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
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EM ID
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EM-492 |
EM-729 |
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EM Short Name
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EnviroAtlas - Restorable wetlands | WESP: Urban Stormwater Treatment, ID, USA |
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EM Full Name
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US EPA EnviroAtlas - Percent potentially restorable wetlands, USA | WESP: Urban Stormwater Treament, ID, USA |
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EM Source or Collection
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US EPA | EnviroAtlas | None |
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EM Source Document ID
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262 |
393 ?Comment:Additional data came from electronic appendix provided by author Chris Murphy. |
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Document Author
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US EPA Office of Research and Development - National Exposure Research Laboratory | Murphy, C. and T. Weekley |
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Document Year
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2013 | 2012 |
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Document Title
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EnviroAtlas - National | Measuring outcomes of wetland restoration, enhancement, and creation in Idaho-- Assessing potential functions, values, and condition in a watershed context. |
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Document Status
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Peer reviewed and published | Peer reviewed and published |
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Comments on Status
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Published on US EPA EnviroAtlas website | Published report |
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EM ID
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EM-492 |
EM-729 |
| https://www.epa.gov/enviroatlas | Not applicable | |
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Contact Name
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EnviroAtlas Team | Chris Murphy |
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Contact Address
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Not reported | Idaho Dept. Fish and Game, Wildlife Bureau, Habitat Section, Boise, ID |
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Contact Email
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enviroatlas@epa.gov | chris.murphy@idfg.idaho.gov |
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EM ID
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EM-492 |
EM-729 |
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Summary Description
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DATA FACT SHEET: "This EnviroAtlas national map depicts the percent potentially restorable wetlands within each subwatershed (12-digit HUC) in the U.S. Potentially restorable wetlands are defined as agricultural areas that naturally accumulate water and contain some proportion of poorly-drained soils. The EnviroAtlas Team produced this dataset by combining three data layers - land cover, digital elevation, and soil drainage information." "To map potentially restorable wetlands, 2006 National Land Cover Data (NLCD) classes pasture/hay and cultivated crops were reclassified as potentially suitable and all other landcover classes as unsuitable. Poorly- and very poorly drained soils were identified using Natural Resources Conservation Service (NRCS) Soil Survey information mainly from the higher resolution Soil Survey Geographic (SSURGO) Database. The two poorly drained soil classes, expressed as percentage of a polygon in the soil survey, were combined to create a raster layer. A wetness index or Composite Topographic Index (CTI) was developed to identify areas wet enough to create wetlands. The wetness index grid, calculated from National Elevation Data (NED), relates upstream contributing area and slope to overland flow. Results from previous studies suggested that CTI values ≥ 550 captured the majority of wetlands. The three layers, when combined, resulted in four classes: unsuitable, low, moderate, and high wetland restoration potential. Areas with high potential for restorable wetlands have suitable landcover (crop/pasture), CTI values ≥ 550, and 80–100% poorly- or very poorly drained soils (PVP). Areas with moderate potential have suitable landcover, CTI values ≥ 550, and 1–79% PVP. Areas with low potential meet the landcover and 80–100% PVP criteria, but do not have CTI values ≥ 550 to corroborate wetness. All other areas were classed as unsuitable. The percentage of total land within each 12-digit HUC that is covered by potentially restorable wetlands was estimated and displayed in five classes for this map." | A wetland restoration monitoring and assessment program framework was developed for Idaho. The project goal was to assess outcomes of substantial governmental and private investment in wetland restoration, enhancement and creation. The functions, values, condition, and vegetation at restored, enhanced, and created wetlands on private and state lands across Idaho were retrospectively evaluated. Assessment was conducted at multiple spatial scales and intensities. Potential functions and values (ecosystem services) were rapidly assessed using the Oregon Rapid Wetland Assessment Protocol. Vegetation samples were analyzed using Floristic Quality Assessment indices from Washington State. We compared vegetation of restored, enhanced, and created wetlands with reference wetlands that occurred in similar hydrogeomorphic environments determined at the HUC 12 level. |
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Specific Policy or Decision Context Cited
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None Identified | None identified |
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Biophysical Context
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No additional description provided | restored, enhanced and created wetlands |
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EM Scenario Drivers
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No scenarios presented | Sites, function or habitat focus |
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EM ID
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EM-492 |
EM-729 |
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Method Only, Application of Method or Model Run
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Method + Application | Method + Application (multiple runs exist) View EM Runs |
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New or Pre-existing EM?
