Physical processes and governing equations

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Revision as of 12:43, 9 February 2017 by Klmos (talk | contribs) (Contaminant transport)
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Physical processes

Flow in fractured limestone can be very complex, because strongly contrasting flow conditions between fractures and matrix can prevail. The flow in the fractures can be very fast, whereas the limestone matrix has usually low flow velocities, which is characterized by relatively low hydraulic conductivities (or permeabilities). However, the fate of contaminants in fractured limestone aquifer is determined by both, the fractures and the matrix. Transport of substances in porous media can be subdivided in advective transport (due to the groundwater flow) and diffusive/dispersive transport (related to concentration gradients).

The fractures are the primary transport pathways for contaminants, where mainly advective transport dominates. The hydraulic conductivity of the fractures is mainly depending on their aperture (width). For an estimation of the flow velocity in fractures, the cubic law is often used as approximation. With that, the velocity scales with the third power of the fracture aperture. Hence, fractures with a big aperture are far more important as small fractures, since the flow and the velocity are greater in them. The connectivity of the fractures is another very important parameter for the spreading of a substance in the aquifer.

While being transported through the fractures, the contaminant diffuses into the surrounding matrix. Once diffused into the matrix, the contaminant is difficult to get out again, since the matrix provides usually a high porosity and can store substantial amounts of contaminants. Due to the extremely low flow velocities in the limestone matrix, the removal of a contaminants happens again due to diffusion back to the fractures.

Part of the contaminant can be sorbed to the surface of the limestone matrix (and the fracture walls). The sorption behavior is often quantified by sorption coefficients.

Governing equations

Flow

Groundwater flow in porous media can be described by Darcy's law, giving a relation between hydraulic head gradient and groundwater flow, with the hydraulic conductivity as proportionality factor. The flow field is calculated by solving the mass balance for incompressible fluid flow in combination with Darcy's law. The conductivities in the fractures can be several orders of magnitude higher than the conductivity of the limestone matrix. The fracture conductivity is usually calculated via the fracture aperture using the cubic law, which gives a relation between fracture aperture and .

include: Mass balance, groundwater flow equation. Cubic law.

Contaminant transport

The advection-dispersion equation is a balance equation for the transport of a substance in a porous medium. The first term describes the storage (here including retardation due to linear sorption), the second and third terms describe advective and dispersive transport of a substance. Degradation can be included as additional source/sink term.

The transport equation for an equivalent porous medium model.

Variables are:

Variable Name
n porosity
rho_b bulk density
k_d sorption coefficient
c concentration
v flow velocity
D_m dispersion coefficient


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