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The management and disposal of radioactive wastes are key
international issues requiring a sound, fundamental scientific
basis to insure public and environmental protection. Large
quantities of existing nuclear waste must be treated to encapsulate
the radioactivity in a form suitable for disposal. The treatment of
this waste, due to its extreme diversity, presents tremendous
engineering and scientific challenges. Geologic isolation of
transuranic waste is the approach currently proposed by all nuclear
countries for its final disposal. To be successful in this
endeavor, it is necessary to understand the behavior of plutonium
and the other actinides in relevant environmental media. Conceptual
models for stored high level waste and waste repository systems
present many sCientific difficulties due to their complexity and
non-ideality. For example, much of the high level nuclear waste in
the US is stored as alkaline concentrated electrolyte materials,
where the chemistry of the actinides under such conditions is not
well understood. This lack of understanding limits the successful
separation and treatment of these wastes. Also, countries such as
the US and Germany plan to dispose of actinide bearing wastes in
geologic salt deposits. In this case, understanding the speciation
and transport properties of actinides in brines is critical for
confidence in repository performance and risk assessment
activities. Many deep groundwaters underlying existing contaminated
sites are also high in ionic strength. Until recently, the
scientific basis for describing actinide chemistry in such systems
was extremely limited."
The management and disposal of radioactive wastes are key
international issues requiring a sound, fundamental scientific
basis to insure public and environmental protection. Large
quantities of existing nuclear waste must be treated to encapsulate
the radioactivity in a form suitable for disposal. The treatment of
this waste, due to its extreme diversity, presents tremendous
engineering and scientific challenges. Geologic isolation of
transuranic waste is the approach currently proposed by all nuclear
countries for its final disposal. To be successful in this
endeavor, it is necessary to understand the behavior of plutonium
and the other actinides in relevant environmental media. Conceptual
models for stored high level waste and waste repository systems
present many sCientific difficulties due to their complexity and
non-ideality. For example, much of the high level nuclear waste in
the US is stored as alkaline concentrated electrolyte materials,
where the chemistry of the actinides under such conditions is not
well understood. This lack of understanding limits the successful
separation and treatment of these wastes. Also, countries such as
the US and Germany plan to dispose of actinide bearing wastes in
geologic salt deposits. In this case, understanding the speciation
and transport properties of actinides in brines is critical for
confidence in repository performance and risk assessment
activities. Many deep groundwaters underlying existing contaminated
sites are also high in ionic strength. Until recently, the
scientific basis for describing actinide chemistry in such systems
was extremely limited."
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