Radionuclides in the terrestrial ecosystem near a Canadian uranium mill--Part II: Small mammal food chains and bioavailability

210Po sequential extraction applied to wetland soils at uranium mining sites

Former uranium mining activities have led to the presence of naturally occurring nuclides embedded in soil. Such activities have also modified the secular equilibrium between radionuclides in ²³⁸U decay series. The objective of this paper is to quantify the long-term effect of former uranium mining activities on the behavior of the final radionuclide in the ²³⁸U-series, i.e. polonium-210 (²¹⁰Po), present in soils. Soil samples are extracted from two uranium sites in France, specifically a quarried site and a natural site. The polonium distribution is studied within the various soil fractions, namely: water soluble, exchangeable, bound to carbonates, bound to iron/manganese oxides, bound to organic matter, and residual. ²¹⁰Po is mainly found in the residual fraction of both study sites (87-90%), followed by the carbonates fraction (5-9%). The ²¹⁰Po activity in the other fractions is very small in comparison with total activity.

Accumulation of plutonium in mammalian wildlife tissues following dispersal by accidental-release tests

We examined the distribution of plutonium (Pu) in the tissues of mammalian wildlife inhabiting the relatively undisturbed, semi-arid former Taranaki weapons test site, Maralinga, Australia. The accumulation of absorbed Pu was highest in the skeleton (83% ± 6%), followed by muscle (10% ± 9%), liver (6% ± 6%), kidneys (0.6% ± 0.4%), and blood (0.2%). Pu activity concentrations in lung tissues were elevated relative to the body average. Foetal transfer was higher in the wildlife data than in previous laboratory studies. The amount of Pu in the gastrointestinal tract was highly elevated relative to that absorbed within the body, potentially increasing transfer of Pu to wildlife and human consumers that may ingest gastrointestinal tract organs. The Pu distribution in the Maralinga mammalian wildlife generally aligns with previous studies related to environmental exposure (e.g. Pu in humans from worldwide fallout), but contrasts with the partitioning models that have traditionally been used for human worker-protection purposes (approximately equal deposition in bone and liver) which appear to under-predict the skeletal accumulation in environmental exposure conditions.

Uranyl Nitrilotriacetate, a Stabilized Salt of Uranium, is Genotoxic in Nontransformed Human Colon Cells and in the Human Colon Adenoma Cell Line LT97

Previous uranium mining in the "Wismut" region in Germany enhanced environmental distribution of heavy metals and radionuclides. Carryover effects may now lead to contamination of locally produced foods. Compounds of "Wismut" origin are probably genotoxic via their irradiating components (radon) or by interacting directly with cellular macromolecules. To assess possible hazards, we investigated the genotoxic effects of uranyl nitrilotriacetate (U-NTA) in human colon tumor cells (HT29 clone 19A), adenoma cells (LT97), and nontransformed primary colon cells. These are target cells of oral exposure to environmentally contaminated foods and represent different cellular stages during colorectal carcinogenesis. Colon cells were incubated with U-NTA. Cell survival, cytotoxicity, cellular glutathione (GSH) levels, genotoxicity, and DNA repair capacity (comet assay), as well as gene- and chromosome-specific damage combination of comet assay and fluorescence in situ hybridization [FISH], 24-color FISH) were determined. U-NTA inhibited growth of HT29 clone 19A cells (75-2000 microM, 72 h) and increased GSH (125-2000 microM, 24 h). U-NTA was genotoxic (1000 microM, 30 min) but did not inhibit the repair of DNA damage caused by hydrogen peroxide (H(2)O(2)), 4-hydroxynonenal, and 2-hydroxyamino-1-methyl-6-phenylimidazo[4,5-b]-pyridine. U-NTA was also genotoxic in LT97 cells and primary colon cells, where it additionally increased migration of TP53 into the comet tail. In LT97 cells, 0.5-2mM U-NTA increased chromosomal aberrations in chromosomes 5, 12, and 17, which harbor the tumor-related genes APC, KRAS, and TP53. It may be concluded that uranium compounds could increase alimentary genotoxic exposure in humans if they reach the food chain in sufficient amounts.

