Similarities
of WEPP with other Models that might be used for Erosion
Computations
This is Appendix 8 of the WEPP User Requirements
- I. USLE (Universal Soil Loss Equation)
- A. Principal application
- 1. Compute soil loss in conservation planning and inventories
- 2. Compute soil loss to use to estimate yield for offsite sedimentation
and water quality evaluations
- B. Major similarities
- 1. Computes sheet - rill erosion from rainfall
- 2. Computes average annual soil loss from eroding portions of the landscape
- 3. Planning and assessment tool for use by field, state, and national
office agency personnel
- 4. Similar inputs
- C. Major differences
- 1. Model structure
- a. USLE empirical and lumped
- b. WEPP process based
- c. WEPP computes by storm
- 2. Additional computational features of WEPP
- a. Deposition in furrows, on concave slopes, at edges of a landuse change, and
in concentrated
flow channels
- b. Concentrated flow erosion
- c. Grid version of WEPP allows computations over a field
- II. CREAMS (A field scale model for Chemicals, Runoff, and Erosion from Agricultural
Management Systems)
- A. Principal application
- 1. Water quality analyses for field sized areas
- B. Major similarities
- 1. Model structure similar but CREAMS more detailed
- 2. Provide similar hydrologic and erosion estimates
- 3. Both operate on individual storms
- 4. WEPP profile and watershed versions and CREAMS model field
representations
are the same
- C. Major differences
- 1. User environment
- a. CREAMS is not intended for day-to-day field operations
- 2. WEPP does not compute chemical movement
- 3. CREAMS algorithms are more detailed and thus more powerful
- 4. CREAMS uses older technology including SCS curve number runoff
prediction method and USLE factors
(Note: CREAMS is structured so that components can be and are being changed)
- 5. CREAMS is primarily intended to operate as a continuous simulation model
- 6. CREAMS is limited to a single crop in a "field"
- 7. CREAMS has no comparable "grid" model
- III. EPIC (Erosion/Productivity Impact Calculator)
- A. Principal applications
- 1. Calculate the loss of crop yield from erosion
- B. Major similarities
- 1. Model components are similar but EPIC much more detailed except for erosion
component
- 2. Operate on individual storms
- C. Major differences
- 1. Thrusts of models
- a. EPIC emphasizes the impact of erosion on change in soil and its impact on
productivity
- b. Main thrust of WEPP is in its erosion estimates as affected in detail by climate,
soil, topography
and land use
- 2. EPIC is not intended for day-to-day field operations
- 3. EPIC is a continuous simulation model
- 4. EPIC requires more detailed inputs
- 5. EPIC applies to a point on the landscape and thus does not consider sediment
transport,
deposition or concentrated flow erosion
- IV. SWRRB (Simulator for Water Resources in Rural Basins)
- A. Principal applications
- 1. Efficient computation of sediment yield from small to large, complex watersheds
- B. Major similarities
- 1. Model structure of both estimate sediment yield when SWRRB is applied to WEPP
sized areas
- 2. Both operate on individual storms
- 3. Both require similar inputs
- C. Major differences
- 1. Model thrusts
- a. SWRRB mainly is to deal with sediment yield from large, complex watersheds
- b. WEPP deals in detail with erosion and deposition within a field
- 2. Erosion relationships in WEPP are more process based: SWRRB hydrology and erosion
relationships are from
the SCS curve number method and the USLE
- 3. WEPP has very limited routing capability
- 4. WEPP is aimed to a field user
- V. SPUR (Simulation of Production and Utilization of Rangelands)
- A. Principal application
- 1. Evaluation of impact of alternative range management practices
- B. Major similarities
- 1. Model Structure
- 2. Both estimate sediment yield
- 3. Both operate on single storms
- C. Major differences
- 1. Model thrusts
- a. SPUR has an elaborate plant growth model that considers species interaction
and response to
environment but is limited to rangeland
- b. SPUR has an animal and economics component
- c. SPUR is more elaborate and has a complex watershed version
- 2. Erosion relationships in WEPP are more process based
- 3. WEPP is aimed to a field user
- VI. ANSWERS (Areal Nonpoint Source Watershed Environment Response Simulation)
- A. Principal application
- 1. Watershed planning for erosion and sediment yield control on complex watersheds
- 2. Water quality analysis associated with sediment associated chemicals
- B. Major similarities
- 1. Process based
- 2. Event based
- 3. Grid topography representation
- C. Major differences
- 1. ANSWERS is primarily limited to single storm
- 2. ANSWERS has limited capability for concentrated flow erosion
- 3. ANSWERS is a fully dynamic model
- VII. AGNPS - field scale version (Agricultural Nonpoint Source Pollution
Model)
- A. Principal application
- 1. Analysis of nonpoint source pollution from agricultural fields
- B. Major similarities
- 1. Grid based topographic representation
- 2. Process and hydrologically driven
- 3. Considers multiple particle classes
- C. Major differences
- 1. AGNPS relies on older hydrologic and erosion prediction technology
- 2. AGNPS has limited capabilities for estimating concentrated flow erosion
- VIII. SEDIMOT II (SEdimentology by DIstributed MOdel Treatment)
- A. Principal application
- 1. Design of sediment control structure on surface mined land
- B. Major similarities
- 1. Process and hydrologically driven
- 2. Considers multiple particle classes
- C. Major differences
- 1. Single event model
- 2. One option uses older hydrologic (SCS curve number) and erosion (USLE)
prediction technology
- 3. Provide a more detailed analysis of impoundments and other such sediment
control structures

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