"The treatment was connected with the dissolution of the contaminants in the upper soil horizons and their transfer into the deeply located soil horizons (mainly to the horizon B2) where they were immobilized as different insoluble compounds.The dissolution of contaminants was connected with the activity of both heterotrophic and chemolithotrophic aerobic microorganisms and the immobilization was due mainly to the anaerobic sulphate-reducing bacteria."
I don't do biology well, but I'll try to translate.
The contaminants in the upper layers of the soil were dissolved. Bacteria converted the contaminants into a form that could dissolve in water; water soaks into the ground, so the contaminants, radioactive or not, penetrated farther into the soil. When they reached a deep enough level they ran into other backterial, bacterial that are "anaerobic sulfate-reducing' bacteria--i.e., they take sulfur compounds and reduce them to something closer to elemental sulfur. At that point the compounds with the heavy metal/radioactive contaminants are no longer water soluble; they precipate out and sit there, fairly inert. The B2 horizon is the subsoil, typically with a lot more clay in it (but maybe organics ... nod to
http://en.wikipedia.org/wiki/Soil_horizon#B_Horizon for the B2-horizon stuff).
Down that deep the contaminants aren't a problem: You're unlikely to pick them up, they won't go airborne, and most food plants won't find them; trees and the like could. In any event, they won't be a large problem, and the radioactive component can decay. The article says that by helping the bacteria dissolve the compounds in the soil, they can be moved to the subsoil more quickly--soil remediation.