2D Infiltration Model
The 2D Infiltration Model calculates the infiltration properties in 2D elements of a 2D mesh.
The areas in the network to which infiltration is to be applied are represented either by an entire 2D Zone or by Infiltration Zone (2D) objects set up by the user.
The infiltration characteristics for specific surface types are defined in Infiltration Surface (2D) objects. Infiltration properties are assigned to a 2D Zone or Infiltration Zone by associating an Infiltration Surface with the zone.
The volume infiltrated in the 2D surface can, if required, be connected to a node, single or multiple links, or a subcatchment in the 1D system using a Permeable Zone (2D) object.
Infiltration Models
An infiltration model is selected for each Infiltration Surface (2D) object. The infiltration models currently available are Green-Ampt and:
The effective infiltration rate is calculated as described below.
The maximum theoretical infiltration IMAX is given by the function of the infiltration loss coefficient:
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where: IMAX = maximum theoretical infiltration (mm) ILC = infiltration loss coefficient Dt = timestep (hr) |
If the available water volume in the surface is higher than the maximum infiltration, the soil will be saturated and the effective infiltration will be given by:
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where: IE = effective infiltration (mm/hr) ILC = infiltration loss coefficient i - rainfall intensity (mm/hr) |
If the available water volume in the surface is lower than the maximum infiltration, the effective infiltration will be given by:
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where: IE = effective infiltration (mm/hr) AWV = available water volume Dt = timestep (hr) |
A fixed percentage of the net rainfall which becomes runoff is defined.
The effective infiltration rate is calculated using the following:
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where: IE = effective infiltration (mm/hr) i - rainfall intensity (mm/hr) |
Infiltration either on pervious surfaces or on semi-pervious surfaces can be directly modelled using a variant of the Horton equation. This is an empirical formula derived from infiltrometer/small catchment studies and is usually expressed as a function of time:
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where: ¦ is the potential infiltration rate (mm/hr) ¦0 is the initial infiltration rate (soil water content is zero) (mm/hr) ¦c is the final (limiting) infiltration rate (soil is saturated) (mm/hr) kdecay is an exponent governing the rate of decay of the potential infiltration rate (1/hr) t is equivalent infiltration time |
Equation 1 is used to evaluate the change in infiltration when there is effective infiltration range, (i.e. whenever there is some water in the surface). The soil becomes more saturated as more water is infiltrated and the infiltration capacity reduces with time.
To evaluate the change in potential infiltration rate during a time step in a mesh element, the maximum potential infiltration volume is calculated as the integral of the potential infiltration rate curve over the time interval (t2-t1=dt):
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where: F is the maximum potential infiltration volume (mm) t* is the initial equivalent infiltration time of the soil |
The equivalent infiltration time, t*, will be different for each mesh element, and in effect represents the soil saturation state. For example, when the equivalent infiltration time of an element is zero, the soil is considered completely dry and therefore the potential infiltration rate will be at its maximum level.
If the available water in the surface is higher than the maximum potential infiltration rate, F, the new potential infiltration rate will decay from:
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to:
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If the available water in the surface is lower than the maximum potential infiltration rate, F, the potential infiltration rate, f, of the soil at the end of the time step will be calculated based on the soil moisture content.
The soil water content is a quantity given by the balance of the infiltration volume and the drainage volume of the soil. Therefore, the variation in soil water content is given by:
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where: DS is change in soil moisture content (mm) Vi is infiltration volume (mm) Vd is drainage volume (mm) |
The drainage capacity of the soil is given by the following function of the infiltration equivalent time:
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where: d is drainage capacity (mm/hr) |
Therefore, for a given equivalent infiltration time, the soil moisture content, S, can be defined as the integral of the difference between the potential infiltration rate and the drainage capacity of the soil, d:
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The soil water content, S, will reach its maximum value as the equivalent infiltration time tends to infinity. In that situation, the potential infiltration rate, f, equals the discharge capacity, d, and the net contribution to S is null. The maximum value of S is given by:
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To calculate the new potential infiltration rate, f, if the available water in the surface is lower than the maximum potential infiltration volume,. F, the procedure is as follows:
- Calculate the increment of S:
- From the new value of S, the new value of equivalent infiltration time, t can be obtained from the formula:
- From the new value of t, the new potential infiltration rate will be given by:
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where: Vs is volume in surface (mm) Vd is given by the integral of the drainage curve over the time interval (dt=t2-t2):
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where: t is equivalent infiltration time (h) |
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Once an element becomes dry, i.e. there is no water volume available in the surface to infiltrate, the soil will start drying up. The drying process is governed by the recovery rate krecovery.
In this situation, the change in potential infiltration rate in a time step (dt=t2-t1) will be governed by the change in S.
The change in S will be governed by the drainage volume, as there is no infiltration volume:
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where: Vd is the drainage volume (mm) given by:
where: St1 is the soil water content at time t1 (mm) ¦c is the final (limiting) infiltration rate (soil is saturated) (mm/hr) ¦0 is the initial infiltration rate (soil water content is zero) (mm/hr) krecovery is an exponent governing the rate of recovery of the potential infiltration rate (1/hr) dt is the timestep (hr) |
The new potential infiltration rate will be obtained following the procedure shown above in steps 2 and 3.
Setting initial soil water content percentage
When using the Horton infiltration model, it is possible to set an initial soil water content percentage for the entire 2D Zone or for specific areas in the network by the use of Infiltration Initial Condition (IC) Zones.
The initial soil water content values for specific zones are defined in the Initial Conditions 2D grid. Soil water content values between 0 and 100 can be specified, where 0 represents dry initial condition, and 100 represents saturated initial condition.
Setting initial moisture deficit percentage
When using the Green-Ampt infiltration model for 2D simulations, it is possible to set the initial moisture deficit (i.e. the difference between soil porosity and actual moisture content) percentage for the entire 2D Zone or for specific areas in the network by the using Infiltration Initial Condition (IC) Zones. The initial soil moisture deficit values for specific zones are defined in the Initial Conditions 2D grid. Moisture deficit values between 0 and 100 can be specified, where 0 represents a saturated initial condition, and 100 represents a dry initial condition.
2D Infiltration Results
When an infiltration surface is associated with a 2D zone, or with an Infiltration Zone overlapping the 2D zone, additional 2D Zone Results Data Fields will become available:
- Cumulative infiltration
- Effective infiltration (derived from the cumulative infiltration result)
- Potential infiltration (only displayed when using Horton infiltration model)
- Soil water content percentage (only displayed when using Horton infiltration model)
- Soil moisture deficit percentage (only displayed when using the Green-Ampt infiltration model)
- Moisture content of the upper zone (only displayed when using the Green-Ampt infiltration model)
- Time needed to drain the upper zone (only displayed when using the Green-Ampt infiltration model)
- Saturation flag (only displayed when using the Green-Ampt infiltration model)