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New or revised model | WESP - Urban Stormwater Treatment |
Related EMs (for example, other versions or derivations of this EM) described in ESML
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EM ID
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EM-492 |
EM-729 |
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Document ID for related EM
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None | Doc-390 |
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EM ID for related EM
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None | EM-718 | EM-734 |
EM Modeling Approach
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EM ID
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EM-492 |
EM-729 |
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EM Temporal Extent
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2006-2013 | 2010-2011 |
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EM Time Dependence
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time-stationary | time-dependent |
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EM Time Reference (Future/Past)
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Not applicable | past time |
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EM Time Continuity
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Not applicable | Not applicable |
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EM Temporal Grain Size Value
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Not applicable | Not applicable |
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EM Temporal Grain Size Unit
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Not applicable | Not applicable |
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EM ID
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EM-492 |
EM-729 |
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Bounding Type
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Geopolitical | Multiple unrelated locations (e.g., meta-analysis) |
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Spatial Extent Name
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conterminous United States | Wetlands in idaho |
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Spatial Extent Area (Magnitude)
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>1,000,000 km^2 | 100,000-1,000,000 km^2 |
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EM ID
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EM-492 |
EM-729 |
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EM Spatial Distribution
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spatially distributed (in at least some cases) | spatially lumped (in all cases) |
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Spatial Grain Type
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other (specify), for irregular (e.g., stream reach, lake basin) | Not applicable |
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Spatial Grain Size
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irregular | Not applicable |
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EM ID
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EM-492 |
EM-729 |
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EM Computational Approach
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Analytic | Numeric |
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EM Determinism
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deterministic | deterministic |
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Statistical Estimation of EM
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EM ID
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EM-492 |
EM-729 |
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Model Calibration Reported?
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No | No |
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Model Goodness of Fit Reported?
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No | No |
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Goodness of Fit (metric| value | unit)
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None | None |
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Model Operational Validation Reported?
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No | No |
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Model Uncertainty Analysis Reported?
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No | No |
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Model Sensitivity Analysis Reported?
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No | No |
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Model Sensitivity Analysis Include Interactions?
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Not applicable | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
| EM-492 |
EM-729 |
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Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
| EM-492 |
EM-729 |
| None | None |
Centroid Lat/Long (Decimal Degree)
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EM ID
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EM-492 |
EM-729 |
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Centroid Latitude
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39.5 | 44.06 |
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Centroid Longitude
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-98.35 | -114.69 |
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Centroid Datum
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WGS84 | WGS84 |
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Centroid Coordinates Status
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Estimated | Estimated |
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EM ID
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EM-492 |
EM-729 |
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EM Environmental Sub-Class
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Agroecosystems | Inland Wetlands |
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Specific Environment Type
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Terrestrial | created, restored and enhanced wetlands |
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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 |
Scale of differentiation of organisms modeled
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EM ID
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EM-492 |
EM-729 |
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EM Organismal Scale
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Not applicable | Not applicable |
Taxonomic level and name of organisms or groups identified
| EM-492 |
EM-729 |
| None Available | None Available |
EnviroAtlas URL
| EM-492 |
EM-729 |
| GAP Ecological Systems, The Watershed Boundary Dataset (WBD) | Total Annual Reduced Nitrogen Deposition, Carbon Storage by Tree Biomass |
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-492 |
EM-729 |
| None |
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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-492 |
EM-729 |
| None | None |
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