Version: 3.0
Public Domain Software
Click here to download the Hydrus1D zip file
Click here to download the Hydrus1D manual in pdf
HYDRUS-1D is a Microsoft Windows-based
modeling environment for analysis of water flow and solute transport in variably
saturated porous media.
The software package includes the one-dimensional finite element model HYDRUS (version 7.0) for simulating the movement of water, heat, and multiple solutes in variably saturated media.
The model is supported by an interactive graphics-based interface for data-preprocessing, discretization of the soil profile, and graphic presentation of the results.
HYDRUS Model (version 7.0)
The HYDRUS program is a finite element model for simulating the one-dimensional movement of water, heat, and multiple solutes in variably saturated media. The program numerically solves the Richards' equation for saturated-unsaturated water flow and Fickian-based advection dispersion equations for heat and solute transport. The Flow equation incorporates a sink term to account for water uptake by plant roots. The Heat transport equation considers conduction as well as convection with flowing water. The Solute transport equations consider advective-dispersive transport in the liquid phase, and diffusion in the gaseous phase.
The transport equations also include
provisions for:
* Nonlinear
* and/or Nonequilibrium reactions between the solid and liquid phases, Linear
equilibrium reactions between the liquid and gaseous phases,
* Zero order production, and
* Two First order degradation reactions:
* One which is independent of other solutes, and
* One which provides the coupling between solutes involved in sequential first-order
decay reactions.
The program may be used to analyze water and solute movement in unsaturated, partially saturated, or fully saturated porous media. The flow region itself may be composed of nonuniform soils. Flow and transport can occur in the vertical, horizontal, or a generally inclined direction. The water flow part of the model can deal with (constant or time-varying) prescribed head and flux boundaries, boundaries controlled by atmospheric conditions, as well as free drainage boundary conditions. Soil surface boundary conditions may change during the simulation from prescribed flux to prescribed head type conditions (and vice versa).
For solute transport the code supports
both (constant and varying) prescribed concentration (Dirichlet or first-type)
and concentration flux (Cauchy or third-type) boundary conditions. The dispersion
coefficient includes terms reflecting the effects of molecular diffusion and
tortuosity.
The Unsaturated Soil Hydraulic Properties are described using van Genuchten [1980], Brooks and Correy [1964] and modified van Genuchten type analytical functions. Modifications were made to improve the description of hydraulic properties near saturation. The HYDRUS code incorporates hysteresis by using the empirical model introduced by Scott et al. [1983] and Kool and Parker [1987]. This model assumes that drying scanning curves are scaled from the main drying curve, and wetting scanning curves from the main wetting curve.
HYDRUS also implements a scaling procedure to approximate hydraulic variability in a given soil profile by means of a set of linear scaling transformations which relate the individual soil hydraulic characteristics to those of a reference soil.
Root growth is simulated by means of a logistic growth function. Water and salinity stress response functions can be defined according to functions proposed by Feddes et al. [1978] or van Genuchten [1987].
The governing flow and transport equations are solved numerically using Galerkin type linear finite element schemes. Integration in time is achieved using an implicit (backwards) finite difference scheme for both saturated and unsaturated conditions. Additional measures are taken to improve solution efficiency for transient problems, including automatic time step adjustment and adherence to preset ranges of the Courant and Peclet numbers. The water content term is evaluated using the mass conservative method proposed by Celia et al. [1990]. Possible options for minimizing numerical oscillations in the transport solutions include upstream weighing, artificial dispersion, and/or performance indexing.
HYDRUS implements a Marquardt-Levenberg
type parameter estimation technique for inverse estimation of selected soil
hydraulic and/or solute transport and reaction parameters from measured transient
or steady-state flow and/or transport data. The procedure permits several unknown
parameters to be estimated from observed water contents, pressure heads, concentrations,
and/or instantaneous or cumulative boundary fluxes (e.g., infiltration or outflow
data). Additional retention or hydraulic conductivity data, as well as a penalty
function for constraining the optimized parameters to remain in some feasible
region (Bayesian estimation), can be optionally included in the parameter estimation
procedure.
User Interface
A Microsoft Windows-based graphical
user interface (GUI) manages the input data required to run HYDRUS, as well
as for nodal discretization and editing, parameter allocation, problem execution,
and visualization of results.
All spatially distributed parameters,
such as soil type/layer, root water uptake distribution, and the initial conditions
for water, heat and solute movement, are specified in a graphical environment.
The location of discretization nodes
can be graphically edited by a user to optimize the thickness of different elements.
The program includes controls to
allow a user to build an application specific flow and transport model, and
to perform graphical analyses on the fly.
Both input and output can be examined
using graphical tools.
The HYDRUS-1D shell program translates
all geometric and parameter data into the HYDRUS input format.
File management is handled by a sophisticated
project manager.
Post-Processing
Post-processing is also carried out
in the shell.
HYDRUS-1D offers graphs of
the distribution of the pressure head, water content, water and solute fluxes,
root water uptake, temperature and the concentration in the soil profile at
preselected times. Output also includes variable-versus-time
plots, such as actual, potential and cumulative fluxes across boundaries or
leaving the root zone. Observation points can be added anywhere
in the profile to obtain graphical output for the water content, pressure head,
temperature, and/or the concentration. Peripheral devices supported include
most popular types of printers and plotters. A small catalog of soil hydraulic
properties is included in the program. Extensive context-sensitive, online
Help is part of the interface. Test Examples distributed with the
model:
Direct:
1. Water Flow and Solute Transport
in a field soil profile under grass
Seasonal simulation
2. Infiltration and Drainage in a large caisson
3. Transient Flow involving hysteresis
4. Skaggs' Column Infiltration Test
5. Solute Transport with nonlinear cation adsorption - Data from Lai and Jurinak
6. Solute Transport with nonlinear cation adsorption - Data from Selim
7. Solute Transport with nitrification chain
8. Solute Transport with non-equilibrium cation adsorption
9. Heat Transport under fluctuating atmospheric condition
Inverse:
1. One-step outflow experiment -
Data from Kool et al. (1987)
2. Multistep Outflow Experiment - Data from Jan Hopmans
3. Evaporation Experiment - Data from Ole Wendroth
4. Upward Infiltration
5. Transient Flow involving hysteresis
6. Solute Transport with nonlinear cation adsorption - Data from Lai and Jurinak
7. Solute Transport with nonlinear cation adsorption - Data from Selim
8. Solute Transport with nitrification chain
9. Horizontal infiltration - Data from George Vachaud
10. Horizontal infiltration and redistribution - Data from George Vachaud
11. Drainage in a sand column - Data from George Vachaud
12. Water Flow in a field soil profile under grass - Seasonal simulation
System Requirements:
Intel 80386 with math coprocessor,
Intel 80486DX, or higher processor, 4 Mb RAM, DOS 5.0 or higher, hard disk with
at least 10 Mb free disk space, VGA graphics (SVGA with 256 colors recommended),
MS Windows 95, 98, or Windows NT.
Developers: U.S. Salinity Laboratory (USDA/ARS) Riverside, CA