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Upscaling and Inverse Modeling of Groundwater Flow and Mass ...

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CHAPTER 2. A COMPARATIVE STUDY OF THREE- . . . 21<br />

When block conductivities are represented by a tensor, the concept <strong>of</strong> how to<br />

average the block tensors in adjacent blocks is not clear. To overcome this<br />

difficulty, the code developed by Li et al. (2010) takes directly, as input, interblock<br />

conductivity tensors, removing the need <strong>of</strong> any internal averaging <strong>of</strong><br />

tensors defined at block centers. Within the context <strong>of</strong> upscaling, deriving the<br />

interblock conductivity tensors simply amounts to isolate the parallelepiped<br />

centered at the interface between adjacent blocks, instead <strong>of</strong> isolating the block<br />

itself, <strong>and</strong> then apply the upscaling techniques described in the previous section.<br />

In other contexts, the user must supply the interblock conductivity tensors<br />

directly. Several authors (Appel, 1976; Gómez-Hernández, 1991; Romeu<br />

<strong>and</strong> Noetinger, 1995; Li et al., 2010) have recommended to work directly with<br />

interblock conductivities for more accurate groundwater flow simulations.<br />

<strong>Mass</strong> transport is simulated using the advection-dispersion equation: (Bear,<br />

1972; Freeze <strong>and</strong> Cherry, 1979):<br />

∂C(x, t)<br />

ϕ = −∇·<br />

∂t<br />

( q(x)C(x, t) ) + ∇· ( ϕD∇C(x, t) )<br />

(2.9)<br />

where C is the dissolved concentration <strong>of</strong> solute in the liquid phase; ϕ is the<br />

porosity; D is the local hydrodynamic dispersion coefficient tensor, <strong>and</strong> q is<br />

the Darcy velocity given by q(x) = −K(x)∇h(x).<br />

As in the works <strong>of</strong> Salamon et al. (2007) <strong>and</strong> Llopis-Albert <strong>and</strong> Capilla<br />

(2009) at the MADE site, the r<strong>and</strong>om walk particle tracking code RW3D<br />

(Fernàndez-Garcia et al., 2005; Salamon et al., 2006) is used to solve the<br />

transport equation (2.9). In this approach, the displacement <strong>of</strong> each particle<br />

in a time step includes a deterministic component, which depends only<br />

on the local velocity field, <strong>and</strong> a Brownian motion component responsible for<br />

dispersion. A hybrid scheme is utilized for the velocity interpolation which<br />

provides local as well as global divergence-free velocity fields within the solution<br />

domain. Meanwhile, a continuous dispersion-tensor field provides a good<br />

mass balance at grid interfaces <strong>of</strong> adjacent cells with contrasting hydraulic<br />

conductivities (LaBolle et al., 1996; Salamon et al., 2006). Furthermore, in<br />

contrast to the constant time scheme, a constant displacement scheme (Wen<br />

<strong>and</strong> Gómez-Hernández, 1996a), which modifies automatically the time step<br />

size for each particle according to the local velocity, is employed in order to<br />

reduce computational effort.<br />

2.4.2 <strong>Upscaling</strong> design <strong>and</strong> error measure<br />

In this work, we have performed both uniform <strong>and</strong> non-uniform upscaling. In<br />

the case <strong>of</strong> uniform upscaling, the original hydraulic conductivity realization<br />

discretized into 110 × 280 × 70 cells <strong>of</strong> 1 m by 1 m by 0.15 m is upscaled onto<br />

a model with 11 × 28 × 14 blocks <strong>of</strong> 10 m by 10 m by 0.75 m. This upscaling

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