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Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

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Page 1: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste

matrices

Page 2: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 2

Lisa Almkvist and Börje Torstenfelt

Swedish Nuclear Fuel and Waste Management Co (SKB)

Peter Cronstrand

Vattenfall Power Consultant (VPC)

Thermodynamic modelling

Page 3: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 3

Cement waste matrix development(presented at the RCM in Moskow)

Solidification of operational intermediate-level waste– Ion exchange resins– Evaporator concentrates

Laboratory test programs studying:– Waste load– Water-to-cement ratio– Type of cement– Additives (liquid, solid)– Type of storage (dry, wet (deionised, salt or chalk

water))

Page 4: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 4

A 1D cell-divided representation of a nuclear repository

The state of the engineered barriers is simulated through multi-component diffusive transport followed by thermo-dynamical calculations of relevant mineral species for each transport step.

Integrity of the repository concrete structure; short-term and long-term (presented at the RCM in Moskow)

Computational model

Cement encapsu-lated waste

Cl-

SO42-

CO32-

Na+

bentonite

Shotcrete Concrete wall

Ambient water with time-dependent ionic composition

Page 5: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 5

Reactive-transport modelling - uncertainties

Transport:•Diffusion, (Ficks law or MCD)

•Advection

Thermodynamic database

Rates

Representation of CSH, (variable log k vs. solid solution)

Composition of the cement paste

Composition of infiltrating water

Reaction:• Thermodynamic equilibrium

• Kinetics

Transport

Reaction

Uncertainties

Flows

Diffusivities

Porosity evolution

Porosity-diffusivity-relation

Page 6: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 6

Uncertainty assessment

• Uncertainties can initially be characterized in simplified leaching models before entering the full scale degradation scenario.

+ Easy to visualize the result

+ Easy to identify and isolate the influence of a specific input parameter

+ Easy to compare with experiments

• Degradation indicators:

• Dissolution of Ca(OH)2

• Decalcification of CSH

Page 7: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 7

Leaching models

Reactive properties

• Thermodynamic database

• Log k vs. solid solution

• Water composition

Performed on crushed cement

Transport properties

• Porosity-diffusivity relations

• Flows

• Diffusivities

• Porosity evolution

Performed on solid samples

Page 8: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 8

Database

Portlandite dissolution

0.00E+00

1.00E-01

2.00E-01

3.00E-01

4.00E-01

5.00E-01

6.00E-01

7.00E-01

8.00E-01

9.00E-01

0 20 40 60 80 100

Leaching step

M C

a(O

H)2

PCHatches-17

Minteq

Llnl

Wateq

Nagra/PSI

Thermoddem

Page 9: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 9

Log k vs. Solid solution

Portlandite dissolution

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

0 20 40 60 80

Leaching step

M (

Ca(

OH

)2)

11.2

11.4

11.6

11.8

12

12.2

12.4

12.6

pH

Portlandite (ss, Walker2003)

Portlandite (stepwise log k)

pH (ss, Walker 2003)

pH (stepwise log k)

Page 10: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 10

Water intrusionPortlandite dissolution

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

0 10 20 30 40 50 60 70

Leaching step

M (

Ca(

OH

)2)

Brine

Glacial

Litorina

Biogenic

Rain

Ramlösa

Evian

SFR-mean

Distilled water

Page 11: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 11

Porosity-diffusion relation

Portlandite dissolution, porosity evolution

0

1

2

3

4

5

6

0 5 10 15

Year

M C

a(O

H)2

0

0.05

0.1

0.15

0.2

0.25

0.3

0.35

Po

rosi

ty

Portlandite, m=0

Portlandite, m=1

Portlandite, m=2

Portlandite, m=3

Porosity, m=0

Porosity, m=1

Porosity, m=2

Porosity, m=3

me dd 0Archies law:

Page 12: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 12

Recipe for a conservative - yet realistic- estimate

• Databases yielding high dissolution rates (PCHatches or Thermoddem)

• Log k approach can reproduce the result obtained by a solid solution approach.

• Water: Low calcium, high NaCl. Carbonates have a non-trivial and twofold effect; enhance dissolution rates, but the precipitation of calcite reduces the porosity.

• Porosity-diffusion relation: Case-dependent (although a conservative estimate can always be achieved by choosing a sufficiently high diffusivity)

Page 13: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 13

Full scale scenario - the Silo at SFR: initial state

Silo Year 0

0

100

200

300

400

500

600

700

800

900

1000

0 1 2 3 4

Distance (m)

Vo

lum

e (

cc

)

BiotiteK-feldsparAlbiteQuartzSaponite-hSaponite-mgSaponite-caSaponite-kSaponite-naMordenite-naMagnetiteKatoiteIlliteClinoptil-kPhillipsite-naPhillipsite-kMontmor-mgMontmor-caMontmor-kMontmor-naHydroxyapatiteHydrotalciteHydrogarnetBruciteMonocarboaluminateFriedelsaltEttringiteMonosulphateCalcitePortlanditeCSH_0.8CSH_1.1CSH_1.8

Bentonite Silowall ILW&LLW

Shotcrete Grout

Page 14: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 14

Full scale scenario - the Silo at SFR: 100 000 years

E. Silo year 100 000

0

200

400

600

800

1000

1200

1400

0 1 2 3 4

Distance (m)

Vo

lum

e (

cc

)

BiotiteK-feldsparAlbiteQuartzSaponite-hSaponite-mgSaponite-caSaponite-kSaponite-naMordenite-naMagnetiteKatoiteIlliteClinoptil-kPhillipsite-naPhillipsite-kMontmor-mgMontmor-caMontmor-kMontmor-naHydroxyapatiteHydrotalciteHydrogarnetBruciteMonocarboaluminateFriedelsaltEttringiteMonosulphateCalcitePortlanditeCSH_0.8CSH_1.1CSH_1.8

Bentonite Silowall ILW&LLWShotcrete Grout

Page 15: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 15

Full scale scenario - monitoring some parameters

Notation Diffusivity Water composition

Temperature

A Fixed Fixed Fixed

B Fixed Fixed Varying

C Fixed Varying Fixed

D Varying Fixed Fixed

E Varying Varying Varying

Page 16: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 16

Full scale scenario - porosity distribution

Silo Year 100 000

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0 1 2 3 4

Distance (m)

Po

ros

ity

A

B

C

D

E

Bentonite Silowall ILW&LLWShotcrete Grout

Page 17: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 17

Full scale scenario - pH distributionSilo Year 100 000

7

8

9

10

11

12

13

14

0 1 2 3 4

Distance (m)

pH

A

B

C

D

E

Bentonite Silowall ILW&LLWShotcrete Grout

Page 18: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 18

Some remaining uncertainties - clogging

• Introduces both a mesh-and time-step-dependency

• Is there a residual diffusivity (through the gel-pores) even in perfectly clogged material?

• Can remaining non-hydrated clinker materials lead to fractures?

• Are there types of waste that can accelerate the degradation process?

Page 19: Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices

Thermodynamic modelling 19

Some remaining uncertainties - fractures

The effect within the fracture

Pure advection Advection and diffusion to adjacent pores

Dual porosity approachOnly evaluates degradation in the fracture itself

The effect on the overall sample.