the cementitious barriers partnership: predicting the long-term chemical and physical performance of...
TRANSCRIPT
The Cementitious Barriers Partnership:Predicting the Long-term Chemical and Physical Performance
of Cementitious Materials used in Nuclear Applications
K. G. Brown (Presenter); CRESP, Vanderbilt U.D. Esh, M. Fuhrmann , J. Phillip; US NRC
D. Kosson, S. Mahadevan, A. Garrabrants, S. Sarkar, J. Arnold; CRESP, Vanderbilt U.H. Van der Sloot†, J.C.L. Meeussen‡, P. Seignette, R. Comans; ECN (NL)
E. Garboczi, K. Snyder, J. Bullard, P. Stutzman; NISTE. Samson, J. Marchand; SIMCO Technologies, Inc. (CA)C. Langton, G. Flach, R. Seitz, S. Marra, H. Burns; SRNL
DOE-EM Project Manager: Pramod Mallick 29 November 2011
†Hans van der Sloot Consultancy after 01JAN2010‡NRG after 01SEP2010
2
Project Goal Develop a reasonable and credible set of tools to predict the
structural, hydraulic and chemical performance of cement barriers used in nuclear applications over extended time frames (e.g., up to or >100 years for operating facilities and > 1000 years for waste management).
• Mechanistic / Phenomenological Basis
• Parameter Estimation and Measurement
• Boundary Conditions (physical, chemical interfaces)
• Uncertainty Characterization
3
Partnership Members• Department of Energy – Office of
Environmental Management Scenarios & Key Uncertainties Primary end-user
• Nuclear Regulatory Commission Scenarios & Key Uncertainties Primary end-user
• Savannah River National Laboratory
Performance Assessment (PA) Interface
Model Integration Cracking Scenarios Test Beds
• NIST THAMES – Microstructure Evolution &
Properties
• SIMCO Technologies, Inc. STADIUM® – Physical & Hydraulic
Performance
• Energy Research Centre of the Netherlands (w/ Nuclear Research Group, Hans van der Sloot Consultancy)
LeachXS™/ORCHESTRA – Chemical Performance & Constituent Release
• Vanderbilt University/CRESP Chemical Performance & Constituent
Release (experimental) Uncertainty Analysis Framework Model Integration
4
Technical Strategy / Approach• Reference Cases – provide basis for comparison and demonstration of tools under
development Cementitious waste form in concrete disposal vault with cap Grouted high-level waste (HLW) tank closure Spent fuel pool Nuclear processing facilities closure / D&D (e.g., canyons) Grouted vadose zone to immobilize contamination Materials – surrogate low-activity waste (LAW) cementitious waste form, reducing grout,
reinforced concrete (historical), and reinforced concrete (future)
• Extension/enhancement of existing tools – CEMHYD3D/THAMES, STADIUM®, LeachXS™/ORCHESTRA, GoldSim Performance Assessment (PA) framework
• Coordinated experimental and computational program Conceptual model development and improvement Define test methods and estimate important parameters Model calibration and validation
6
Integration of CBP Tools with PAs
Atmosphere
Soil layers
Cap layers
Source
Vadose Zone(s)
Saturated Zone(s)
Surface Water
EngineeredSystem
Exposure Scenarios
Failures
Risk
Airborne (diffusion)
Waterborne (advection)
Airborne (barometric pumping)
Airborne (resuspension/deposition)
