EcoService Models Library (ESML)
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Compare EMs
Which comparison is best for me?EM Variables by Variable Role
One quick way to compare ecological models (EMs) is by comparing their variables. Predictor variables show what kinds of influences a model is able to account for, and what kinds of data it requires. Response variables show what information a model is capable of estimating.
This first comparison shows the names (and units) of each EM’s variables, side-by-side, sorted by variable role. Variable roles in ESML are as follows:
- Predictor Variables
- Time- or Space-Varying Variables
- Constants and Parameters
- Intermediate (Computed) Variables
- Response Variables
- Computed Response Variables
- Measured Response Variables
EM Variables by Category
A second way to use variables to compare EMs is by focusing on the kind of information each variable represents. The top-level categories in the ESML Variable Classification Hierarchy are as follows:
- Policy Regarding Use or Management of Ecosystem Resources
- Land Surface (or Water Body Bed) Cover, Use or Substrate
- Human Demographic Data
- Human-Produced Stressor or Enhancer of Ecosystem Goods and Services Production
- Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services
- Non-monetary Indicators of Human Demand, Use or Benefit of Ecosystem Goods and Services
- Monetary Values
Besides understanding model similarities, sorting the variables for each EM by these 7 categories makes it easier to see if the compared models can be linked using similar variables. For example, if one model estimates an ecosystem attribute (in Category 5), such as water clarity, as a response variable, and a second model uses a similar attribute (also in Category 5) as a predictor of recreational use, the two models can potentially be used in tandem. This comparison makes it easier to spot potential model linkages.
All EM Descriptors
This selection allows a more detailed comparison of EMs by model characteristics other than their variables. The 50-or-so EM descriptors for each model are presented, side-by-side, in the following categories:
- EM Identity and Description
- EM Modeling Approach
- EM Locations, Environments, Ecology
- EM Ecosystem Goods and Services (EGS) potentially modeled, by classification system
EM Descriptors by Modeling Concepts
This feature guides the user through the use of the following seven concepts for comparing and selecting EMs:
- Conceptual Model
- Modeling Objective
- Modeling Context
- Potential for Model Linkage
- Feasibility of Model Use
- Model Certainty
- Model Structural Information
Though presented separately, these concepts are interdependent, and information presented under one concept may have relevance to other concepts as well.
EM Identity and Description
EM ID
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EM-131 | EM-417 |
EM-632 ![]() |
EM Short Name
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InVEST marine water quality, Hood Canal, WA, USA | SWAT, Guanica Bay, Puerto Rico, USA | Waterfowl pairs, CREP wetlands, Iowa, USA |
EM Full Name
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InVEST (Integrated Valuation of Envl. Services and Tradeoffs) marine water quality, Hood Canal, WA, USA | SWAT (Soil and Water Assessment Tool) Guánica Bay, Puerto Rico, USA | Waterfowl pairs, CREP (Conservation Reserve Enhancement Program) wetlands, Iowa, USA |
EM Source or Collection
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InVEST | US EPA | None |
EM Source Document ID
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205 | 334 | 372 |
Document Author
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Toft, J. E., Burke, J. L., Carey, M. P., Kim, C. K., Marsik, M., Sutherland, D. A., Arkema, K. K., Guerry, A. D., Levin, P. S., Minello, T. J., Plummer, M., Ruckelshaus, M. H., and Townsend, H. M. | Hu, W. and Y. Yuan | Otis, D. L., W. G. Crumpton, D. Green, A. K. Loan-Wilsey, R. L. McNeely, K. L. Kane, R. Johnson, T. Cooper, and M. Vandever |
Document Year
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2013 | 2013 | 2010 |
Document Title
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From mountains to sound: modelling the sensitivity of dungeness crab and Pacific oyster to land–sea interactions in Hood Canal,WA | Evaluation of Soil Erosion and Sediment Yield for the Ridge Watersheds in the Guanica Bay Watershed, Puerto Rico, Using the SWAT Model | Assessment of environmental services of CREP wetlands in Iowa and the midwestern corn belt |
Document Status
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Peer reviewed and published | Peer reviewed and published | Peer reviewed and published |
Comments on Status
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Published journal manuscript | Published EPA report | Published report |
EM ID
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EM-131 | EM-417 |
EM-632 ![]() |
https://www.naturalcapitalproject.org/invest/ | Not applicable | Not applicable | |
