EcoService Models Library (ESML)
loading
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
em.detail.idHelp
?
|
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
EM Short Name
em.detail.shortNameHelp
?
|
EPA H2O, Tampa Bay Region, FL,USA | Wetland shellfish production, Gulf of Mexico, USA | WESP Method | WESP: Urban Stormwater Treatment, ID, USA |
EM Full Name
em.detail.fullNameHelp
?
|
EPA H2O, Tampa Bay Region, FL, USA | Wetland shellfish production, Gulf of Mexico, USA | Method for the Wetland Ecosystem Services Protocol (WESP) | WESP: Urban Stormwater Treament, ID, USA |
EM Source or Collection
em.detail.emSourceOrCollectionHelp
?
|
US EPA |
US EPA ?Comment:Marine and Coastal Fisheries: Dynamics, Management, and Ecosystem Science |
None | None |
EM Source Document ID
|
321 | 324 | 390 |
393 ?Comment:Additional data came from electronic appendix provided by author Chris Murphy. |
Document Author
em.detail.documentAuthorHelp
?
|
Ranade, P., Soter, G., Russell, M., Harvey, J., and K. Murphy | Stephen J. Jordan, Timothy O'Higgins and John A. Dittmar | Adamus, P. R. | Murphy, C. and T. Weekley |
Document Year
em.detail.documentYearHelp
?
|
2015 | 2012 | 2016 | 2012 |
Document Title
em.detail.sourceIdHelp
?
|
EPA H20 User Manual | Ecosystem Services of Coastal Habitats and Fisheries: Multiscale Ecological and Economic Models in Support of Ecosystem-Based Management | Manual for the Wetland Ecosystem Services Protocol (WESP) v. 1.3. | Measuring outcomes of wetland restoration, enhancement, and creation in Idaho-- Assessing potential functions, values, and condition in a watershed context. |
Document Status
em.detail.statusCategoryHelp
?
|
Peer reviewed and published | Peer reviewed and published | Peer reviewed and published | Peer reviewed and published |
Comments on Status
em.detail.commentsOnStatusHelp
?
|
Published EPA report | Published journal manuscript | Published report | Published report |
EM ID
em.detail.idHelp
?
|
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
http://www.epa.gov/ged/tbes/EPAH2O | Not applicable |
http://people.oregonstate.edu/~adamusp/WESP/ ?Comment:This is an Excel spreadsheet calculator |
Not applicable | |
Contact Name
em.detail.contactNameHelp
?
|
Marc J. Russell, Ph.D. | Stephen J. Jordan | Paul R. Adamus | Chris Murphy |
Contact Address
|
USEPA GED, One Sabine Island Dr., Gulf Breeze, FL 32561 | U.S. Environmental Protection Agency, Gulf Ecology Division, 1 Sabine Island Drive, Gulf Breeze, FL 32561, USA | 6028 NW Burgundy Dr. Corvallis, OR 97330 | Idaho Dept. Fish and Game, Wildlife Bureau, Habitat Section, Boise, ID |
Contact Email
|
russell.marc@epa.gov | jordan.steve@epa.gov | adamus7@comcast.net | chris.murphy@idfg.idaho.gov |
EM ID
em.detail.idHelp
?
|
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
Summary Description
em.detail.summaryDescriptionHelp
?
