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Sites
The Texas site is located near Sierra Blanca, which is about 120
km southeast of El Paso, Texas. The site is within the Chihuahuan
Desert of Texas. Long-term (30-yr) mean annual precipitation at
Sierra Blanca is 320 mm. The site consists of heavily instrumented
engineered covers that were installed in the summer of 1997. The
surface dimensions of the engineered cover are 34 × 17 m.
The Idaho site
is located at the Idaho National Engineering and Environmental Laboratory
in southeastern Idaho (Porro, 2001) on the Snake River Plain. Long-term
(40-yr) mean annual precipitation is 221 mm. The site consists of
a concrete structure containing 10 cells, each of which is 3 m ×
3 m × 3 m (four walls and a floor). Replicates of a monolithic
soil cover and a capillary barrier cover were constructed in the
cells. Data from only one of the monolithic soil cover cells are
used in this study.
Codes
This study demonstrates the variability in simulated water-balance
components using a variety of codes (listed above in Table 1) on
the basis of field monitored data from engineered covers at warm
(Texas) and cold desert (Idaho) sites and provides some indication
of the expected reliability of simulated water balances. Simulation
results from most codes were similar and generally reproduced measured
water-balance components at the Texas and Idaho sites. Both sites
consisted of unvegetated loam soil.
Simulation of
infiltration-excess runoff was a problem for all codes, underscoring
the difficulties of representing actual precipitation intensities
and of measuring hydraulic conductivity of surficial sediments (as
shown by the data from Texas). Drainage is the most critical parameter
for evaluation of contaminant transport, engineered covers for waste
containment, and groundwater recharge. Drainage could be estimated
to within ~ ± 64% by most codes. Outliers for the various
simulations could be attributed to the following factors:
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the
modeling approach, i.e., water-storage routing versus Richards'
equation, |
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the upper boundary condition during precipitation and time
discretization of precipitation input, |
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water retention functions (i.e., van Genuchten versus Brooks
and Corey), and |
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the lower boundary condition (i.e., unit gradient versus seepage
face). |
The water storage
routing approach does not seem to adequately represent the flow
system in semiarid regions. By assuming that gravity is the only
driving force and ignoring matric-potential gradients that are often
upward in semiarid regions, downward flow is generally overestimated
and ultimately results in overestimation of drainage.
The approach
used to simulate the upper boundary condition during precipitation
is crucial when precipitation is input on a daily or larger time
step. Setting PE to zero on rain days (VS2DTI) greatly underestimated
evaporation and overestimated drainage. Subtracting PE from precipitation
and applying net precipitation or net PE on a daily basis (HYDRUS-1D)
had a much lesser impact on simulation results. The best approach
is to disaggregate daily precipitation and apply it at a specified
rate, allowing PE to occur throughout the rest of the day, as shown
by the UNSAT-H simulations.
The impact of
water retention functions was demonstrated at the Idaho site, where
increased unsaturated hydraulic conductivity based on the Brooks
and Corey functions relative to the van Genuchten functions resulted
in overestimation of evaporation and underestimation of drainage.
In contrast, the input value of residual water content (0 for Campbell
function versus > 0 for Brooks and Corey) had little impact on
simulation results.
The most appropriate
lower boundary condition for simulating wickless lysimeters is a
seepage face. Simulations using HYDRUS-1D demonstrated that this
boundary condition could be approximated by simulating a thin bottom
layer of gravel with a unit gradient boundary condition in codes
that use Richards' equation but do not include a seepage face option.
However, use of a unit-gradient lower boundary condition alone greatly
overestimated drainage. This study demonstrates the usefulness of
conducting intercode comparisons to evaluate the reliability of
water-balance simulations and to determine important factors controlling
water-balance simulation results.
References
Scanlon, B. R., Christman, M., Reedy, R. C., and Gross, Beth, 2002,
Intercode comparisons
for simulating water balance in an engineered cover, in
2001 International Containment and Remediation Technology Conference,
Orlando, Florida, Institute for International Cooperative Environmental
Research, Florida State University, Paper ID. No. 148, http://www.iicer.fsu.edu,
3 p. [PDF]
Scanlon, B.
R., Christman, M., Reedy, R. C., Porro, I., Simunek, J., and Flerchinger,
G. N., in press,
Intercode comparisons for simulating water balance of surficial
sediments in semiarid regions: Water Resources Research. [PDF]
Scanlon, B.
R., Christman, M., Simunek, J., and Reedy, R. C., 2001, Intercode
comparisons for simulating water balance of near-surface soils
(abs.), in Eos, v. 82, no. 47, Fall Meeting Supplement, American
Geophysical Union, Abstract H12F-10. [PDF]
February
2003
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