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Home > Research > Ifsdocs > PHYSICS >  
   

Chapter 7. Land surface parametrization

IFS documentation Front Page


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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7.6 Soil-water budget




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 :

 
(7.57)
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:

 
(7.58)
( ) 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.


7.6.1 Interception




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

 
(7.59)
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
(a)   the inteception layer contents at time step ;
(b)   Throughfall (ie, rainfall minus intercepted water); and
(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 :

 
(7.60)
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

 
(7.61)


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 ( )

 
(7.62)


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

 
(7.63)
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).


7.6.2 Soil properties




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:

 
(7.64)
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

 
(7.65)
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.


7.6.3 Discretization and the root profile




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)

 
(7.66)


where . The boundary conditions are given by

 
(7.67)
The difference between throughfall and surface runoff is the soil infiltration at the surface:

 
(7.68)


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:
(a)   tile 3 mismatch(after the evaporated water used by the interception reservoir for the given tile is subtracted) ; and
(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

 
(7.69)
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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