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Plugin was written by Andrew Freebairn, it is based on Scott Wilkinson's et al paper "Development of a time-stepping sediment budget model for assessing land use impacts in large river basins".  It also borrows from the Dynamic SedNet plugin developed at DERM by Robin Ellis (Unlicensed) and Ross Searle (Unlicensed) (now at CSIRO).

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S.N. Wilkinson, C. Dougall, A.E. Kinsey-Henderson, R. Searle, R. Ellis, R. Bartley
Development of a time-stepping sediment budget model for assessing land use impacts in large river basins
Sci Total Environ, 468–469 (2014), pp. 1210–1224: http://www.sciencedirect.com/science/article/pii/S0048969713008176

LT Cetin, A Freebairn, S Easton, M Sands, P Pedruco
Application of daily SedNet for modelling catchment-scale sediment generation and transport: New Zealand case study
37th Hydrology & Water Resources Symposium 2016:  Water, Infrastructure and the Environmenthttps://search.informit.com.au/documentSummary;dn=683996186142861;res=IELENG

A Freebairn, N Fleming, L van der Linden, Y He, SM Cuddy, J Cox, R Bridgart
Extending the water quality modelling capability within eWater Source–developing the dSedNET plugin
Goyder Institute for Water Research Technical Report Serieshttp://www.goyderinstitute.org/_r425/media/system/attrib/file/397/15~42_WQ_dSedNETReport_RAC.pdf

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  1. Load the “dSedNet” plug-in using the 'Plugin Manager'
  2. Use the dSednetDerivedLayers to derive useful data.  This tool removes the need to have a DEM saved within the project file.  It also generates many of the spatial parameter layers used to parameterise the dSednet models and to construct the base scenario.  Inputs required are, a hydrologically sound DEM, stream threshold (50km^2 is default), the easting and northing of the outlet cell (if one is not given all outlets will be produced at the edge of the data provided) and the file path to save results.
  3. Define a Source Catchments scenario using the “Geographic Wizard”.  When defining the 'Network' use the option to 'Draw Network' and use the layers generated from the above process. 
  4. Define FU areas with the use of a land-use map (raster) which covers 100% of the catchment (This is a prerequisite for using the Spatial Parameteriser)
  5. Select a rainfall runoff model and assign parameters/calibrate it
  6. Define constituents (e.g. “Fine” and “Coarse”).
    1. You may need to define multiple sources of constituents for a given functional unit (e.g. Hill slope and Gully)
  7. Assign models for constituent generation -  (“Hillslope Model – dSedNet” and “Gully Model - dSedNet”) and enter static model parameters
  8. Assign spatial parameters to selected constituent generation models using the Spatial Parameterisation tool.
  9. Execute the temporal parameterisers for associated constituent generation models

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ParameterDescriptionSource
USLE HSDR - FineHill sediment delivery ratioDefault 0.1 (Prosser et al, 2001)
Rrainfall erosivity factorInternally calculated based on rainfall for the given timestep and uses Yang and Yu (1987) method
KLSCSoil erodibility factor, slope length, steepness factor and cover factor (static)

K - Soil erodability (Wischmeier and Smith (1978))

L - Slope length (default, 1)

S - Steepness raster generated by dSednetDerivedLayers for steepness factor

C - Cover factor (Rosewell, 1993)

KLSCdynamicSoil erodibility factor, slope length, steepness factor and cover factor Where C is played as a time series to capture the temporal variance of vegetation cover. Perform raster operations, where static KLS are multiplied together to for a single KLS raster. Then for each daily C layer multiple with the KLS raster to produce a daily layers for KLSC. Use the spatial parameteriser the model, using t
Smean summer rainfallInternally calculated by the temporal parameterisation
Pmean annual rainfallInternally calculated by the temporal parameterisation
R Factor Rainfall ThresholdR rainfall threshold12.7 mm (If daily rainfall is less than this threshold then the R value is set to 0)
AlphaRainfall erosivity factor used to calculate RCalculated at runtime based upon S and P
BetaRainfall erosivity factor used to calculate R Default values are set - 1.49, or use the Beta raster generated by dSednetDerivedLayers which uses Yang and Yu (1987) method
Etarainfall erosivity factor used to calculate R Default, 0.389 (Yang and Yu, 1987) method
DWCDry Weather Concentration User defined from literature
Off set from day of yearNumber of days that are subtracted from the current day of yearDefault, 15
Daily RainRainfall that fell on a single 24hrs measured in mmThis will be assigned at runtime by the system.  It is obtained from the rainfall runoff model for the associated FU

R is based on Yang et al (2015) - Yang Xihua, Yu Bofu (2015) Modelling and mapping rainfall erosivity in New South Wales, Australia. Soil Research 53, 178-189.

Beta base on on Yang et al (2015) - Yang Xihua, Yu Bofu (2015) Modelling and mapping rainfall erosivity in New South Wales, Australia. Soil Research 53, 178-189.

The parameter KLSC (static) (or KLSCdynamic, dynamic) can be provided to the model in a number of different ways.

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ParameterDescriptionSource
Link SlopeAverage channel slope (m/m)use the Reach slope raster generated by dSednetDerivedLayers)
Link LengthLength of main channel (m)use the Reach length raster generated by dSednetDerivedLayers)
Link WidthWidth of main channel (m)yCurrently not used
Link DepthChannel DepthCurrently not used
Bank HeightBank HeightObservations
Channel RoughnessChannel roughnessMannings N value
Riparian Vegetation PercentageRiparian Vegetation PercentageObservations
Bank Full FlowThe flow when the stream is full to the top of the bankInternally calculated by the temporal parameterisation
Bank Full Flow Annual Recurrence IntervalAnnual Recurrence Interval of the flow when the stream is full to the top of the bankUser defined from literature
Max Riparian Vegetation EffectivenessRiparian Vegetation Percentage - EffectivenessUser defined from literature
Soil ErodibilitySoil Erodibility %Input layer - spatial parameterisation
Erosion Coefficient Adjusted for long-term rates of bank retreat as observed (0.00001)Observations
Soil Percent Fine ParticlesSoil Percent Fine Particles %Input layer - spatial parameterisation
Sediment Bulk DensityThe weight (tonnes) of 1m3 of sedimentInput layer - spatial parameterisation
Long Term Average Daily FlowLong Term Average Daily Flow raised to the Daily Flow Power FactorInternally calculated by the temporal parameterisation
Daily Flow Power FactorUsed to manually fit data of bank erosion ratesDefault to 1.4

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