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RD&D-Programme 2004 - SKB

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Q3<br />

Tunnel<br />

Crushed rock - bentonite<br />

Canister<br />

Bentonite<br />

Q2<br />

Disturbed zone<br />

Damage (hole)<br />

Rock<br />

Deposition hole<br />

Fuel<br />

Q1<br />

Bentonite<br />

Channel<br />

Canister wall<br />

Fracture zone<br />

Q4<br />

Figure 14-4. Schematic view of the near-field, with the transport pathways used in SR 97.<br />

Figure 14-4 shows how the deposition holes and the backfill in the deposition tunnel were<br />

modelled in SR 97. In the model, four different flow paths, Q1–Q4, were used for the interface<br />

between near-field and far-field.<br />

To represent the barrier system through which radionuclides are transported, Comp23 makes use<br />

of an integrated finite difference method and the compartment concept.<br />

The far-field model<br />

The far field model for SR-Can is similar to the one used in SR 97. This model, Farf31, /14-8/<br />

calculates the transport of dissolved radionuclides through fractured rock, the retention caused<br />

by interactions between the nuclides and the rock matrix, and radioactive chain decay.<br />

The biosphere model<br />

Radionuclide transport through the biosphere and doses to man were handled in SR 97 by the<br />

Proper sub-module Bio42. This module was based on nuclide- and ecosystem-specific dose<br />

conversion factors (EDFs), which convert nuclide releases to an ecosystem into doses. In SR 97,<br />

the EDFs for the six ecosystems considered (well, lake, river, peat, soil, coast) were calculated<br />

in a separate code /14-10/ using generic data for the ecosystem parameters. The different<br />

ecosystems were represented by compartment models where each compartment corresponded<br />

to a distinct part of an ecosystem. Figure 14-5 shows the example of a peat bog modelled as<br />

two compartments, representing nuclides dissolved in water and nuclides sorbed to organic<br />

and/or solid material, respectively. The nuclide exchange between the two compartments was<br />

modelled using ecosystem- and element-specific distribution coefficients (Kd). In the modelled<br />

peat bog, Figure 14-5, both nuclide inflow and outflow take place in the soluble phase and are<br />

therefore controlled by the water balance. Depending on the water exchange at the studied site,<br />

in- and outflow may take place to other ecosystem models, inflow may take place from release<br />

points from the geosphere’s streamtubes, or outflow of nuclides may take place from the model<br />

domain. However, in SR 97, only single ecosystems were considered with inflow only from<br />

release points from streamtubes.<br />

RD&D-<strong>Programme</strong> <strong>2004</strong> 161

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