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Cleaning Uranium Waste with Bacteria
Roland Piquepaille writes "Nuclear bombs can kill people even if they're not used. In the U.S. alone, the Department of Energy estimates that more than 2,500 billion liters of groundwater are contaminated with uranium as a consequence of nuclear weapons production. In "Uranium 'pearls' before slime," scientists from the Pacific Northwest National Laboratory (PNNL) say they discovered that some common bacteria could "convert deadly heavy metal into less threatening nano-spheres." In fact, these bacteria can convert soluble radioactive uranium into a non-toxic solid form called uraninite. Still, more research needs to be done before using these bacteria on a large scale, but it's a step in the good direction. Read more for additional references and photos showing how Shewanella oneidensis can help us to decontaminate groundwater at nuclear waste sites."
We cannot simply exploit these living animals for our own selfish needs. These bacteria need to be allowed free range so they can live healthy, happy, natural lives without human oppression. We have a consistent track record of exploiting animals for our own use - even torturing them for our own entertainment. These bacteria need to be protected immediately! Oh won't someone please think of the bacteria!
Maybe not quite a "Holy Grail," but a possible solution nonetheless. It seems like the spent fuel would have to be removed from the reactor as it is currently and transported to a safe storage location on or off site in order for the bacteria to have a controlled environment to work their alleged magic. But you'd also have to consider the type of fuel. It would likely take less time for bacteria to attack and transform nuclear pellets than fuel rods, because the pellets have a greater surface area to "attack."
It'd be interesting to get more information on how long it takes the bacteria to transform the material, the lifespan, and reproductive cycle of the bacteria. If you need a massive quantity, it may not be quite so feasible.
Second, U-238 is 99.28% of natural uranium. U-235 is 0.72% Weapons grade, or enriched uranium is natural uranium that has a much higher percentage of U-235.
Suddenly, the hairy finger of a familiar monkey tapped me on the shoulder. It was time.--G. T.
Reading through the comments so far, there seems to be some misunderstanding of the work by the PNNL crowd and of bioremediation in general. My research group here at Argonne National Laboratory (which outside of Chicago) collaborates with the folks from PNNL. In fact, I am writing this very early on a Sunday morning while measuring the oxidation state of uranium using X-ray Absorption Spectroscopy at the Advanced Photon Source in samples from a collaborator at Oak Ridge National Laboratory, which, like PNNL, is a center of research into uranium bioremediation.
First, a few words about the concept of bioremediation. The Department of Energy became interested in bioremediation of metallic contamination after the extensive success of bioremediative techniques for cleaning up organic contamination -- things like benzene or trichloroethylene. The basic idea is that you dose the ground with bacteria that can metabolize the organic contaminant, let the bugs happily live their lives, then in the end the ground is much cleaner than before. Variations on this technique are in wide use for many organic contaminants and in many places around the world.
The Department of Energy's started several years ago to fund research into using similiar concepts to clean up ground water contamination associated with various sites where materials for nuclear weapons or nuclear fuel were produced. There are several sites in the US where the groundwater has elevated levels of uranium and other metals. Bioremediation is attractive because it involves remediation in situ. The ground doesn't need to be dug up, which introduces a whole slew of other problems into the mix.
Unfortunately, metals are different from organics. When a bacterium metabolizes benzene, the benzene goes away. When a dissimilatory metal reducer, like Shewanella, respires on a uranium compound, the most it can do is change the chemical state of uranium. It is impossible to turn the uranium into some other element. As several other posters have pointed out, uraninite (the end product of Shewnella's respiration of uranium compounds) is still radioactive and it is still toxic.
However, uraninite is not soluble. The uranium in the ground water is in a soluble form and therefore will flow through the ground and find its way into rivers and into drinking water supplies. Uraninite is highly insoluble. When Shewnella converts soluble uranium into uraninite, the uraninite particles adhere to the rocks in the ground.
Thus uranium bioremediation is a containment-in-place strategy. The danger of the contaminated sites is that the contamination will spread. The uranium-polluted site will still be polluted after the Shewnella has done its thing, but at least the uranium will not move out of the contaminated site. And that's the point of the DOE's bioremediation strategy -- to keep a problem that exists from spreading and becoming a bigger problem.