Landscape soil erosion modeling for spatial conservation planning: GIS-based tutorial

Prepared by Helena Mitasova, GMSL UofI, MEAS NCSU, Bill Brown GMSL UofI

1. Introduction

purpose, goal

2. Multiple scale approach

 2.1 Look-up table for multiple scale approach

Designed for  quick access to the relevant parts of the tutorial the table will have links to the topics/documents needed to fulfill the given task  (change the order to tasks, data,models)
 

Scale / unit
FIGURE - installation region  FIG lanscape/watershed FIG subwatershed/field 
Data Spatially averaged
  • existing and planned use at hydrologic units level
  • polygon/vector data or 100-30m resolution
Distributed
  • low resolution grid 
Distributed
  • existing and planned use at grid level
  • 10-20m resolution data or detailed polygons

 
 
 
Distributed
  • existing and planned use including manmade features
  • 1-2m resolution raster + linear features/borderlines

 
 

Tasks
  • identification of high risk subwatersheds requiring detailed analysis and installation of measures
  • identification of large conservation areas
  •  hot spots in watersheds
  • prevailing erosion deposition pattern for given land use
  • location of conservation measures (dense vegetation, stream buffers, sedimentation ponds/constructed wetlands)
  • detailed erosion, deposition pattern including the effects of conservation measures
  • detailed impact of erosion on roads
  • design of measures 
Models  Spatially averaged
  • SWAT
  • Distributed
  • RUSLE3D (simplified)
Distributed 
  • RUSLE3d
  • USPED
  • SIMWE
Distributed
  • RUSLE3d
  • USPED
  • SIMWE

 

2.2 Theory and algorithms used in the models

3. Runing the analysis in GIS

4. Notes on preparation of data

The data needed for erosion modeling are often already available from other projects and mapping efforts. Then simple checks of their suitability is sufficient and the methods outlined above can be directly applied. However, in some cases further processing of data is needed to extract the necessary parameters with sufficient accuracy and realism. It is impossible to address all issues that can arise so the focus of the next sections will be on the most common problems and approaches to solution.
 

4.1 Digital elevation model


4.2 Land use/land cover
 


sources, resolution, level of detail - broad categories at 20-30m resolution, %vegetation cover for design at sites (1m resolution)

4.3 Soils
 


4.4 Rainfall

Rainfall - R-factor - annual, monthly, storm
 

5. Notes on running the models

6. Notes on creating and analyzing the resulting maps

  • 6.1 Continuous value maps - what they mean, legend, color tables (automatic creation of exponential legend with intesity given by parameter p=0.01, colors see Cebecauer/GRASScurvatures for erosion/deposition)
  • 6.2 Class maps - reclassifying the continuous maps, standardized classes
  • 6.3 Sumary statistics, reports:
  • histograms,
  • %area from each class,
  • average rate,
  • total soil detached, total net soil loss, ...
  • 7. Notes on applications for planning


    Change laduse/implement conservation measure,...- installation wide, sub-installation-landscape scale

    Minimize detachment and net erosion:
    a)model based: set max detachment treshold - create new cover, (necessary C, suggested cover invertly derived from the table), set max net erosion treshold, set elimination of concentrated flow and other criteria
    b)feature based: set buffers along the streams (uniform with given width, adjusted by model,..), set hedge along contour, grass filter strip, conservation area - compute necessary C and adjust shape,

    applications manual: sequence of commands to find roads affected by high erosion risk wetland areas affected by high erosion
     
     

    Deposit sediment: increase sedimentation rate in deposition area, create sedimentation pond, ....
    Notes - for the management purposes there seems to be a need for categorization/classification - first streams, land are split into discrete homogeneous units and then they are classified/zoned for what we can do with them - is this the most effective approach??? (this results in uniform buffers, interactions between various landscape phenomena such as streams/topography ignored, etc. this also results in such observations that we have more sediment coming from the forested watershed that from agricultural/developed one.
     

    Link-in the following material (some need modifications)

    - USLE, USPED on-line tutorials
    - GRASSBook erosion modeling
    - preparation of data from reports and grassbook
    - processing of results from grassbook and reports

    Notes/questions

    Standardized filed names (e.g. used in ATTAC document) - is there any official list for that?
    Standardized categories for erosion rates severe/high/moderate/low/stable
    Standardized color tables for inputs and outputs