100-N Area
Active liquid waste disposal operations at 100-N Area did not cease until mid-1992. These disposal
operations released millions of gallons per year of reactor cooling water from N Reactor containing
high concentrations of strontium-90 into the soil immediately adjacent to the Columbia River. In
some parts of the groundwater plume, strontium-90 was thousands of times its drinking water
standard, and although no aquatic water quality standard for strontium-90 was available, the shear
magnitude of these releases were considered sufficient cause to initiate action.
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Because strontium-90 in groundwater is tightly bound to the aquifer
sediments, it represents a threat to groundwater quality well into the future.
A number of technologies to slow the release of strontium-90 to the Columbia
River will be evaluated; plus, studies are underway to evaluate the impact of
strontium-90 on the aquatic ecosystem. These studies will help the Groundwater
Remediation Project re-evaluate how well the pump-and-treat system protects
the ecosystem and assess the need for alternative measures.
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The effectiveness of the pump-and-treat operations in limiting the discharge of strontium-90 to the
Columbia River at N Springs has been questioned throughout its period of operation. The major
reason concentrations of strontium-90 in groundwater were reduced occurred as a direct result of
ending the discharge of contaminated liquids to the soil column in the early 1990s. Much of the
strontium-90 remaining in the groundwater beneath 100-N Area is tightly bound to the aquifer
sediments and represents a threat to groundwater quality well into the future, making the return
to beneficial use for this portion of the aquifer unrealistic.
A number of technologies other than pump-and-treat have been tested or are planned to be tested
to assess their effectiveness for the long-term protection of the Columbia River ecosystem.
Previously, technologies including impermeable barriers constructed of steel and sorptive
permeable barriers of clay-like materials were evaluated as alternatives to pump-and-treat
systems. Investigation determined neither barrier was a suitable replacement for pump-and-treat.
Tests are now planned to evaluate two additional technologies that may be candidates to replace
the pump-and-treat systems. One alternative under consideration would use deep-rooted vegetation
to absorb strontium 90 from the groundwater along the shoreline; then, the contaminated vegetation
would be removed and disposed on the Central Plateau. A second method under consideration would
be to develop a chemical barrier that would further immobilize strontium-90 in the soil and limit
its release to the river through N Springs.
In addition to the evaluation of new and innovative technologies to slow
the release of strontium-90 to the Columbia River, studies are underway
to evaluate the actual impact of strontium-90 on the aquatic ecosystem.
A number of species are now being assessed to determine bioaccumulation
rates and the potential impact to organisms exposed to strontium-90. These
efforts, in conjunction with the evaluation of new and innovative technologies,
should enable the Groundwater Remediation Project to re-evaluate how well
the pump-and-treat actions protect the ecosystem and assess the need for
additional measures to mitigate the impacts. Evaluation of the technologies,
risks, and potential impacts of strontium-90 are expected to be complete
in 2006.
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