Distribution and form of uranium-containing deposits in chickens treated with uranyl nitrate

Temporal Clinical Chemistry and Microscopic Renal Effects Following Acute Uranyl Acetate Exposure

Military use of depleted uranium (DU) has renewed interest in the toxicology of this metal. In this study, the nephrotoxicity of single exposure DU was assessed with and without pre-exposure stress. Adult male Sprague–Dawley rats (n = 288) were administered a single IM dose of 0, 0.1, 0.3 or 1.0 mg/kg DU. Corticosterone concentrations (ng/ml, mean ± SD) were 763.65 ± 130.94 and 189.80 ± 90.81 for swim stressed and unstressed rats. Serum and kidney uranium concentration, hematocrit, chemistry, and renal histology were assessed on sacrifice days 1, 3, 7 and 30 post-DU-dosing. Dose related increases in serum and kidney uranium were noted. DU concentration peaked day 1 in the kidney and days 3–7, in the serum. Dose-related elevations of Cr and BUN concentrations were seen on days 3 and 7. A decline in serum albumin coincided with Cr and BUN suggesting protein losing nephropathy. Dose related acute tubular necrosis and proliferative glomulonephritis were seen. Tubular regeneration in low dose rats was almost complete by day 30. High dose rats had extensive tubular necrosis and delayed regeneration with focal residual chronic interstitial nephritis and cortical scarring. Glomular changes were reversed in all treatment groups by day 30. Stress exposure had no impact on any measured renal parameter.

Chronic Exposure to Uranium Leads to Iron Accumulation in Rat Kidney Cells

After it is incorporated into the body, uranium accumulates in bone and kidney and is a nephrotoxin. Although acute or short-term uranium exposures are well documented, there is a lack of information about the effects of chronic exposure to low levels of uranium on both occupationally exposed people and the general public. The objective of this study was to identify the distribution and chemical form of uranium in kidneys of rats chronically exposed to uranium in drinking water (40 mg uranium liter(-1)). Rats were killed humanely 6, 9, 12 and 18 months after the beginning of exposure. Kidneys were dissected out and prepared for optical and electron microscope analysis and energy dispersive X-ray (XEDS) or electron energy loss spectrometry (EELS). Microscopic analysis showed that proximal tubule cells from contaminated rats had increased numbers of vesicles containing dense granular inclusions. These inclusions were composed of clusters of small granules and increased in number with the exposure duration. Using XEDS and EELS, these characteristic granules were identified as iron oxides. Uranium was found to be present as a trace element but was never associated with the iron granules. These results suggested that the mechanisms of iron homeostasis in kidney could be affected by chronic uranium exposure.

Uranyl nitrate-induced proximal tubule alterations in rabbits: a quantitative analysis

Naturally occurring uranium in drinking water is a significant health concern in several areas of North America. Because the kidney is a known target organ to examine the effects of uranium or its compounds, the objective of this study was to determine whether kidney repair occurs after exposure to, and withdrawal of, uranyl nitrate (UN). This work, part of a larger study to establish safe levels of uranium in drinking water supplies, examined the ultrastructural changes in proximal tubule cells of New Zealand white rabbits following subchronic exposure to UN in water and for 91 days after exposure ended. The rabbit was chosen as the experimental animal because of its high sensitivity to uranium. Animals were exposed to 24 or 600 mg UN per liter (UN/L) in drinking water for 91 days, with no recovery or recovery periods of 45 or 91 days. Ultrastructural changes, quantified by a stereological image analysis system based on point counting, were observed in renal proximal tubules (PTs). Each electron micrograph was statistically considered an experimental unit. The severity of lesions was directly proportional to the dose. Animals exposed to 600 mg UN/L had the most severe lesions; nevertheless, alterations were remarkable in animals exposed to the low dose. At both recovery periods, the lesions were significantly more severe than those in animals of the no-recovery group, which may result from the kidney's ability to store uranium. The PT cells had increased lysosomal and vacuolar mass as well as variations in mitochondrial mass. In addition, there was epithelial cell degeneration with a focal loss of brush borders, thickening and splitting of tubular basement membrane, and occasionally cell necrosis. Interstitial fibrosis of the renal cortex persisted as the recovery period increased in the animals of UN-dosed groups. Alterations may be due to disturbed fluid transport across the PT and other cells and decreased cell respiration resulting from damaged cell constituents. Cell damage caused by UN in drinking water persisted throughout the 91-day recovery period. By eventually determining the no observable effect level for the kidney by UN, this study may assist in devising a model to ascertain the safe levels of uranium in water.