Radionuclides and trace metals in Canadian moose near uranium mines: comparison of radiation doses and food chain transfer with cattle and caribou

Tissues from 45 moose and 4 cattle were collected to assess the health of country foods near uranium mines in northern Saskatchewan. Bone, liver, kidney, muscle and rumen contents were analyzed for uranium, radium-226 (226Ra), lead-210 (210Pb), and polonium-210 (210Po). Cesium-137 (137Cs), potassium-40 (40K), and 27 trace metals were also measured in some tissues. Within the most active mining area, Po in liver and muscle declined significantly with distance from tailings, possibly influenced by nearby natural uranium outcrops. Moose from this area had significantly higher 226Ra, 210Pb, 210Po, and 137Cs in some edible soft tissues vs. one control area. However, soil type and diet may influence concentrations as much as uranium mining activities, given that a) liver levels of uranium, 226Ra, and 210Po were similar to a second positive control area with mineral-rich shale hills and b) 210Po was higher in cattle kidneys than in all moose. Enhanced food chain transfer from rumen contents to liver was found for selenium in the main mining area and for copper, molybdenum and cadmium in moose vs. cattle. Although radiological doses to moose in the main mining area were 2.6 times higher than doses to control moose or cattle, low moose intakes yielded low human doses (0.0068 mSv y(-1)), a mere 0.3% of the dose from intake of caribou (2.4 mSv y(-1)), the dietary staple in the area.

Uranium mill tailings: nuclear waste and natural laboratory for geochemical and radioecological investigations

Uranium mill tailings (UMT) are a high volume, low specific activity radioactive waste typically disposed in surface impoundments. This review focuses on research on UMT and related earth materials during the past decade relevant to the assessment of: (1) mineral hosts of radionuclides; (2) the use of soil analogs in predicting long-term fate of radionuclides; (3) microbial and diagenetic processes that may alter radionuclide mobility in the surficial environment; (4) waste-management technologies to limit radionuclide migration; and (5) the impact of UMT on biota.

Radionuclides in the terrestrial ecosystem near a Canadian uranium mill--Part I: Distribution and doses

Soils, vegetation, small mammals, and birds were measured for uranium series radionuclides at three sites near the operating Key Lake uranium mill in northern Saskatchewan. Sites, impacted by windblown tailings and mill dust, had significantly higher concentrations of uranium, 226Ra, 210Pb, and 210Po in soils, litter, vegetation, tree needles and twigs, small mammals, and birds, compared to a control site. Samples were collected from both upland jackpine and black spruce bog habitats in triplicate at each site. Both habitats were similar in radionuclide accumulation. Absorbed doses averaged 0.92, 8.4, and 4.9 mGy y(-1) to small mammals and 2.0, 5.8, and 2.8 mGy y(-1) to Lincoln's sparrows at the control, tailings, and mill sites, respectively. These doses do not include doses from short-lived radon progeny. The majority of the dose increment at the tailings and mill sites was due to 226Ra, whereas it was 210Po at the control site. Thus, use of a radiation weighting factor of 20 for alpha radiation raised equivalent doses (in mSv y(-1)) by nearly a factor of 20.

Radionuclides in the terrestrial ecosystem near a Canadian uranium mill--Part III: Atmospheric deposition rates (pilot test)

Atmospheric deposition rates of uranium series radionuclides were directly measured at three sites near the operating Key Lake uranium mill in northern Saskatchewan. Sites impacted by windblown tailings and mill dusts had elevated rates of uranium deposition near the mill and elevated 226Ra deposition near the tailings compared to a control site. Rainwater collectors, dust jars, and passive vinyl collectors previously used at the Ranger Mine in Australia were pilot-tested. Adhesive vinyl surfaces (1 m2) were oriented horizontally, vertically, and facing the ground as a means of measuring gravitational settling, wind impaction, and soil resuspension, respectively. Although the adhesive glue on the vinyls proved difficult to digest, relative differences in deposition mode were found among radionuclides and among sites. Dry deposition was a more important transport mechanism for uranium, 226Ra, and 210Pb than rainfall, while more 210Po was deposited with rainfall.