Plant-induced
Animal-induced
CBP Focus:• Cementitious materials
performance as part of engineered system and their interfaces with natural system
• To provide near field source term
• Uncertainty approach being developed to be broadly applicable to PA and design process
CBP Interest Area
Landfills Partnership (CRESP)Craig Benson (U of Wisconsin)
7
Key Degradation Phenomena
Phenomena• Chloride ingress & corrosion• Leaching • Sulfate attack & cracking /
damage (2011)• Carbonation (2012)• Oxidation (2012)• Cracking (2013)• Pore structure relationships
with mass transfer and hydraulic properties (TBD NIST)
Integration with Conceptual Models
• Coupled degradation phenomena
• Saturated, unsaturated and variable saturation
• Liquid, vapor mass transfer
• System geometry and boundary conditions
8
Specifications, Properties, and Phenomena for the Evaluation of Performance of Cementitious Barriers
10
CBP Progress and Impacts• Demonstrated coupling of LeachXS™/ORCHESTRA and
STADIUM® with GoldSim (using a Dynamic-link Library / DLL) • Understanding potential for sulfate attack during salt waste
disposal in a concrete vault• Supporting DOE-ORP Secondary Waste treatment evaluation• Participation in inter-laboratory validation of draft EPA
leaching test procedures• Data for evaluation of environmental impact of fly ash usage
in cementitious materials (grout, concrete, etc.) – input into EPA regulatory process
Software integration objectives: Provide a common, unified interface to CBP partner codes through a
GoldSim Graphical User Interface (GUI) Provide a “wrapper” for probabilistic uncertainty / sensitivity analysis
(e.g., Monte Carlo) Couple LeachXS™/ORCHESTRA,
STADIUM® and THAMES in a synergistic manner
Connect to broader systems-level performance, safety and environmental assessment models
13
Impact: Comparison of Cement Data and Thermodynamic Model Predictions
1,0E-08
1,0E-07
1,0E-06
1,0E-05
1,0E-04
1,0E-03
1,0E-02
1 2 3 4 5 6 7 8 9 10 11 12 13 14
Conce
ntr
ati
on (m
ol/
l)
[Al+3] as function of pH
0,0001
0,001
0,01
0,1
1
1 2 3 4 5 6 7 8 9 10 11 12 13 14
[Ca+2] as function of pH
1,0E-06
1,0E-05
1,0E-04
1,0E-03
1,0E-02
1 2 3 4 5 6 7 8 9 10 11 12 13 14
pH
[H4SiO4] as function of pH
1,0E-09
1,0E-08
1,0E-07
1,0E-06
1,0E-05
1,0E-04
1,0E-03
1,0E-02
1,0E-01
1 2 3 4 5 6 7 8 9 10 11 12 13 14
Conce
ntr
ati
on (m
ol/
l)
pH
[Mg+2] as function of pH
Mortar CEM V/A GBFS-CFA
LXS model CEMV/A
CBP concrete VU 2009
1,0E-09
1,0E-08
1,0E-07
1,0E-06
1,0E-05
1,0E-04
1,0E-03
1 2 3 4 5 6 7 8 9 10 11 12 13 14
pH
[Fe+3] as function of pH
1,0E-06
1,0E-05
1,0E-04
1,0E-03
1,0E-02
1,0E-01
1 2 3 4 5 6 7 8 9 10 11 12 13 14
[SO4-2] as function of pH
Experimental data from USEPA Draft Method 1313
14
Impact: Uncertainty Reduction via Calibrationof Thermodynamic Model Parameters
Prior Best Fit
Most prominent changes: Stratlingite, hydrogarnet and ettringite
Al
15
Impact: Influence of Cement Type on DamageEttringite and Gypsum Profiles Damage Fronts
• Damage depends on both ettringite and gypsum formation; primary damage observed from ettringite for Type I and from gypsum for Type V cements.
