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Radioactive waste is the general term for a variety of hazardous by-products generated in both the military and civil nuclear industries. Both the volatility and longevity of most radioactive waste present a unique set of safety concerns for its handling and disposal.

As nuclear waste decays, it releases, or “radiates,” dangerous emissions (principally, alpha and beta particles, as well as gamma rays) that can cause cellular and genetic damage when absorbed by humans, animals, and plants. Due to the threat that radioactive by-products of nuclear energy production pose to public health and safety, this so-called radwaste cannot be disposed of through the public waste stream's normal channels.

The radioactive elements, some having half-lives of thousands of years, cannot simply be buried in conventional sanitary landfills or incinerated, since doing so would inevitably expose living beings to particles of radwaste that are mutagenic and lethal. To dispose of this waste in unregulated ways poses a threat not only to those living near the disposal sites but also to those distant in time and space. The specter of radioactive elements slowly decaying over hundreds of thousands of years presents a virtually interminable problem of containment, and these elements, when released into the atmosphere or water table, can travel surprising distances.

Radioactive fallout from the Chernobyl disaster, for example, was later detected in British livestock thousands of miles away. The dangers this type of waste present and the amount of oversight radwaste requires after its disposal, however, vary, depending on its source, concentration, and atomic structure. Scientists charged with its management have therefore divided radioactive waste into three basic categories: high-level, transuranic, and low-level.

High-Level Waste

High-level waste is comprised of the spent uranium assemblies that fuel a nuclear reactor. These assemblies consist of pellets of fissionable uranium, approximately the size of a pencil eraser, that are stacked on top of each other in long, thin tubes, which are then bundled together. These fuel assemblies can be raised or lowered into the reactor tank as a means for slowing or accelerating the nuclear chain reactions through which electricity is generated. The uranium used to drive this reaction is regularly replaced after one to three years of use. The spent fuel is not inert, however. It continues to emit potentially harmful radiation for many years after it has been removed from the reactor. The 110 operating nuclear reactors in the United States produce approximately 40,000 cubic feet of high-level waste every year (enough to cover a regulation football field to a depth of almost one foot). With reprocessing, this amount can be decreased dramatically: 400 cubic feet per reactor can be reduced to as little as 3.4 cubic feet of radioactive material. However, the intense radioactivity of this distillate requires dilution for transportation or storage, so industry claims to the effect that a nuclear reactor's waste for a year could be stored comfortably under a desk, while technically accurate, do not tell the whole story. Because, as of 2010, there was no permanent disposal site for this high-level waste material, nuclear utilities keep the spent fuel on site in pools or in sealed casks that are designed to contain the emission of harmful radiation while the fuel slowly decays.

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