(i) How does spatial and temporal distribution of radio-nuclide concentration get distributed as soon as it leaches out of the disposal facility, particularly in the near field, and that too, in the absence of thermodynamic equilibrium?

(ii) What is the rate at which the mobility of radio-nuclides takes place soon after its release from the disposal facilities?

(iii) What happens to mixing or spreading details of radioactive wastes within the subsurface system associated with different disposal practices connected with different depths/geology?

(iv) How fast the nuclear wastes gets diluted, especially within deep-seated unweathered hard rock?

(v) In case, if the nuclear waste (or radionuclides) leaches out of the repository, will the concentration of the soluble species such as Cesium and Technetium be diluted to natural background level, and if so, what is the associated rate at which the concentration of radionuclides gets diluted?

(vi) What happens to the concentration of insoluble species such as Plutonium?

(vii) What is the likelihood of leached radioactive wastes reaching all the way to the biosphere from geosphere?

(viii) Whether the concept of nuclear heat associated with the subsurface and deep geological disposal require the transport of thermal fronts with

reference to the transport of solutes?

(ix) How far colloids influence the radionuclide migration? and

(x) Whether NAPL behavior has a significant role to play with, in the vicinity of a Nuclear Waste Repository?

Reference:

ISH Journal of Hydraulic Engineering, 2015, Vol. 21, No. 2, 162–176

http://dx.doi.org/10.1080/09715010.2014.984249

Suresh Kumar

http://www.doe.iitm.ac.in/gskumar/

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