Uranium is an element with chemical and radiological properties that make it useful in industry, military, and commerce, but toxic at sufficient levels. Various analytical methods are available to determine the presence, concentration, or quantity of uranium or its isotopes in a range of media. Results confirm that uranium is present in ambient air, water, and soil, so human exposure is assured. At least seven of its more than 100 mineral forms are found at mineable levels in various parts of the world, and the primary producers in 2019 by weight were Australia, Canada, China, Kazakhstan, Namibia, Niger, Russia, and Uzbekistan. Uranium is mined primarily for the ²³⁵U isotope. The process of enrichment adjusts the ratio of the three natural isotopes (²³⁴U, ²³⁵U, and²³⁸U) to produce two fractions. The fraction with increased ²³⁵U compared with natural is called enriched uranium and is the source of energy production for nuclear reactors and weapons. The other fraction is depleted in ²³⁵U and ²³⁴U, termed depleted uranium and is less radioactive than crustal uranium. Uranium is also used in a range of products that include glass tinting agents, ceramic glazes, gyroscope wheels, chemical catalysts, shields for radioactive sources, X-ray tube targets, and military armor and kinetic penetrators. It is no longer used in dental porcelains.
Intakes from water and food are approximately equivalent, at 0.9–1.5 micrograms per day (μg/day) based on the water source (higher in ground water) or diet (higher in beef, beef kidney and liver, onions, parsley, and salt; lower in poultry, fruit juices, fruits and vegetables, and dairy). Air concentrations are normally low. The highest human exposures result from drinking well water high in uranium and working in the uranium milling and production industries, with the greatest environmental challenge coming from mine and mill tailings. Human exposure involves inhalation, ingestion, and, since 1991, military metal fragment wounds. Uranium intestinal absorption is low (0.1%–6%, typically 1%–2.5%), increases with solubility, and is higher for neonates than nonfasting or iron deficient adults. Dermal absorption may not occur across intact skin for insoluble forms, but increases with solubility and extent of skin damage and excoriation, or if a puncture occurs. Severely damaged (e.g., burned) skin has lower absorption. Once in the blood, uranium's distribution and elimination kinetics are functions of its oxidation state. Tetravalent uranium entering the body converts to hexavalent as uranyl ions, which complex with citrate or bicarbonate in blood or plasma proteins. Distribution is broad, with a primary long-term concentration in lung (for heavy occupational exposure to insoluble forms), bone, liver, and kidney. Uranium can cross the placenta and excrete in breast milk based on rat fetus levels following oral exposure of the dam from before mating through lactation. Initial elimination is rapid, with two-or-more phase excretion. Computer programs can estimate timeframe concentrations and radiation doses to organs and tissues. Inhaling 1 μg U/day can result in kidney concentrations of 0.003, 0.00075, and 0.000078 μg U/g for type F (highly soluble), M (moderately soluble), and S (slightly soluble) uranium, respectively. Sv/Bq conversion factors have been developed to estimate radiation doses to the body and selected organs from inhaled or ingested uranium isotopes. The International Commission on Radiological Protection (ICRP) has developed new biokinetics modeling and methodology resulting in revised Sv/Bq (rem/pCi) dose conversion factors. Dose coefficients are being developed with a plan to address exposure via breast milk and cross-placental transfer. Federal Guidance Report No. 13 provides such conversion factors.
Overexposure impacting human and animal health depends on pathway, enrichment, and compound. It has been determined that adverse health effects of natural or low-enriched uranium are primarily from its chemical rather than radiological toxicity and this chemical toxicity is independent of its radiation exposure. Lung damage from inhaled uranium involves alveolar injury with potential long-term fibrosis and emphysema. The health effects from inhalation, oral, and dermal exposure are primarily to the kidney, and nonsevere damage can be reversible. Less severe effects are observed for the liver, lung, nervous system, and reproductive system. The mechanism for renal toxicity involves the accumulation of uranium in tubular epithelium progressing to tubulointerstitial nephritis or tubular necrosis based on exposure and duration. This may be from cellular oxidative stress, altered cell signaling-related gene expression, and inhibited sodium-dependent phosphate and glucose transport systems. Impacts on liver enzymes and receptors might affect drug therapy regimens. Uranium can interfere with bone remodeling and liver integrity. Uranium is not classified as a carcinogen, and cancer has not been observed in high-dose human and animal studies, except for a foreign body response at metal implantation sites. If cancer should develop, bone sarcomas are the most likely since uranium, like radium, deposits long term in bone and radium dial painters developed sarcomas. Immunological and genetic assessments could tease out unconfirmed effects or mechanisms.