|
AUTHORS DESCRIPTION: "EPA H2O is a GIS based demonstration tool for assessing ecosystem goods and services (EGS). It was developed as a preliminary assessment tool in support of research being conducted in the Tampa Bay watershed. It provides information, data, approaches and guidance that communities can use to examine alternative land use scenarios in the context of nature’s benefits to the human community. . . EPA H2O allows users for the Tampa Bay estuary and its watershed to: • Gain a greater understanding of the significance of EGS, • Explore the spatial distribution of EGS and other ecosystem features, • Obtain map and summary statistics of EGS production's potential value, • Analyze and compare potential impacts from predicted development scenarios or user specified changes in land use patterns on EGS production's potential value EPA H2O is designed for analyzing data at neighborhood to regional scales.. . The tool is transportable to other locations if the required data are available. . . . | ABSTRACT: "We present concepts and case studies linking the production functions (contributions to recruitment) of critical habitats to commercial and recreational fishery values by combining site specific research data with spatial analysis and population models. We present examples illustrating various spatial scales of analysis, with indicators of economic value, for … commercial blue crab Callinectes sapidus and penaeid shrimp fisheries in the Gulf of Mexico." | Author Description: " The Wetland Ecosystem Services Protocol (WESP) is a standardized template for creating regionalized methods which then can be used to rapid assess ecosystem services (functions and values) of all wetland types throughout a focal region. To date, regionalized versions of WESP have been developed (or are ongoing) for government agencies or NGOs in Oregon, Alaska, Alberta, New Brunswick, and Nova Scotia. WESP also may be used directly in its current condition to assess these services at the scale of an individual wetland, but without providing a regional context for interpreting that information. Nonetheless, WESP takes into account many landscape factors, especially as they relate to the potential or actual benefits of a wetland’s functions. A WESP assessment requires completing a single three-part data form, taking about 1-3 hours. Responses to questions on that form are based on review of aerial imagery and observations during a single site visit; GIS is not required. After data are entered in an Excel spreadsheet, the spreadsheet uses science-based logic models to automatically generate scores intended to reflect a wetland’s ability to support the following functions: Water Storage and Delay, Stream Flow Support, Water Cooling, Sediment Retention and Stabilization, Phosphorus Retention, Nitrate Removal and Retention, Carbon Sequestration, Organic Nutrient Export, Aquatic Invertebrate Habitat, Anadromous Fish Habitat, Non-anadromous Fish Habitat, Amphibian & Reptile Habitat, Waterbird Feeding Habitat, Waterbird Nesting Habitat, Songbird, Raptor and Mammal Habitat, Pollinator Habitat, and Native Plant Habitat. For all but two of these functions, scores are given for both components of an ecosystem service: function and benefit. In addition, wetland Ecological Condition (Integrity), Public Use and Recognition, Wetland Sensitivity, and Stressors are scored. Scores generated by WESP may be used to (a) estimate a wetland’s relative ecological condition, stress, and sensitivity, (b) compare relative levels of ecosystem services among different wetland types, or (c) compare those in a single wetland before and after restoration, enhancement, or loss."] | 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. |
Specific Policy or Decision Context Cited
em.detail.policyDecisionContextHelp
?
|
None reported | None identified | None identified | None identified |
Biophysical Context
|
Not applicable | Estuarine environments and marsh-land interfaces | None | restored, enhanced and created wetlands |
EM Scenario Drivers
em.detail.scenarioDriverHelp
?
|
Land Use, EGS algorithm values, | Shellfish type; Changes to submerged aquatic vegetation (SAV) | N/A | Sites, function or habitat focus |
EM ID
em.detail.idHelp
?
|
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
Method Only, Application of Method or Model Run
em.detail.methodOrAppHelp
?
|
Method + Application |
Method + Application (multiple runs exist) View EM Runs ?Comment:Ten runs; blue crab and penaeid shrimp, each combined with five different submerged aquatic vegetation habitat areas. |
Method Only | Method + Application (multiple runs exist) View EM Runs |
New or Pre-existing EM?
em.detail.newOrExistHelp
?
|
New or revised model | New or revised model | New or revised model | WESP - Urban Stormwater Treatment |
Related EMs (for example, other versions or derivations of this EM) described in ESML
EM ID
em.detail.idHelp
?
|
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
Document ID for related EM
em.detail.relatedEmDocumentIdHelp
?
|
None | None | None | Doc-390 |
EM ID for related EM
em.detail.relatedEmEmIdHelp
?
|
None | EM-604 | EM-603 | EM-718 | EM-718 | EM-734 |
EM Modeling Approach
EM ID
em.detail.idHelp
?
|
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
EM Temporal Extent
em.detail.tempExtentHelp
?
|
Not applicable | 1950 - 2050 | Not applicable | 2010-2011 |
EM Time Dependence
em.detail.timeDependencyHelp
?
|
time-stationary | time-dependent | time-stationary | time-dependent |
EM Time Reference (Future/Past)
em.detail.futurePastHelp
?
|
Not applicable | future time | Not applicable | past time |
EM Time Continuity
em.detail.continueDiscreteHelp
?
|
Not applicable | discrete | Not applicable | Not applicable |
EM Temporal Grain Size Value
em.detail.tempGrainSizeHelp
?
|
Not applicable | Varies by Run | Not applicable | Not applicable |
EM Temporal Grain Size Unit
em.detail.tempGrainSizeUnitHelp
?
|
Not applicable | Year | Not applicable | Not applicable |
EM ID
em.detail.idHelp
?
|
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
Bounding Type
em.detail.boundingTypeHelp
?
