VZJ sign up for etocs
HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
 QUICK SEARCH:   [advanced]


     


Published online 8 March 2006
Published in Vadose Zone J 5:126-127 (2006)
DOI: 10.2136/vzj2005.0077L
© 2006 Soil Science Society of America
677 S. Segoe Rd., Madison, WI 53711 USA
This Article
Right arrow Figures Only
Right arrow Full Text (PDF) Free
Right arrow Alert me when this article is cited
Right arrow Alert me if a correction is posted
Services
Right arrow Similar articles in this journal
Right arrow Similar articles in ISI Web of Science
Right arrow Alert me to new issues of the journal
Right arrow Download to citation manager
Right arrow reprints & permissions
Citing Articles
Right arrow Citing Articles via Google Scholar
Google Scholar
Right arrow Articles by Groenendijk, P.
Right arrow Articles by Van Dam, J.C.
Right arrow Search for Related Content
PubMed
Right arrow Articles by Groenendijk, P.
Right arrow Articles by Van Dam, J.C.
GeoRef
Right arrow GeoRef Citation
Agricola
Right arrow Articles by Groenendijk, P.
Right arrow Articles by Van Dam, J.C.

COMMENTS

Comments on "A Set of Analytical Benchmarks to Test Numerical Models of Flow and Transport in Soils"

P. Groenendijk, J.G. Kroes and J.C. Van Dam

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 convection–dispersion 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:

  1. Changes in both the volumetric water content and the pressure head are used to test progress of the iteration cycle. The criterion for the volumetric water content is user-supplied, while the criterion for the change of pressure head is fixed in the model code.
  2. When progress of the numerical solution is not sufficient within six iterations, the time step is decreased and the iteration cycle starts again. It appeared that the maximum number of six was not sufficient for this case. After increasing this maximum to 20, the model generated a stable pressure head profile, although results were still not accurate.
  3. The hydraulic conductivity is described as a function of relative saturation (Se) using the analytical Mualem–van Genuchten function (van Genuchten, 1980) (MVG). Near saturation the SWAP model uses a not well documented linearization of this function: in the range 0.99 < Se < 1.00, the hydraulic conductivity is linearly interpolated between its value at Se = 0.99 according to van Genuchten (1980) and the saturated hydraulic conductivity at Se = 1.00. Figure 1 shows the effect of this linearization. In the benchmark test the final relative saturation of the clay layer was >0.99 and the linearization caused higher conductivity values than would be the case for the analytical MVG model.


Figure 1
View larger version (9K):
[in this window]
[in a new window]
 
Fig. 1 Conductivity of the clay soil and linearization of this relation near saturation. ksat = 10 (cm d–1); {alpha} = 0.01 (cm–1); n = 1.1; {lambda} = 0.5.
 
After increasing the maximum number of iterations and disabling the linearization of the conductivity near saturation, the SWAP model exactly reproduced the analytical solution of the infiltration problem. We expect that computer codes which internally use tabulation for the MVG model will also exhibit deviations from the exact analytical solution for the infiltration case.

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 {theta}(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





This Article
Right arrow Figures Only
Right arrow Full Text (PDF) Free
Right arrow Alert me when this article is cited
Right arrow Alert me if a correction is posted
Services
Right arrow Similar articles in this journal
Right arrow Similar articles in ISI Web of Science
Right arrow Alert me to new issues of the journal
Right arrow Download to citation manager
Right arrow reprints & permissions
Citing Articles
Right arrow Citing Articles via Google Scholar
Google Scholar
Right arrow Articles by Groenendijk, P.
Right arrow Articles by Van Dam, J.C.
Right arrow Search for Related Content
PubMed
Right arrow Articles by Groenendijk, P.
Right arrow Articles by Van Dam, J.C.
GeoRef
Right arrow GeoRef Citation
Agricola
Right arrow Articles by Groenendijk, P.
Right arrow Articles by Van Dam, J.C.


HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
The SCI Journals Agronomy Journal Crop Science
Journal of Natural Resources
and Life Sciences Education
Soil Science Society of America Journal
Journal of Plant Registrations Journal of
Environmental Quality
The Plant Genome