measured kidney weight and analyzed selected biochemical parameters in blood and urine, characterizing the state of the excretory system. We also examined histological sections of kidneys and estimated proportions of different cells in imprint smears of this organ. All element oxide NPs under investigation demonstrated a nephrotoxic effect following subchronic exposure. Following the exposure to SeO and SiO2 NPs, we observed a decrease in serum creatinine and urea, respectively. Exposure to Al2O3 NPs caused an increase in urinary creatinine and urea, while changes in total protein were controversial, as it increased under the effect of Al2O3 NPs and was reduced after exposure to CuO NPs. Histomorphological changes in kidneys are associated with desquamation of the epithelium (following the exposure to all NPs except those of Al2O3 and SiO2) and loss of the brush border (following the exposure to all NPs, except those of Al2O3, TiO2, and SiO2). The cytomorphological evaluation showed greater destruction of proximal sections of renal tubules. Compared to the controls, we observed statistically significant alterations in 42.1% (8 of 19) of parameters following the exposure to PbO, CuO, and SeO NPs in 21.1% (4 of 19)-following that, to CdO and Al2O3 NPs-and in 15.8% (3 of 19) and 10.5% (2 of 19) of indicators, following the exposure to TiO2 and SiO2 nanoparticles, respectively. Histomorphological changes in kidneys are associated with desquamation of epithelium and loss of the brush border. The cytomorphological evaluation showed greater destruction of proximal sections of renal tubules. The severity of cyto- and histological structural changes in kidneys depends on the chemical nature of NPs. These alterations are not always consistent with biochemical ones, thus impeding early clinical diagnosis of renal damage. Unambiguous ranking of the NPs examined by the degree of their nephrotoxicity is difficult. Additional studies are necessary to establish key indicators of the nephrotoxic effect, which can facilitate early diagnosis of occupational and nonoccupational nephropathies.

Keywords: kidney diseases; nanoparticles; nephrotoxicity; occupational exposure; oxides; urogenital system.

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Conflict of interest statement

The authors declare no conflict of interest.

Figures

Figure 1
Figure 1
Histological picture of kidneys in control and EO-NP-exposed animals, periodic acid–Schiff staining, a 90× magnification for top and middle rows, and 400× magnification for bottom row. (a) Controls in the experiment with Al2O3, TiO2 and SiO2 NPs; animals exposed to (b) Al2O3 NPs, (c) TiO2 NPs, and (d) SiO2; (e) controls in the experiment with CdO and PbO NPs; animals exposed to (f) CdO NPs and (g) PbO NPs; (h) controls in the experiment with SeO and CuO NPs; and animals exposed to (i) SeO NPs and (j) CuO NPs. Black scale bars—35 mkm. The black arrow points at dilated renal tubules, and the green arrow marks pronounced dystrophic and necrobiotic changes.
Figure 2
Figure 2
Loss of the brush border in rat kidney tissues following exposure to selected element oxide nanoparticles compared to the controls; the value of the indicator in each control group was taken as 1; values of the indicator in other groups were normalized to the control. Statistically significant difference from the corresponding values in *—control group (p < 0.05 via Student’s t-test).
Figure 3
Figure 3
Percentage of desquamated epithelial cells in the kidneys of the rats exposed to selected element oxide nanoparticles compared to controls. Statistically significant difference from the corresponding values in *—control group (p < 0.05 via Student’s t-test).

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