10.07.2015 Views

Architecture and management of a geological repository - Andra

Architecture and management of a geological repository - Andra

Architecture and management of a geological repository - Andra

SHOW MORE
SHOW LESS
  • No tags were found...

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

4 – Waste disposal PackagesHowever, during the first few hundred years, the decay <strong>of</strong> fission products <strong>and</strong> actinids having averagehalf-lives engenders significant local heating. The mastery <strong>of</strong> phenomena during this so-called"thermal phase" begs the question <strong>of</strong> primary waste package disposal in their existing condition or <strong>of</strong>the advantage <strong>of</strong> placing them in an over-pack prior to disposal. Based on the current state <strong>of</strong>knowledge, <strong>Andra</strong> has chosen the second option.This chapter describes the scientific considerations which led to this choice, the different technicalresponses envisaged <strong>and</strong> the option preferred at this stage <strong>of</strong> study.With the aim <strong>of</strong> evaluating feasibility, it also includes the dimensions <strong>of</strong> the over-pack <strong>and</strong>manufacturing techniques based on tried <strong>and</strong> tested industrial practices.4.2.1 Description <strong>of</strong> the main questions4.2.1.1 Need for an over-packTo underst<strong>and</strong> the justification <strong>of</strong> studying an over-pack, we should first remember that the primarypackage consists <strong>of</strong> a glass matrix inside a stainless steel envelope. The need for an over-pack resultsfrom phenomenological aspects <strong>of</strong> the so-called "thermal" phase during which the temperature <strong>of</strong> thepackage falls gradually after rising to a maximum or "thermal peak" 32 . The phenomena characterisingthis phase increase the alterability <strong>of</strong> the glass matrix, influence the behaviour <strong>of</strong> the radionuclides itcontains <strong>and</strong> weaken the stainless steel envelope <strong>of</strong> the primary packages with respect to corrosion[37].Concerning the alterability <strong>of</strong> the matrix, glass dissolution models take into account (i) a control <strong>of</strong> thealteration process kinetics by silica dissolution, main constituent <strong>of</strong> glass <strong>and</strong> (ii) radionuclide releasegoverned by dissolution congruent 33 with that <strong>of</strong> the silica. For C1 to C4 type packages, the modelpreferred for its robustness given strength at the current state <strong>of</strong> knowledge, consists <strong>of</strong> two phases.During the first phase, the initial dissolution speed [V 0 ] results from geochemical imbalance betweenthe glass <strong>and</strong> its environment. During the second phase, silica saturation <strong>of</strong> the waste environment isreflected in a slowing <strong>of</strong> dissolution towards a residual speed [V R ]. For C0 type packages, thedissolution regime according to the initial speed is assumed to continue for a long time. These twospeeds, V 0 et V R , depend on temperature: between 50°C <strong>and</strong> 90°C, the initial speed <strong>of</strong> dissolutionincreases by a factor <strong>of</strong> 30, the residual speed by a factor <strong>of</strong> about 15 34 [40].Concerning the behaviour <strong>of</strong> radionuclides likely to have been released, the question <strong>of</strong> mastering thethermodynamic phenomena governing chemical equilibria must be considered. Indeed, thephysicochemical phenomena involved are temperature-sensitive. Element solubility may be increasedor decreased when the temperature increases. The physical data which determine the speciation 35 <strong>of</strong> anelement in solution are known in a temperature range which is currently theoretically limited to 50-60°C. In practice, it is considered that uncertainty in extrapolating speciation evaluated on the basis <strong>of</strong>equilibrium constants acquired at 25°C, is understood up to 80°C. The temperature also influencessorption mechanisms at solid phase interfaces, as well as the transport <strong>of</strong> chemical species in water bydiffusion (in particular via the "Soret" effect); the speed <strong>of</strong> diffusion increases with temperature.32333435For information, this peak is 100°C at most on the surface <strong>of</strong> the package.Congruence means that the same dissolution speed is used for all the species in the glass.Note also that the description <strong>of</strong> the passage from V0 to VR may show increasing uncertainty with temperature, because <strong>of</strong> theextrapolation <strong>of</strong> thermodynamic data available governing the behaviour <strong>of</strong> chemical species in solution <strong>and</strong> at the interface between theliquid <strong>and</strong> solid phases (sorption mechanisms).Radionuclide speciation in solution is evaluated on the basis <strong>of</strong> mass action, enthalpic <strong>and</strong> heat capacity constants. The last twoparameters are particularly difficult to measure directly in temperature; this leads to considering for the speciation models a reactionalenthalpy that is independent <strong>of</strong> temperature <strong>and</strong> a heat capacity <strong>of</strong> zero; as a corollary to this, this approximation limits the range <strong>of</strong>validity <strong>of</strong> these models..DOSSIER 2005 ARGILE -ARCHITECTURE AND MANAGEMENT OF A GEOLOGICAL DISPOSAL SYSTEM129/495

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!