High-level radioactive waste management addresses the handling of radioactive materials generated from nuclear power production and nuclear weapons manufacture. Radioactive waste contains both short-lived and long-lived radionuclides, as well as non-radioactive nuclides.[1] In 2002, the United States stored approximately 47,000 tonnes of high-level radioactive waste.
Among the constituents of spent nuclear fuel, neptunium-237 and plutonium-239 are particularly problematic due to their long half-lives of two million years and 24,000 years, respectively.[2] Handling high-level radioactive waste requires sophisticated treatment processes and long-term strategies such as permanent storage, disposal, or conversion into non-toxic forms to isolate it from the biosphere.[3]Radioactive decay follows the half-life rule, which means that the intensity of radiation decreases over time as the rate of decay is inversely proportional to the duration of decay. In other words, the radiation from a long-lived isotope like iodine-129 will be much less intense than that of short-lived isotope like iodine-131.[4]
Governments worldwide are exploring various disposal strategies, usually focusing on a deep geological repository, though progress in implementing these long-term solutions has been slow.[5] This challenge is exacerbated by the timeframes required for safe decay, ranging from 10,000 to millions of years.[6][7][8] Thus, physicist Hannes Alfvén identified the need for stable geological formations and human institutions that can endure for extended periods, noting the absence of any civilization or geological formation that has proven stable for such durations.[9]
The management of radioactive waste not only involves technical and scientific considerations but also raises significant ethical concerns regarding the impacts on future generations.[10] The debate over appropriate management strategies includes arguments for and against the reliance on geochemical simulation models and natural geological barriers to contain radionuclides post-repository closure.[11]
Despite some scientists advocating for the feasibility of relinquishing control over radioactive materials to geohydrologic processes, skepticism remains due to the lack of empirical validation of these models over extensive time periods.[12] Others insist on the necessity of deep geologic repositories in stable formations.[13][14] Forecasts concerning the health impacts of long-term radioactive waste disposal are critically assessed,[15] with practical studies typically considering only up to 100 years for planning and cost evaluation.[16][17] Ongoing research continues to inform the long-term behavior of radioactive wastes, influencing management strategies and national policies globally.[18]
^Ojovan, M. I.; Lee, W.E. (2014). An Introduction to Nuclear Waste Immobilisation. Amsterdam: Elsevier Science Publishers. p. 362. ISBN978-0-08-099392-8.
^Bruno, Jordi, Lara Duro, and Mireia Grivé. 2001. The applicability and limitations of the geochemical models and tools used in simulating radionuclide behavior in natural waters: Lessons learned from the blind predictive modelling exercises performed in conjunction with natural analogue studies. QuantiSci S. L. Parc Tecnològic del Vallès, Spain, for Swedish Nuclear Fuel and Waste Management Co.
^Shrader-Frechette, Kristin S. Expert judgment in assessing radwaste risks: What Nevadans should know about Yucca Mountain. Carson City: Nevada Agency for Nuclear Projects, Nuclear Waste Project, 1992 ISBN0-7881-0683-X