Table of contents
Chapter 1. Overview
Chapter 2. Radiation
Chapter 3. Turbulent diffusion and interactions
with the surface
Chapter 4. Subgrid-scale orographic drag
Chapter 5. Convection
Chapter 6. Clouds and large-scale precipitation
Chapter 7. Land suface parametrization
Chapter 8. Methane oxidation
Chapter 9. Climatological data
REFERENCES
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The vertical movement of water in the unsaturated zone of the soil matrix
obeys the following equation (see Richards (1931), Philip (1957), Hillel (1982), and Milly
(1982) for the conditions under which Eqs. (7.57) and (7.58) are valid) for the
volumetric water content :
is the water density ( ), is the water flux in the soil (positive downwards, ), and is a volumetric sink term ( ), corresponding to root extraction. Using Darcy's law, can be specified as:
( ) and ( ) are the hydraulic diffusivity and hydraulic conductivity, respectively.
Replacing (7.58)
in (7.57), specifying
, and defining parametric relations for and as functions of soil water, a partial differential equation for is obtained; it can be numerically integrated
if the top boundary condition is precipitation minus evaporation minus surface
runoff. The bottom boundary condition assumes free drainage. Abramopoulos et al. (1988) specified
free drainage or no drainage, depending on a comparison of a specified geographical
distribution of bedrock depth, with a model-derived water-table depth. For
the sake of simplicity the assumption of no bedrock everywhere has been
adopted.
The interception reservoir is a thin layer on top of the soil/vegetation,
collecting liquid water by the interception of rain and the collection of
dew, and evaporating at the potential rate. The water in the interception
reservoir, , obeys
where is the water evaporated by the interception reservoir (or dew
collection, depending on its sign), D represents the dew deposition
from other tiles, and ( ) is the interception-the fraction of
precipitation that is collected by the interception reservoir and is later
available for potential evaporation. Because the interception reservoir
has a very small capacity (a maximum of the order of 1 mm, see Eq. (7.2)), it can fill up or
evaporate completely in one time step; special care has to be taken in order
to avoid numerical problems when integrating Eq.
(7.59). In addition, since El is defined in the vertical
diffusion code, it might impose a rate of evaporation that depletes entirely
the interception layer in one time step. In order to conserve water in the
atmosphere-intercepted water-soil continuum, the mismatch of evaporation
of tile 3 plus dew deposition from the other tiles (which is not explicitely
dealt with by the vertical diffusion) as seen by the vertical diffusion
and the intercepted water has to be fed into the soil.
The equation is solved in three fractional steps: evaporation, dew deposition,
and rainfall interception. The solver provides as outputs
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(a) the inteception layer contents at time step
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(b) Throughfall (ie, rainfall minus intercepted
water); and |
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(c) The evaporation effectively seen by the intercepted
layer in each tile i. |
First, the upward evaporation ( ) contribution is considered; because depends linearly on (see Eq. (7.2)), an implicit version
of the evaporating part of (7.59) is obtained by linearizing
:
where is the new value of interception-reservoir content after the
evaporation process has been taken into account. After solving for , a non-negative value of evaporation
is obtained and the evaporation seen by this fractional time step is calculated
The dew deposition is dealt with explicitely for each non-snow tile in succession,
for tiles 3, 4, 6, 7, 8, where tile 7 is also considered because in the
exposed snow tile, the canopy is in direct evaporative contact with the
atmosphere. When the evaporative flux is downwards ( )
where superscript 2 denotes the final value at the end of the this fractional
time step.
The interception of rainfall is considered by applying the following set
of equations to large-scale and convective rainfall
is a modified convective rainfall flux,
computed by applying the heterogeneity assumption that convective rainfall
only covers a fraction of the grid box, is a coefficient of efficiency of interception of rain. The
total evaporation seen by the interception reservoir is for tiles 4, 6, 7, and 8 and for tile 3.
