1 / 20

HYDRUS_1D Sensitivity Analysis

This study aims to identify the most important parameters in water flow simulation in the vadose zone, allowing users to allocate resources effectively. The HYDRUS-1D software package is used to model the one-dimensional movement of water and solutes in variably saturated media. Sensitivity analysis reveals that parameters such as saturated hydraulic conductivity (Ks) and saturated water content (θs) have significant influence on the vadose zone flow.

rshepard
Download Presentation

HYDRUS_1D Sensitivity Analysis

An Image/Link below is provided (as is) to download presentation Download Policy: Content on the Website is provided to you AS IS for your information and personal use and may not be sold / licensed / shared on other websites without getting consent from its author. Content is provided to you AS IS for your information and personal use only. Download presentation by click this link. While downloading, if for some reason you are not able to download a presentation, the publisher may have deleted the file from their server. During download, if you can't get a presentation, the file might be deleted by the publisher.

E N D

Presentation Transcript


  1. HYDRUS_1D Sensitivity Analysis Limin Yang Department of Biological Engineering Sciences Washington State University

  2. INTRODUCTION • 1. To find the parameters of greatest importance in water flow simulation in vadose zone. • 2. To allow users to budget resources so that the most important parameters can be determined with the greatest accuracy.

  3. HYDRUS-1D HYDRUS-1D is a commercial software package based on finite element model, for simulating the one-dimensional movement of water and solute in variably saturated media. This program was developed by U.S. Salinity Laboratory, U.S. Department of Agriculture, Agriculture Research Service (Simunek and van Genuchten, 1998).

  4. Governing Equations (2)

  5. INTEC SITE

  6. Soil distributions at INTEC

  7. Soil Properties • There are two major types of soil, sediment and basalt, at INTEC. The average surficial alluvium samples saturated hydraulic conductivity Ks is 4.1x10-2 cm/sec. The average interbeds’ Ks is 1.221x10-4 cm/sec. α is between 0.0001 and 1.9868. n is between 1.1024 and 4.2289. θr is between 0 and 0.0764. θs is between 0.2247 and 0.6049.

  8. Methods • The sensitivity of model results to any given parameter can be described by the partial derivative of an output variable with respect to that parameter. • 2. The change in cumulative bottom flux was calculated as: Where, ΔR is percent change in the result value of the testing function Rt is result value for using the test parameter value Rb is result value for using the base parameter value

  9. Basic settings • Only consider water flow; • Only one type soil will be considered with a depth of 500 cm, and there is no incline from vertical axis; • Totally 512 min with each time step 1e-5, and the maximum time step is 25 min; • The maximum number of iteration is 50, with all other iteration criteria default;

  10. Basic settings (cont’d) • Hydraulic model is van Genuchten without air-entry value and no hysteresis; • Soil properties based on sand; • Upper boundary condition is constant pressure head; Lower boundary condition is free drainage; Initial condition is in the pressure head (10 cm water head on the top, -100 cm water head for other part of soil).

  11. Table 1. Outline

  12. NUMERICAL RESULTS • α This experimental parameter was introduced for expressing the relationship of soil water content and the pressure head. It will influence the shape of the retention curve. In most case, since α is a small number and with a power of n, which is bigger than 1, it should not be a sensitive factor. Experiments’ results proved this true as shown in Table 2. The cumulative bottom flux changes less than 3% while α changes 25%.

  13. Table 2. Results

  14. Residual water content θr • It is not strange that θr has only very limited influence on the cumulative bottom flux, since θr is too small comparing to θs. The cumulative bottom flux changes less than 3.5% while θr changes 25%. • Saturated water content θs • θs determines θe, the effective water content, which is a critical factor for solving governing equation. It is sensitive parameter to the bottom flux causing about 60% change in flux while itself changes only 25%. Notably, there is a negative linear relationship between θs and the bottom flux. This can also be explained because that it occurs in the formula of θe as a denominator.

  15. n • Empirical parameter n occurs in formula (2, 3) as a power of h. It is also less sensitive to the flux although its influence to the bottom flux is bigger than those of α and θr. It causes at most 12% changes in flux while itself changes 25%. • Saturated hydraulic conductivity Ks • Ks is of most sensitivity in all the parameters, as a key factor of equation (1). It also has a linear relationship with the cumulative bottom flux with a slope of about 3.2, which means that one unit change in Ks will cause 3.2 unit changes in flux. • l • Empirical factor l is almost fixed as 0.5 according Simunek, J., M. Sejna, and M. Th. van Genuchten. (1998). In this study, it is the least important factor to the flux.

  16. Discussion and conclusions • Hysteresis is an important phenomenon in soil physics and will have influence on the ground water flow. But comparisons of the runs of HYDRUS_1D indicate it has no significant effect on the cumulative flow flux (in most cases no effect). • From the results, Ks and θs are very sensitive parameters to the vadose zone flow. In reality, Ks and θs are localized and cannot easily get with respect to the limitations of field methods. These will greatly hamper the solution of vadose zone flow and in turn influence of solute transport.

  17. Thank You

  18. References Simunek, J., M. Sejna, and M. Th. van Genuchten. 1998. The HYDRUS_1D Software Package for Simulating the One-Dimensional Movement of Water, Heat, and Multiple Solutes in Variably-Saturated Media. Version 2.0. US Salinity Laboratory, ARS/USDA. Riverside, California. • Hull, L.C.et al, 1999, Draft Work Plan for the Waste Area Group 3, Operable Unit 3-14, Tank Farm Soil and Groundwater, Remedial Investigation/Feasibility Study. INEEL. • Hull, L.C.et al, 2002, Phase I Monitoring Well and Tracer Study Reportfor Operable Unit 3-13, Group 4, Perched Water. DOE. • Jacomino, V.M.F., Fields, D.E. “A critical approach to the calibration of a watershed model.” 1997. American Water Resources Association. 33 (1), 143-154 • van Genuchten, M. Th. 1980. A Closed-Form Equation for Predicting the Hydraulic Conductivity of Unsaturated Soils. Soil Science Society American Journal. Vol. 44, pp 892-898.

More Related