Contact Name
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J.E. Toft | Yongping Yuan | David Otis |
Contact Address
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Not reported | USEPA, ORD, NERL, Environmental sciences Division, Las Vegas, Nevada | U.S. Geological Survey, Iowa Cooperative Fish and Wildlife Research Unit, Iowa State University |
Contact Email
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jetoft@stanford.edu | Yuan.Yongping@epa.gov | dotis@iastate.edu |
EM ID
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EM-131 | EM-417 |
EM-632 ![]() |
Summary Description
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Marine Water Quality Model. Please note: This ESML entry describes a specific, published application of an InVEST model. Different versions (e.g. different tiers) or more recent versions of this model may be available at the InVEST website. AUTHOR'S DESCRIPTION: "We used outputs from the freshwater models as inputs to the marine water quality model.We adapted a box model that has been successfully applied in Puget Sound (Babson et al., 2006; Sutherland et al., 2011) to simulate seasonal and interannual variations in salinity, water temperature, and nitrates in the Canal." (p. 4) | AUTHOR'S DESCRIPTION: " SWAT is a physically-based continuous watershed simulation model that operates on a daily time step. It is designed for long-term simulations. The U.S. Department of Agriculture-Agriculture Research Station (USDA-ARS) Grassland, Soil and Water Research Laboratory in Temple, Texas created SWAT in the early 1990s. It has undergone continual review and expansion of capabilities since it was created (Arnold et al., 1998; Neitsch, et al., 2011a and b). This model has the ability to predict changes in water, sediment, nutrient and pesticide loads with respect to the different management conditions in watershed. Major components of the SWAT model include hydrology, weather, erosion, soil temperature, crop growth, nutrients, pesticides and agricultural management practices (Neitsch et al., 2011b). SWAT subdivides a watershed into multiple sub-watersheds, and the subwatersheds are further divided into Hydrologic Response Units (HRUs) that consist of homogeneous land use, soils, slope, and management (Gassman et al., 2007; Neitsch, et al., 2011b; Williams et al., 2008). | ABSTRACT: "This final project report is a compendium of 3 previously submitted progress reports and a 4th report for work accomplished from August – December, 2009. Our initial primary objective (Progress Report I) was prediction of environmental services provided by the 27 Iowa Conservation Reserve Enhancement Program (CREP) wetland sites that had been completed by 2007 in the Prairie Pothole Region of northcentral Iowa. The sites contain 102.4 ha of wetlands and 377.4 ha of associated grassland buffers... With respect to wildlife habitat value, USFWS models predicted that the 27 wetlands would provide habitat for 136 pairs of 6 species of ducks, 48 pairs of Canada Geese, and 839 individuals of 5 grassland songbird species of special concern..." AUTHOR'S DESCRIPTION: "Number of duck pairs per site was estimated for 6 species of ducks: Mallard (Anas platyrhynchos), Blue-winged Teal (Anas discors), Northern Shoveler (Anas clypeata), Gadwall (Anas strepera), Northern Pintail (Anas acuta), and Wood Duck (Aix sponsa), using models developed by Cowardin et al. (1995). Pair abundance was based on wetland class (i.e., temporary, seasonal, semi-permanent, lake, or river), wetland size, and a set of species specific regression coefficients. All CREP wetlands were considered semi-permanent for this analysis; therefore only coefficients associated with the semipermanent wetland pair model were used in calculations. The general equation used to estimate the pairs per wetland was: Pairs = e (a + bx + α) * p where, e = mathematical constant ≈ 2.718, a = species specific regression coefficient a, b = species specific regression coefficient b, x = the natural log of wetland size, α = species specific alpha value, and p = proportion of the basin containing water (assumed to be 0.90 for this analysis)" |
Specific Policy or Decision Context Cited
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Land use change | None Identified | None identified |
Biophysical Context
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No additional description provided | Need to fill in | Prairie pothole region of north-central Iowa |
EM Scenario Drivers
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future land use and land cover; Climate change | Planting type, fertilizing rate, harvest rate | No scenarios presented |
EM ID
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EM-131 | EM-417 |
EM-632 ![]() |
Method Only, Application of Method or Model Run
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Method + Application (multiple runs exist) | Method + Application | Method + Application (multiple runs exist) View EM Runs |
New or Pre-existing EM?
