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Published byErik Malone Modified over 9 years ago
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Fresh water lenses on saline groundwater Dispersive Behavior of the Mixing Zone between a Shallow Freshwater Lens and Upward Seeping Saline Groundwater S.Eeman, A. Leijnse, S.E.A.T.M. van der Zee Wageningen UR, Sub-department of Soil Physics, Ecohydrology and Groundwater management
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Background Low lying areas Changing climate Non-equilibrium of ground water system Influence on land use options? Characterization of small scale system Source: G. Oude Essink, Deltares
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Lens on field Scale Most relevant for users Mixing zone not negligible Boundary conditions well defined
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Methods Numerical modeling using SUTRA Density dependent Unsaturated zone Analysis of results using spatial moments of concentration change with depth δc/δz Z
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Comparison to the analytical solution by Maas (2007) Analyses of dispersion and diffusion Results
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Numerical vs Maas(2007) First vertical moment dC/dy From initially saline towards steady state Steady state Max. thickness in time
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Processes contributing to mixing Different processes Different circumstances Phase Location Num. calculations Local coordinate system Parallel to “interface” Less accurate near ditch Longitudinal dispersion Transverse dispersion Molecular diffusion
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Contributions to mixing I Moving ‘interface’Steady state conditions
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Contributions to mixing II 5m 15m 25m
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Conclusions Steady conditions: analytical model of Maas (2007) is a very good approximation Contribution of dispersion and diffusion to mixing depend on phase and location Developing lens: longitudinal dispersion Steady state: transverse dispersion / diffusion Mid field: BC prohibits transverse dispersion Near ditch: transverse dispersivity
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Current work Start of fieldwork in Zeeland with P. de Louw, Deltares (thanks!) Sensitivity of a fresh water lens for different climatic conditions
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Thank You!
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