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RD&D-Programme 2004 - SKB

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Newfound knowledge since RD&D 2001<br />

Advection is a process that is generally well-understood /19-53/. Accordingly, no new<br />

knowledge has emerged during the present period which contradicts previous knowledge.<br />

However, some additional support has emerged for existing knowledge. An example is<br />

simulation of advective transport in individual fracture planes /19-54/. Even though the study<br />

mainly deals with diffusion processes, certain conclusions can nonetheless be drawn regarding<br />

how the advective and dispersive processes influence transport. Specifically, it is shown that the<br />

effect of transverse dispersion is small with regard to the transport resistance (F factor).<br />

Simulations of discrete fracture networks have been done to understand the dependence of the<br />

transport resistance (F factor) on various properties of the network /19-55/. The results show<br />

that the assumption of complete mixing, or streamline routing, at fracture intersections does not<br />

significantly affect the results. This is important, since it is difficult to prove which assumption<br />

is most correct. Furthermore, it is shown that the results are sensitive to whether the fracture<br />

intensity, expressed by the so-called P32 value, dramatically decreases. Finally, it is shown that<br />

retention is typically underestimated in the type of channel models /19-56, 19-57/ that are often<br />

used for transport calculation in conjunction with FracMan simulations. In the study in question,<br />

transport has been simulated directly in the two-dimensional fracture planes rather than being<br />

simplified to one-dimensional channels. The results in /19-55/ have also been used in a parallel<br />

study /19-58/. This study shows that the distribution of (bv) –1 , where b is the half-aperture and v<br />

is the velocity of the water, follows a power-law distribution. The transport resistance (F factor)<br />

is in turn dependent on the distribution of (bv) –1 . The results indicate that transport that is<br />

characterized by this type of power-law distribution cannot be described by a classic advectiondispersion<br />

equation, but that more sophisticated methods are needed if analytical approaches<br />

are to be used. The results from /19-55/ have also been used in /19-59/, where it has been<br />

investigated whether the transport resistance can be estimated from quantities measured in the<br />

field. Under certain circumstances the transport resistance can be expressed as a linear function<br />

of the advective travel time and an effective retention aperture. This aperture can be estimated<br />

from transmissivity data or fracture density and porosity data. However, the results indicate that<br />

these simplified estimates tend to overestimate retention, which is why explicit calculation of<br />

the transport resistance in a numerical discrete model is preferable.<br />

Numerical simulations have also been carried out with the code Chan3D for transport in<br />

transient flow fields /19-21/. In this study, transport (advection and matrix diffusion) were<br />

simulated in a flow field that changes with time. The results indicate that transient flow can be<br />

important to incorporate in the analysis of radionuclide transport when shoreline displacement<br />

occurs. This type of study requires a coupled modelling strategy, i.e. that both flow and transport<br />

are simulated in the same model. <strong>SKB</strong>’s primary modelling strategy is to model flow and<br />

transport separately. To justify such an approach, the limitations must be investigated in detail.<br />

This can be done with the type of modelling tool presented in /19-21/.<br />

<strong>Programme</strong><br />

No programme will be initiated to specifically understand advection as a process. However, the<br />

studies of advection and matrix diffusion during transient flow will continue. The objective here<br />

is to understand specifically how transient flow effects that occur due to shoreline displacement<br />

affect radionuclide transport, and how simplified analyses based on separate flow and transport<br />

modelling can be bounded. The purpose is thus to be able to use, in the safety assessment for<br />

example, a coupled model in order to get a feeling for the limitations implied by a simplified<br />

analysis.<br />

A project aimed at studying how the transport resistance (F factor) can be up-scaled from<br />

detailed to block and site scales has been commenced and will continue. Preliminary results<br />

have been presented in /19-60/. The results show how sampling of the transport resistance on<br />

a small scale can be used to calculate the transport resistance on a larger scale by means of<br />

RD&D-<strong>Programme</strong> <strong>2004</strong> 257

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