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Application of existing model | New or revised model | New or revised model |
Related EMs (for example, other versions or derivations of this EM) described in ESML
EM ID
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EM-131 | EM-417 |
EM-632 ![]() |
Document ID for related EM
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None | None | None |
EM ID for related EM
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None | None | EM-705 | EM-703 | EM-702 | EM-701 | EM-700 |
EM Modeling Approach
EM ID
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EM-131 | EM-417 |
EM-632 ![]() |
EM Temporal Extent
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varies by run, see runs for values | 1981-2004 | 2002-2007 |
EM Time Dependence
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time-stationary | time-dependent | time-stationary |
EM Time Reference (Future/Past)
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Not applicable | future time | Not applicable |
EM Time Continuity
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Not applicable | discrete | Not applicable |
EM Temporal Grain Size Value
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Not applicable | 1 | Not applicable |
EM Temporal Grain Size Unit
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Not applicable | Day | Not applicable |
EM ID
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EM-131 | EM-417 |
EM-632 ![]() |
Bounding Type
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Physiographic or ecological | Watershed/Catchment/HUC | Multiple unrelated locations (e.g., meta-analysis) |
Spatial Extent Name
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Hood Canal | Guanica Bay, Puerto Rico watersheds | CREP (Conservation Reserve Enhancement Program) wetland sites |
Spatial Extent Area (Magnitude)
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100-1000 km^2 | 100-1000 km^2 | 1-10 km^2 |
EM ID
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EM-131 | EM-417 |
EM-632 ![]() |
EM Spatial Distribution
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spatially distributed (in at least some cases) | spatially distributed (in at least some cases) | spatially distributed (in at least some cases) |
Spatial Grain Type
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other (specify), for irregular (e.g., stream reach, lake basin) | area, for pixel or radial feature | other (specify), for irregular (e.g., stream reach, lake basin) |
Spatial Grain Size
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Not reported | 30m x 30m | multiple, individual, irregular shaped sites |
EM ID
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EM-131 | EM-417 |
EM-632 ![]() |
EM Computational Approach
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Analytic | Numeric | Analytic |
EM Determinism
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deterministic | deterministic | deterministic |
Statistical Estimation of EM
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EM ID
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EM-131 | EM-417 |
EM-632 ![]() |
Model Calibration Reported?
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No |
Yes ?Comment:Used 1981 and 1982 data to calibrate hydrology. |
Unclear |
Model Goodness of Fit Reported?
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No |
No ?Comment:Calibration for both the stream flow and Sediment concentration of the mode |
No |
Goodness of Fit (metric| value | unit)
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None |
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None |
Model Operational Validation Reported?
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No |
Yes ?Comment:Validation with 1983-1984 data from USGS. Used streamflow and water quality data from two stations |
Unclear |
Model Uncertainty Analysis Reported?
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No | Unclear | No |
Model Sensitivity Analysis Reported?
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No |
Yes ?Comment:Yes for both runoff and sediment |
No |
Model Sensitivity Analysis Include Interactions?
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Not applicable | No | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
EM-131 | EM-417 |
EM-632 ![]() |
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Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
EM-131 | EM-417 |
EM-632 ![]() |
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None | None |
Centroid Lat/Long (Decimal Degree)
EM ID
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EM-131 | EM-417 |
EM-632 ![]() |
Centroid Latitude
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47.8 | 18.19 | 42.62 |
Centroid Longitude
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-122.7 | -66.76 | -93.84 |
Centroid Datum
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NAD83 | WGS84 | WGS84 |
Centroid Coordinates Status
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Estimated | Estimated | Estimated |
EM ID
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EM-131 | EM-417 |
EM-632 ![]() |
EM Environmental Sub-Class
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Near Coastal Marine and Estuarine | Terrestrial Environment (sub-classes not fully specified) | Inland Wetlands | Agroecosystems | Grasslands |
Specific Environment Type
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glacier-carver saltwater fjord | watershed | Wetlands buffered by grassland set in agricultural land |
EM Ecological Scale
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Ecological scale is finer than that of the Environmental Sub-class | Ecological scale is finer than that of the Environmental Sub-class | Ecological scale corresponds to the Environmental Sub-class |
Scale of differentiation of organisms modeled
EM ID
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EM-131 | EM-417 |
EM-632 ![]() |
EM Organismal Scale
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Not applicable | Not applicable | Species |
Taxonomic level and name of organisms or groups identified
EM-131 | EM-417 |
EM-632 ![]() |
None Available | None Available |
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EnviroAtlas URL
EM Ecosystem Goods and Services (EGS) potentially modeled, by classification system
CICES v 4.3 - Common International Classification of Ecosystem Services (Section > Division > Group > Class)
EM-131 | EM-417 |
EM-632 ![]() |
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<a target="_blank" rel="noopener noreferrer" href="https://www.epa.gov/eco-research/national-ecosystem-services-classification-system-nescs-plus">National Ecosystem Services Classification System (NESCS) Plus</a>
(Environmental Subclass > Ecological End-Product (EEP) > EEP Subclass > EEP Modifier)
EM-131 | EM-417 |
EM-632 ![]() |
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None |
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