SPHY Manual - All versions
  • 📚Readme
  • manual
    • SPHY manual 3.1
      • Introduction
      • Theory
        • Background
        • Modules
        • Reference and potential evaporation
        • Dynamic vegetation processes
        • Snow processes
        • Glacier processes
        • Soil water processes
        • Soil erosion processes
        • Routing
      • Applications
        • Irrigation management in lowland areas
        • Snow- and glacier-fed river basins
        • Flow forecasting
        • Soil erosion and sediment transport
      • Installation of SPHY
        • Installing SPHY as a stand-alone application
          • Miniconda
          • SPHY v3.1 source code
      • Build your own SPHY-model
        • Select projection extent and resolution
        • Clone map
        • DEM and Slope
        • Delineate catchment and create local drain direction map
        • Preparing stations map and sub-basin.map
        • Glacier table
        • Soil hydraulic properties
        • Other static input maps
        • Meteorological forcing map series
        • Open water evaporation
        • Dynamic vegetation module
        • Soil erosion model input
          • MMF
          • Soil erosion model calibration
          • Soil erosion model output
        • Sediment transport
      • Reporting and other utilities
        • Reporting
        • NetCDF
      • References
      • Copyright
      • Appendix 1: Input and Output
      • Appendix 2: Input and Output description
      • Appendix 3: Soil erosion model input
        • MUSLE
        • INCA
        • SHETRAN
        • DHVSM
        • HSFP
    • SPHY manual 3.0
      • Introduction
      • Theory
        • Background
        • Modules
        • Reference and potential evaporation
        • Dynamic vegetation processes
        • Snow processes
        • Glacier processes
        • Soil water processes
        • Soil erosion processes
        • Routing
      • Applications
        • Irrigation management in lowland areas
        • Snow- and glacier-fed river basins
        • Flow forecasting
      • Installation of SPHY
        • General
        • Installing SPHY as a stand-alone application
          • Miniconda
          • SPHY v3.1 source code
      • Build your own SPHY-model
        • Select projection extent and resolution
        • Clone map
        • DEM and Slope
        • Delineate catchment and create local drain direction map
        • Preparing stations map and sub-basin.map
        • Glacier fraction map
        • Soil hydraulic properties
        • Other static input maps
        • Meteorological forcing map series
        • Open water evaporation
        • Dynamic vegetation module
        • Soil erosion model input
          • MUSLE
          • MMF
          • INCA
          • SHETRAN
          • DHVSM
          • HSFP
          • Soil erosion model calibration
          • Soil erosion model output
        • Sediment transport
        • Applications
        • Reporting
        • NetCDF
      • References
      • Copyright
      • Appendix 1: Input and Output
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  1. manual
  2. SPHY manual 3.0
  3. Build your own SPHY-model
  4. Soil erosion model input

SHETRAN

The SHETRAN soil erosion model requires the following land use specific model parameters (shetran_table):

Table 21: Shetran_table

Land use class

Leaf drip diameter (dl)

Leaf drip distance (X)

Ground cover (Cg)

Canopy cover (Cc)

Manning (n)

No erosion

-99

1

2

3

4

5

6

1

0.005

10

0.65

0.85

0.2

0

2

0.004

0.5

0.35

0.6

0.1

0

3

0.006

0.3

0.3

0.35

0.05

0

…

…

…

…

…

…

…

The leaf drip diameter should be specified per land use class, with a typical value of around 0.005 m. See Table 4.2 of (Wicks, 1988) for values per land use class. The leaf drip distance is similar to the plant height used in the other models. The same holds for ground and canopy cover, for which the latter is ignored in case the vegetation module is used. Table 4.2 of Wicks (1988) gives also suggestions for these model parameters. The Manning’s roughness should be specified for all land use classes. The “no erosion” (0 or 1) column prevents erosion from happening, for instance for water and paved land use classes.

The raindrop impact soil erodibility coefficient kr is typically between 0.1-70 J-1, while the overland flow soil erodibility coefficient kf is typically between 0.5-20 ∙ 10-6 kg m-2 s-1.

The flow and sediment density can be assumed to be 1100 and 2650 kg m-3, respectively.

The particle diameter of the three textural classes should be provided, which can be assumed similar to the values provided by Morgan & Duzant (2008) for the MMF model.

The median grain size D50 can be provided, but when left empty, the median grain size will be estimated from the particle diameter and texture maps.

The width-to-depth ratio is used to determine the size of the rills, for the calculation of the flow velocity. Typical values range from 1-3.

The immediate deposition is determined using a transport capacity equation, for which two options are available, i.e. (1) Yalin (1963) and (2) Engelund & Hansen (1967).

Table 22: Model parameters

Model parameter

Model variable

Unit

Range/default

Leaf drip diameter

dl

m

0.003-0.007

Leaf drip distance

X

m

0-50

Ground cover

Cg

-

0-1

Canopy cover

Cc

-

0-1

Manning

n

s m-1/3

0.01-0.5

No erosion

-

0 or 1

Raindrop impact soil erodibility coefficient

kr

J-1

0.1-70

Overland flow soil erodibility coefficient

kf

kg m-2 s-1

0.5-20 ∙ 10-6

Flow density

ρ

kg m-3

1100

Sediment density

ρs

kg m-3

2650

Particle diameter

δc, δz, δs,

m

2 ∙ 10-6, 60 ∙ 10-6, 200 ∙ 10-6

Median grain size

D50

µm

1-2000

Width-to-depth ratio

WD

-

1-3

Capacity equation

1 or 2

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Last updated 1 year ago