13 DECEMBRE 2012 | PAGE 1 Clays In Natural And Engineered Barriers For Radioactive Waste Confinement - march 23-25, 2015 11 octobre 2015 | PAGE 1 CEA |

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Presentation transcript:

13 DECEMBRE 2012 | PAGE 1 Clays In Natural And Engineered Barriers For Radioactive Waste Confinement - march 23-25, octobre 2015 | PAGE 1 CEA | 10 AVRIL 2012 O. Bildstein, J.E. Lartigue, M.L. Schlegel, C. Bataillon CEA (French Alternative Energies and Atomic Energy Commission) B. Cochepin, I. Munier, N. Michau Andra (French Radioactive Waste Management Agency) GAINING INSIGHT INTO CORROSION PROCESSES AND SECONDARY MINERAL PARAGENESIS FROM NUMERICAL SIMULATIONS OF INTEGRATED IRON- CLAYSTONE EXPERIMENTS

| PAGE 2 OUTLINE PLAN - description of the « ArCorr » integrated experiment - observations to be matched by the modeling - numerical model implementation and parameters - first results :  base case  sensitivity to kinetics parameters  sensitivity to transport parameters - conclusions and perspectives | PAGE 2

13 DECEMBRE 2012 | PAGE 3 THE « ARCORR » EXPERIENCE | PAGE 3 CEA | 10 AVRIL 2012

EXPERIMENTAL CONDITIONS AND MODELING OPTIONS 11 octobre 2015 | PAGE 4 Experimental conditions Isothermal 90°C Pressure 40 bars 2 interfaces : - iron/argilites - glass/argilites Modeling options - only the iron/argilites interface is treated in this presentation - « ThermoChimie V8 » thermodynamic database - kinetic parameters and diffusion coefficients at 90°C - dissolution kinetics parameters from Palandri & Kharaka (1984) - precipitation kinetics = k diss /100 - use BET specific surface areas

13 DECEMBRE 2012 | PAGE 5 SIMULATION GEOMETRY AND PARAMETERS | PAGE 5 Geometry base case parameters Iron zone –porosity = 0.15 –D eff = 2, m 2 /s Argilites (38 mm) –porosity = 0.18 ; –D eff = m 2 /s 6 mm – 6 nodes µ-container + gaps thickness 0,3 + 0,04 mm (34 nodes) argilites 29 mm – 100 nodes glass zone

REACTIVITY OF THE DIFFERENT MATERIALS 11 octobre 2015 | PAGE 6 Argilites - no ion-exchange or surface complexation reactions Iron - time-dependent corrosion rate (matching experimentaly measured rate) (data from Schlegel et al. 2014) (data from Brucker and Schlegel, 2012) fer312 argilites

13 DECEMBRE 2012 | PAGE 7 RESULTS FOR THE BASE CASE (1) 11 octobre 2015 | PAGE 7 maximal pH value of 8.7 secondary mineral paragenesis dominated by magnétite argilites zone iron zone argilites zone

13 DECEMBRE 2012 | PAGE 8 RESULTS FOR THE BASE CASE (2) | PAGE 8 reactivity of primary minerals

13 DECEMBRE 2012 | PAGE 9 RESULTS FROM SENSITIVITY TO KINETICS (1) 11 octobre 2015Réunion UPS6/SIMUL2 | 18 décembre 2013 quartz dissolution x100 argilites zone iron zone base case magnetite reactivity/100 magnetite reactivity/1000 argilites zone iron zone argilites zone iron zone argilites zone iron zone

| PAGE 10 RESULTS FROM SENSITIVITY TO KINETICS (2) | PAGE 10 siderite-Ca reactivity /10 base case greenalite reactivity x100 siderite-Ca reactivity x100 argilites zone iron zone argilites zone iron zone argilites zone iron zone argilites zone iron zone

13 DECEMBRE 2012 | PAGE 11 RESULTS FROM SENSITIVITY TO KINETICS (3) QUARTZ 11 octobre 2015 | PAGE 11 quartz dissolution x10 quartz dissolution x30 quartz dissolution x100 base case argilites zone iron zone argilites zone iron zone argilites zone iron zone argilites zone iron zone

13 DECEMBRE 2012 | PAGE 12 RESULTS FROM GLOBAL SENSITIVITY TO KINETICS 11 octobre 2015 | PAGE 12 quartz siderite magnétique greenalite x 10 all reactivity x 100 all reactivity x 1000 base case argilites zone iron zone argilites zone iron zone argilites zone iron zone argilites zone iron zone

13 DECEMBRE 2012 | PAGE 13 RESULTS FROM SENSITIVITY TO CORROSION RATE 11 octobre 2015 | PAGE 13 corrosion rate /10 attention : interface fer-argilite greenalite becomes dominant more iron migration towards the argilites base case argilites zone iron zone argilites zone iron zone

13 DECEMBRE 2012 | PAGE 14 SUMMARY OF SENSITIVITY TO KINETIC PARAMETERS 11 octobre 2015 | PAGE 14 -no modification in the sequence of secondary minerals -magnetite is destabilized only when global reactivity is increased -magnetite DOES NOT FORM at « low » corrosion rate

13 DECEMBRE 2012 | PAGE 15 RESULTATS WITH 1 PRE-EXISTING MAGNETITE NODE | PAGE 15 1 « magnetite » node (porosity = 0.1%  diffusion/10000), kinetics x10 iron312 argilites zone iron zone

13 DECEMBRE 2012 | PAGE 16 RESULTATS WITH 2 PRE-EXISTING MAGNETITE NODES | PAGE 16 magnetite node 1 (porosity = 1%  diffusion/100) magnetite node 2 (porosity = 0.1%  diffusion/10000) iron312 argilites zone iron zone

| PAGE 17 NEW SENSITIVITY TO MAGNETITE REACTIVITY | PAGE 17 magnetite reactivity x100 magnetite reactivity x1000 base case argilites zone iron zone argilites zone iron zone argilites zone iron zone

13 DECEMBRE 2012 | PAGE 18 EFFECT OF VARIABLE POROSITY 11 octobre 2015 | PAGE 18 corrosion rate rapidely drops… constant porosity iron312 argilites zone iron zone

13 DECEMBRE 2012 | PAGE 19 CONCLUSION 11 octobre 2015 | PAGE 19 Modeling and sensitivity analysis: modifying precipitation/dissolution kinetics affects only the amount of mineral precipitated, the mineral sequence remaining unchanged (unless a very high magnetite reactivity is used)  a low corrosion rate changes the nature of corrosion products: greenalite and sidérite instead of magnetite  a low diffusive barrier is necessary to avoid greenalite précipitation in the iron zone  high magnetite dissolution rate is required to allow for its redissolution at the interface with argilites

13 DECEMBRE 2012 | PAGE 20 PERSPECTIVES 11 octobre 2015 | PAGE 20 modify the tortuosity in the iron zone calculate the corrosion rate as controlled by the diffusion of reactants/products (H 2 ) in the internal corrosion layer (magnetite)

13 DECEMBRE 2012 | PAGE 21 DEN DTN SMTA LMTE Commissariat à l’énergie atomique et aux énergies alternatives Centre de Cadarache | Saint Paul lez Durance T. +33 (0) | F. +33 (0) Etablissement public à caractère industriel et commercial | RCS Paris B octobre 2015 | PAGE 21 CEA | 10 AVRIL 2012 THANK YOU FOR YOUR ATTENTION