Gastrointestinal absorption of uranium in humans.

The gastrointestinal absorption factor (f1) for uranium in humans has been determined from a study of 50 volunteers, ingesting uranium at natural levels in drinking water and food. The purpose of the study was to find an appropriate f1 value for humans to use in deriving exposure guidelines for uranium. The participants ranged in age from 13 to 87 years. They were selected from two communities: New Ross, Nova Scotia with elevated uranium in drinking water, and Ottawa, Ontario with very low levels of uranium. Uranium intake and excretion were measured in samples collected concurrently from the same individuals over a three-day period. The duplicate diet method was used to monitor uranium intake in food and water. Uranium levels in all samples were measured by inductively coupled plasma mass spectrometry (ICP/MS). The distribution of f1 values obtained was non-Gaussian with a range of 0.001 to 0.06 and a median of 0.009. Seventy-eight percent of the subjects had values less than 0.02. These values are consistent with the recommendations of ICRP 69. The f1 values were not gender-sensitive and were independent of age at time of study, duration of exposure, and total uranium intake. The implications of these findings are discussed in terms of setting drinking water guidelines.

Chronic ingestion of uranium in drinking water: a study of kidney bioeffects in humans.

A study was conducted of the chemical effects on the human kidney induced by the chronic ingestion of uranium in drinking water. Subjects were divided into two groups: The low-exposure group, whose drinking water was obtained from a municipal water system and contained < 1 microgram uranium/L, and the high-exposure group, whose drinking water was obtained from private drilled wells and contained uranium levels that varied from 2 to 781 micrograms/L. Years of residence varied from 1 to 33 years in the low-exposure group and from 3 to 59 years in the high-exposure group. The indicators of kidney function measured in this study included glucose, creatinine, protein, and beta 2-microglobulin (BMG). The markers for cell toxicity studied were alkaline phosphatase (ALP), gamma-glutamyl transferase (GGT), lactate dehydrogenase (LDH), and N-acetyl-beta-D-glucosaminidase (NAG). Urinary glucose was found to be significantly different and positively correlated with uranium intake for males, females, and pooled data. Increases in ALP and BMG were also observed to be correlated with uranium intake for pooled data. In contrast, the indicators for glomerular injury, creatinine and protein, were not significantly different between the two groups nor was their urinary excretion correlated to uranium intake. These results suggest that at the intakes observed in this study (0.004 microgram/kg to 9 micrograms/kg body wt), the chronic ingestion of uranium in drinking water affects kidney function and that the proximal tubule, rather than the glomerulus, is the site for this interference.

Uranyl nitrate: 91-day exposure and recovery studies in the male New Zealand white rabbit.

This study was undertaken to examine the reversibility of renal injury in the male New Zealand White rabbit subsequent to a 91-day exposure to uranyl nitrate (UN) in drinking water, followed by various recovery periods. Specific pathogen-free (SPF) animals were exposed for 91 days to UN in their drinking water (24 or 600 mg UN/L). Control groups were given municipal tap water (< 0.001 mg U/L). Regular clinical observations were recorded, and urine was collected periodically. Recovery periods between the last UN exposure and termination were 0, 8, 14, 45, or 91 days. Following the study, all animals were anesthetized and terminated by exsanguination, and multiple hematological and biochemical parameters were determined. Necropsies were conducted, and histopathological examination was performed. Exposure-related histopathological changes were observed only at much higher doses than in our previous male rabbit study where non-SPF-free animals had been used. Minor increases in kidney to body weight ratios were observed in the high-dose groups following exposure and early recovery. Renal tubular injury with degenerative nuclear changes, cytoplasmic vacuolation, and tubular dilation was seen in the high-dose group, without consistent resolution even after 91 days recovery. Animals ingested approximately 33% more uranium per day in this study than did males in a comparable dose group in the previous study, yet their kidney tissue uranium residues were 30% lower. These results suggest that SPF rabbits are less sensitive to uranyl injury than the non-SPF animals. The lowest-observed-adverse-effect level is estimated to lie at or below 24 mg UN/L.

Absorption and retention of uranium from drinking water by rats and rabbits.

Uranium in the form of uranyl nitrate hexahydrate was administered in drinking water to Sprague-Dawley rats for periods of 28 and 91 d and New Zealand White rabbits for 91 d. The animals consumed food and water ad libitum. Subgroups of rabbits were followed for recovery periods of up to 91 d; 24-h collections of urine and feces were performed for some of the rabbits at various times during the exposure and recovery periods. At the end of the experiment, all animals were sacrificed and femur and kidney samples were analyzed for uranium residues. The results show that both rats and rabbits absorb about 0.06% of ingested uranium in the gastrointestinal (GI) tract. The distribution and retention of uranium in the skeleton and kidneys of rats are comparable to parameters reported for humans. The retention half-time in rabbit bone is substantially longer than for humans. The implications of extrapolating from animal data to effects on humans are discussed.

Transfer of 226Ra, 210Pb and uranium from soil to garden produce: assessment of risk.

A study of gardens contaminated by uranium processing wastes was carried out in the town of Port Hope, Ontario, during the summer of 1976. Concentrations of 226Ra, 210Pb, and total uranium were measured in soils and in garden produce. Highest concentrations were found in root and stem vegetables and, for radium, also in leafy vegetables. Fruit generally showed the lowest values. Uptake was consistent with a linear dependence on soil concentration. Mean concentration factors of 1.1 X 10(-3), 0.37 X 10(-3), and 0.075 X 10(-3) were obtained for 226Ra, 210Pb, and uranium, respectively. The highest estimated dose to an individual who ingested produce from a contaminated garden was 68 mrem/yr to bone surface from 226Ra. The implications of these findings for other communities affected by nuclear fuel-cycle operations are discussed.