0 0.005 0.01 0.015 0.02 0.0250
0.02
0.04
0.06
0.08
0.1
0.12
0.14
0.16
Depth (m)
Vol
ume
(m3 /m
3 of
mat
eria
l)
Ettringite (Type I)
Gypsum (Type I)
Ettringite (Type V)
Gypsum (Type V)
0 0.005 0.01 0.015 0.02 0.0250
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
Depth (m)
Dam
age
para
met
er
Type IType V
16
CBP Example Problem: Salt Waste Disposal System Integrity
Summary of Results for Sulfate Attack • Ability to model sulfate attack and resulting damage based on concrete
type (cement type, physical properties) and external sulfate concentration
• Probabilistic analysis for both model and parameter uncertainty
• Resulting models and parameters can be used for evaluation of a range of similar materials and scenarios
Impact• Allows selection of design parameters and materials to insure long-
term durability and meeting performance goals
• Results can be integrated into existing performance assessment fate and transport models
17
Sulfate Attack Modeling1. Transport of ions (saturated porous activity gradients)
• Driven by concentration and chemical activity gradients
2. Chemical Reactions• Calculation of liquid-solid equilibrium and solid phase distribution
using LeachXS/ORCHESTRA
3. Cracking• Continuum damage mechanics model (Tixier and Mobasher, 2003)
4. Effect of cracking on diffusivity• Relationships derived from fracture mechanics and numerical
simulations (Krajcinovic et al., 1992)
18
Sulfate Attack Modeling FrameworkDiffusion of Ions Leaching out of Ions
Chemical Reactions
Volume Change
Change in Porosity Strain
Cracking
Damage Parameter
Change in Diffusivity
Damage Assessment-Elastic Properties-Strength
19
Sulfate Attack – Probability of Complete Damage (Example Case)
Complete damage (failure criteria): Time required for cracks to propagate through the entire structure
Time to complete damage (years)
Percentiles
Case 1S = 250 mM
Case 2S = 120 mM
Case 3S = 56 mM
5th 78 109 338
25th 186 318 772
50th 285 508 1,135
75th 513 835 1,849
95th 1,886 4,354 6,120
20
CBP Example Problem: CO2 and O2 Ingress3-Layer Reference Scenario
Salt waste form(1)
Concrete(2)
Soil(3)
1000 cm 20 cm 50 cm
CO2
O2
• 3-Layer, 1-D diffusion model for reactive substances
• CO2 and O2 influx in soil layer proportional to partial pressure difference air-soil.
21
CO2 Ingress & Carbonation Modeling for Tank Integrity and Closure Scenarios
All CBP Partners Provide Unique Data Sources
SIMCO Tech., Inc.experimental results for validation
LEAF Leaching Methods
Method 1313 – Liquid-Solid Partitioning as a Function of Eluate pH using a Parallel Batch Procedure
Method 1314 – Liquid-Solid Partitioning as a Function of Liquid-Solid Ratio (L/S) using an Up-flow Percolation Column Procedure
Method 1315 – Mass Transfer Rates in Monolithic and Compacted Granular Materials using a Semi-dynamic Tank Leaching Procedure
Method 1316 – Liquid-Solid Partitioning as a Function of Liquid-Solid Ratio using a Parallel Batch Procedure
Note: Incorporation of these methods into SW-846 is ongoing; titles and method identification numbers are subject to change.
22
23
Develop a reasonable and credible set of tools to predict the structural, hydraulic and chemical performance of cement barriers used in nuclear applications over extended time frames (e.g.,
up to or >100 years for operating facilities and > 1000 years for waste management).
CBP Goal
Cementitious waste form in concrete disposal vault with cap (↔ Landfills Partnership)
Grouted high-level waste (HLW) tank closure Spent nuclear fuel pool integrity Nuclear processing facilities closure / D&D Grouted vadose zone to immobilize contamination Materials – surrogate low-activity waste (LAW)
cementitious waste form, reducing grout, reinforced concrete (historical) and reinforced concrete (future)
Example Uses and Reference Cases
Mechanistic / Phenomenological Basis
Parameter Estimation and Measurement
Boundary Conditions (physical, chemical interfaces)
Uncertainty Characterization
Basic Elements of the Performance Evaluation
Long-term Structural,
Hydraulic & Chemical
Performance of Cementitious Materials &
Barriers
Being Completed
CBP Coordinated Experimental and Computational Program Develop and improve conceptual models Define test methods and estimate important parameters Calibrate and validate models and perform probabilistic analyses
24
FY2012 CBP Focus• End-user licensing and training
• High-level waste (HLW) tank integrity and closureCarbonation rate as key to external attack
• ASCEM source term demonstration case
www.CementBarriers.org For further information and reports