|
Geopolitical ?Comment:Extent was Tampa Bay area in example, but boundary can be geopolitical or watershed derived. |
Physiographic or ecological | Not applicable | Multiple unrelated locations (e.g., meta-analysis) |
Spatial Extent Name
em.detail.extentNameHelp
?
|
Tampa Bay region | Gulf of Mexico (estuarine and coastal) | Not applicable | Wetlands in idaho |
Spatial Extent Area (Magnitude)
em.detail.extentAreaHelp
?
|
1000-10,000 km^2. | 10,000-100,000 km^2 | Not applicable | 100,000-1,000,000 km^2 |
EM ID
em.detail.idHelp
?
|
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
EM Spatial Distribution
em.detail.distributeLumpHelp
?
|
spatially distributed (in at least some cases) |
spatially distributed (in at least some cases) ?Comment:Computations at this pixel scale pertain to certain variables specific to Mobile Bay. |
spatially distributed (in at least some cases) | spatially lumped (in all cases) |
Spatial Grain Type
em.detail.spGrainTypeHelp
?
|
area, for pixel or radial feature | area, for pixel or radial feature | area, for pixel or radial feature | Not applicable |
Spatial Grain Size
em.detail.spGrainSizeHelp
?
|
30m x 30m | 55.2 km^2 | not reported | Not applicable |
EM ID
em.detail.idHelp
?
|
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
EM Computational Approach
em.detail.emComputationalApproachHelp
?
|
Analytic | Numeric | Analytic | Numeric |
EM Determinism
em.detail.deterStochHelp
?
|
deterministic | deterministic | deterministic | deterministic |
Statistical Estimation of EM
em.detail.statisticalEstimationHelp
?
|
|
|
|
|
EM ID
em.detail.idHelp
?
|
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
Model Calibration Reported?
em.detail.calibrationHelp
?
|
No | Yes | Not applicable | No |
Model Goodness of Fit Reported?
em.detail.goodnessFitHelp
?
|
No | No | Not applicable | No |
Goodness of Fit (metric| value | unit)
em.detail.goodnessFitValuesHelp
?
|
None | None | None | None |
Model Operational Validation Reported?
em.detail.validationHelp
?
|
No | No | No | No |
Model Uncertainty Analysis Reported?
em.detail.uncertaintyAnalysisHelp
?
|
No | No | Not applicable | No |
Model Sensitivity Analysis Reported?
em.detail.sensAnalysisHelp
?
|
No | No | Not applicable | No |
Model Sensitivity Analysis Include Interactions?
em.detail.interactionConsiderHelp
?
|
Not applicable | Not applicable | Not applicable | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
|
|
None |
|
Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
None |
|
None | None |
Centroid Lat/Long (Decimal Degree)
EM ID
em.detail.idHelp
?
|
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
Centroid Latitude
em.detail.ddLatHelp
?
|
28.05 | 30.44 | Not applicable | 44.06 |
Centroid Longitude
em.detail.ddLongHelp
?
|
-82.52 | -87.99 | Not applicable | -114.69 |
Centroid Datum
em.detail.datumHelp
?
|
WGS84 | WGS84 | Not applicable | WGS84 |
Centroid Coordinates Status
em.detail.coordinateStatusHelp
?
|
Estimated | Estimated | Not applicable | Estimated |
EM ID
em.detail.idHelp
?
|
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
EM Environmental Sub-Class
em.detail.emEnvironmentalSubclassHelp
?
|
Terrestrial Environment (sub-classes not fully specified) | Near Coastal Marine and Estuarine | Inland Wetlands | Inland Wetlands |
Specific Environment Type
em.detail.specificEnvTypeHelp
?
|
All terestrial landcover and waterbodies | Submerged aquatic vegetation in estuaries and coastal lagoons | Wetlands | created, restored and enhanced wetlands |
EM Ecological Scale
em.detail.ecoScaleHelp
?
|
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 | Ecological scale is finer than that of the Environmental Sub-class |
Scale of differentiation of organisms modeled
EM ID
em.detail.idHelp
?
|
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
EM Organismal Scale
em.detail.orgScaleHelp
?
|
Not applicable | Species | Not applicable | Not applicable |
Taxonomic level and name of organisms or groups identified
EM-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
None Available |
|
None Available | None Available |
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-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
|
|
|
|
<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-392 |
EM-397 ![]() |
EM-706 |
EM-729 ![]() |
|
|
|
None |