The interception reservoir model described in this section is probably the
simplest water-conserving formulation based on Rutter's original proposition
(Rutter et al. 1972;
Rutter et al. 1975). For more complicated formulations still
based on the Rutter concept see, for instance, Mahfouf
and Jacquemin (1989),
Dolman and Gregory (1992), and de Ridder (2001).
Integration of Eqs. (7.57) and (7.58) requires the specification
of hydraulic conductivity and diffusivity as a function of soil-water content.
Mahrt and Pan (1984) have compared
several formulations for different soil types. The widely used parametric
relations of Clapp and Hornberger (1978) (see
also Cosby et al.
1984) are adopted:
is a non-dimensional exponent, and are the values of the hydraulic conductivity and matric potential
at saturation, respectively. A minimum value is assumed for and corresponding to permanent wilting-point water content.
Cosby et al.
(1984) tabulate best estimates of , , and , for the 11 soil classes of the US
Department of Agriculture (USDA) soil classification, based on measurements
over large samples. Since the model described here specifies only one soil
type everywhere, and because the determination of the above constants is
not independent of the values of and , the following procedure is adopted.
A comprehensive review of measurements of and may be found in Patterson (1990). Starting from Patterson's
estimates of and for the 11 USDA classes, a mean of the
numbers corresponding to the medium-texture soils (classes 4, 5, 7, and
8, corresponding to silt loam, loam, silty clay loam and clay loam, respectively)
is taken. The resulting numbers are and . Averaging the values of Cosby et al. (1984) for soil
moisture and soil-water conductivity at saturation for the same classes
gives the numerical values and . The Clapp and Hornberger expression for the matric potential
is used with (-15 bar) and (-0.33 bar) (see Hillel 1982; Jacquemin and Noilhan 1990)
to find the remaining constants and . The results are and . The above process ensures a soil that has an availability
corresponding to the average value of medium-texture soils, and yields a
quantitative definite hydraulic meaning to and compatible with the Clapp and Hornberger relations (see Table 7.2 for a summary of the
soil constants).
Finally, the water transport in frozen soil is limited in the case of a
partially frozen soil, by considering the effective hydraulic conductivity
and diffusivity to be a weighted average of the values for total soil water
and a very small value (for convenience, taken as the value of Eq. (7.64) at the permanent wilting
point) for frozen water. The soil properties, as defined above, also imply
a maximum infiltration rate at the surface defined by the maximum downward
diffusion from a saturated surface. If the throughfall exceeds the maximum
infiltration rate, the excess precipitation is put into runoff. However,
in practice the maximum infiltration rate is so large that this condition
is never reached. Surface runoff is therefore only produced if the soil
becomes saturated.
A common soil discretization is chosen for the thermal and water soil balance
for ease of interpretation of the results, proper accounting of the energy
involved in freezing/melting soil water, and simplicity of the code. Equations
Eqs. (7.57) and (7.58) are discretized in
space in a similar way to the temperature equations, ie, soil water and
root extraction defined at full layers, and , and the flux of water at the interface between layer and . The resulting system of equations represents an implicit,
water-conserving method.
For improved accuracy, the hydraulic diffusivity and conductivity are taken
as (see Mahrt and
Pan 1984)
where . The boundary conditions are given by
The difference between throughfall and surface runoff is the soil infiltration at the surface:
and , with a similar equation for . The evaporation at the top of the soil layer, , is computed as the sum of the evaporations of tile 8
plus the contributions necessary to conserve water with the solver of the
interception layer:
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(a) tile 3 mismatch(after the evaporated water
used by the interception reservoir for the given tile is subtracted)
; and |
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(b) when the evaporative fluxes are downward
(i.e., dew deposition), the evaporation for tiles 4, 6 and the canopy
evaporation of tile 7. |
Root extraction is computed as
where the sum over tiles i is done for tiles 4,
6, and 7 (for which only the transpiration is used) and the sum over j
is done over all soil levels. In case of dew deposition (i.e., tile downward
evaporative flux), .
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