Douglas D. Walker, DE&S Jan-Olof Selroos, SKB Supported by Swedish Nuclear Fuel and Waste Management Co. (SKB)
Presentation Overview Context and Objectives of the Alternative Models Project The hypothetical Aberg Repository 3 alternative conceptual models of heterogeneity Performance measures Results and Conclusions
Deep Geologic Disposal of Nuclear Waste
Nuclear Waste Disposal Performance Assessment
Uncertainty vs. variability Uncertainty in: - process physics
- measurement
- characterization of heterogeneity
- upscaled representation in models
The Alternative Models Project Nuclear waste disposal performance assessment uncertainty analysis Compare alternative representations of flow / transport in fractured rocks Explicit definition of
Aberg Repository
Aberg Site and Data Hydrogeologic Setting: - Inland recharge, discharge to Baltic
- Fractured granitic rocks
- Large-scale fracture zones (deterministic)
Data: - 53 Boreholes (hydraulic/tracer tests, chem)
- geophysics, fracture trace maps
- Äspö Hard Rock Laboratory
Regional model / boundary conditions
Alternative Conceptual Models
Conductivity distribution - 3m K tests 25m, Lognormal + variogram
- Rock & Conductor distributions
- homogeneous ar = 1.2 m2/m3 rock
Structural model Repository - 945 canisters x 34 realizations
Stochastic Continuum: Travel Paths
Advantages: - hydraulic tests are volume averages
- method / software well-established
Disadvantages: - Scale dependence of K in fractured media poorly understood
- Preferential paths not represented at scales below block size
Discrete Fracture Network
Discrete Fracture Network: Application Fracture Distribution - Deterministic Zones and Canister fractures
- Lognormal, with 20 R 1000m in region and 0.2 R 20m at repository
- Lognormal transmissivity
- ar = f (area between fracture traces)
Repository - 50 to 90% of 81 canisters x 10 realizations
Discrete Fracture Network: Travel Paths
Discrete Fracture Network Advantages: - Represents the conductive structures (Realism)
- Allows for preferential paths
Disadvantages: - Data demand
- Computational demand
- Matrix permeability may be important
Flow Channeling
Channel Network Intersections
Channel Network: Application Conductance Distribution - 3m K tests 30m, Lognormal
- Rock, Conductor, & EDZ distributions
- ar = 1.2 m2/m3 in Zones, 1/10 in Rock
Structural model Repository - 229 cans x 30 real x median (200 particles)
Channel Network: Travel Paths
Channel Network Advantages: - Represents observed channels within fracture planes, directly assigns ar
- Allows for preferential paths and dispersion
- Includes diffusion/sorption in matrix, flow within Rock
Disadvantages: - Conductance is scale dependent
Application Summary
Simulation Summary
Performance Measures Travel time: canister to biosphere tw = qw/f [yr] Canister Flux: Darcy flux at canisters qw [m/yr] F-factor: Retardation vs. Advection F = (dw ar) / qw [yr/m]
Performance measures: Medians
Performance measures: Variances
Discussion - (Controlled by premises of BC, major zones)
For DFN, F-factor variance greater than tw variance (variability of ar impacts PA) SC variances greatest, but differences in studies complicate comparison
Discussion II Modeling study differences: - # particles released
- SC = one / canister
- DFN = one / canister subset
- CN = median of 200 / canister subset
- # canisters with pathways
- 100% in SC and CN; 50 to 90% in DFN
- Not evaluated: team experience, Sensitivity of inference to data
SC and CN boundary flow, DFN low
Conclusions For this site and these performance measures: Problem premises constrain the results Uncertainties regarding conceptual models of flow / transport in fractured rocks have limited effect on PA Chief benefit of DFN / CN is to examine effects of ar
Acknowledgements SC Modeling Study: H.Widén (Kemakta), D. Walker (DE&S) DFN Modeling Study: W Dershowitz, S Follin, T Eiben, J Andersson (GA) CN Modeling Study: B. Gylling, L. Moreno, I. Neretnieks (KTH) Swedish Nuclear Fuel and Waste Management Co. A. Ström, J-O. Selroos (SKB)
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