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Wageningen UR, P.O. Box 47, 6700 AA, Wageningen, The Netherlands
piet.groenendijk{at}wur.nl
The increasing demand for detailed information on hydrological processes as they are influenced by land use, soil characteristics, and water management have encouraged the development of dynamic process-oriented models. Currently applied models are not perfect and have to be thoroughly tested and validated. The awareness of the need for good modeling practice protocols is increasing outside the academic community as well. Testing protocols include verification of (numerical) model codes and validation against field experiments. Therefore, we were very pleased with the paper by Vanderborght et al. (2005) on benchmark tests for numerical models that use Richards' equation for water flow and the convectiondispersion equation for solute transport.
For the case with high infiltration into a soil profile with clay above sand, the SWAP model (Van Dam et al., 1997; Kroes and van Dam, 2003) reproduced exactly the water balance but showed deviations in the computed soil water pressure head profile. Vanderborght et al. (2005) attributed these deviations to the use of volumetric water content changes as a stopping criterion in the iteration procedure, instead of soil water pressure head changes.
Further inspection of the model and the SWAP computer code for this case indicated the following:
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While the benchmark tests presented by Vanderborght et al. (2005) are very useful to test model performance, one may question whether they are representative for practical applications. Especially the parameterization used for the clay soil seems to lack any physical basis. Due to the low n value, the difference between k(h) at 1 cm pressure head and ksat is very large (Fig. 1). At h = 0.1 cm the conductivity is already <25% of ksat. At this pressure head, the air entry value of clay soils will not yet be reached, and the clay matric is still saturated. Therefore, such a large drop in the hydraulic conductivity is not realistic. Vogel et al. (2001) showed that the shape of the k function near saturation can have a large impact on variably saturated flow predictions. The broken line depicts the linearization employed by the SWAP model. This linearization causes the conductivity at the soil surface to be overestimated by a factor of 8.75 times.
Our main conclusions are that the input options of the SWAP model were insufficient for direct application to the infiltration case of a clay soil on top of coarse sand. While linearization of the MVG relation near saturation proved to be a hidden model option useful for practical field simulations, this also caused deviations from the pressure head profile for the extreme case we tested. To increase user flexibility we will release a new version of SWAP that offers input of k(h) and
(h) directly in tabular form in addition to analytical MVG functions. Documentation will be improved and an extensive test-set will be made available for download from our web site (www.swap.alterra.nl [verified 13 Jan. 2006]).
REFERENCES
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