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-193 | EM-704 | EM-967 |
EM Short Name
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Cultural ecosystem services, Bilbao, Spain | Northern Pintail recruits, CREP wetlands, IA, USA | IPaC, USFWS, USA |
EM Full Name
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Cultural ecosystem services, Bilbao, Spain | Northern Pintail duck recruits, CREP (Conservation Reserve Enhancement Program) wetlands, Iowa, USA | Information for Planning and Conservation tool, USFWS, U.S. |
EM Source or Collection
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None ?Comment:EU Mapping Studies |
None | None |
EM Source Document ID
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191 |
372 ?Comment:Document 373 is a secondary source for this EM. |
451 ?Comment:Assume peer reviewed at least internally by USFWS |
Document Author
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Casado-Arzuaga, I., Onaindia, M., Madariaga, I. and Verburg P. H. | 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 | U.S. Fish and Wildlife Service |
Document Year
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2013 | 2010 | None |
Document Title
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Mapping recreation and aesthetic value of ecosystems in the Bilbao Metropolitan Greenbelt (northern Spain) to support landscape planning | Assessment of environmental services of CREP wetlands in Iowa and the midwestern corn belt | Information for Planning and Consultation (IPaC |
Document Status
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Peer reviewed and published | Peer reviewed and published | Other or unclear (explain in Comment) |
Comments on Status
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Published journal manuscript | Published report | Published report |
EM ID
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EM-193 | EM-704 | EM-967 |
Not applicable | Not applicable | https://ipac.ecosphere.fws.gov/ | |
Contact Name
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Izaskun Casado-Arzuaga | David Otis | USFWS |
Contact Address
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Plant Biology and Ecology Department, University of the Basque Country UPV/EHU, Campus de Leioa, Barrio Sarriena s/n, 48940 Leioa, Bizkaia, Spain | U.S. Geological Survey, Iowa Cooperative Fish and Wildlife Research Unit, Iowa State University | 911 NE 11th Avenue Portland, OR 97232 |
Contact Email
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izaskun.casado@ehu.es | dotis@iastate.edu | fwhq_ipac@fws.gov |
EM ID
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EM-193 | EM-704 | EM-967 |
Summary Description
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ABSTRACT "This paper presents a method to quantify cultural ecosystem services (ES) and their spatial distribution in the landscape based on ecological structure and social evaluation approaches. The method aims to provide quantified assessments of ES to support land use planning decisions. A GIS-based approach was used to estimate and map the provision of recreation and aesthetic services supplied by ecosystems in a peri-urban area located in the Basque Country, northern Spain. Data of two different public participation processes (frequency of visits to 25 different sites within the study area and aesthetic value of different landscape units) were used to validate the maps. Three maps were obtained as results: a map showing the provision of recreation services, an aesthetic value map and a map of the correspondences and differences between both services. The data obtained in the participation processes were found useful for the validation of the maps. A weak spatial correlation was found between aesthetic quality and recreation provision services, with an overlap of the highest values for both services only in 7.2 % of the area. A consultation with decision-makers indicated that the results were considered useful to identify areas that can be targeted for improvement of landscape and recreation management." | ABSTRACT: "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…" AUTHOR'S DESCRIPTION: "The first phase of the U.S. Fish and Wildlife Service task was to evaluate the contribution of the 27 approved sites to migratory birds breeding in the Prairie Pothole Region of Iowa. To date, evaluation has been completed for 7 species of waterfowl and 5 species of grassland birds. All evaluations were completed using existing models that relate landscape composition to bird populations. As such, the first objective was to develop a current land cover geographic information system (GIS) that reflected current landscape conditions including the incorporation of habitat restored through the CREP program. The second objective was to input landscape variables from our land cover GIS into models to estimate various migratory bird population parameters (i.e. the number of pairs, individuals, or recruits) for each site. Recruitment for the 27 sites was estimated for Mallards, Blue-winged Teal, Northern Shoveler, Gadwall, and Northern Pintail according to recruitment models presented by Cowardin et al. (1995). Recruitment was not estimated for Canada Geese and Wood Ducks because recruitment models do not exist for these species. Variables used to estimate recruitment included the number of pairs, the composition of the landscape in a 4-square mile area around the CREP wetland, species-specific habitat preferences, and species- and habitat-specific clutch success rates. Recruitment estimates were derived using the following equations: Recruits = 2*R*n where, 2 = constant based on the assumption of equal sex ratio at hatch, n = number of breeding pairs estimated using the pairs equation previously outlined, R = Recruitment rate as defined by Cowardin and Johnson (1979) where, R = H*Z*B/2 where, H = hen success (see Cowardin et al. (1995) for methods used to calculate H, which is related to land cover types in the 4-mile2 landscape around each wetland), Z = proportion of broods that survived to fledge at least 1 recruit (= 0.74 based on Cowardin and Johnson 1979), B = average brood size at fledging (= 4.9 based on Cowardin and Johnson 1979)." ENTERER'S COMMENT: The number of breeding pairs (n) is estimated by a separate submodel from this paper, and as such is also entered as a separate model in ESML (EM 632). | IPaC is a project planning tool that streamlines the USFWS environmental review process. Explores species and habitat: See if any listed species, critical habitat, migratory birds or other natural resources may be impacted by your project. Using the map tool, explore other resources in your location, such as wetlands, wildlife refuges, GAP land cover, and other important biological resources. Conduct a regulatory review: Log in and define a project to get an official species list and evaluate potential impacts on resources managed by the U.S. Fish and Wildlife Service. Follow IPaC's Endangered Species Act (ESA) Review process—a streamlined, step-by-step consultation process available in select areas for certain project types, agencies, and species. Build a Consultation Package: Consultation Package Builder (CPB) replaces and improves on the original Impact Analysis by providing an interactive, step-by-step process to help you prepare a full consultation package leveraging U.S. Fish and Wildlife Service data and recommendations, including conservation measures designed to help you avoid or minimize effects to listed species. |
Specific Policy or Decision Context Cited
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Land management, ecosystem management, response to EU 2020 Biodiversity Strategy | None identified | Determination of Effects on ESA listed taxa. |
Biophysical Context
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Northern Spain; Bizkaia region | Prairie Pothole Region of Iowa | N/A |
EM Scenario Drivers
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No scenarios presented | No scenarios presented | N/A |
EM ID
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EM-193 | EM-704 | EM-967 |
Method Only, Application of Method or Model Run
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Method + Application | Method + Application | Method Only |
New or Pre-existing EM?
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New or revised 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-193 | EM-704 | EM-967 |
Document ID for related EM
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None | Doc-372 | Doc-373 | None |
EM ID for related EM
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None | EM-705 | EM-703 | EM-702 | EM-701 | EM-700 | None |
EM Modeling Approach
EM ID
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EM-193 | EM-704 | EM-967 |
EM Temporal Extent
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2000 - 2007 | 1987-2007 | Not applicable |
EM Time Dependence
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time-stationary | time-stationary | time-stationary |
EM Time Reference (Future/Past)
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Not applicable | Not applicable | Not applicable |
EM Time Continuity
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Not applicable | Not applicable | Not applicable |
EM Temporal Grain Size Value
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Not applicable | Not applicable | Not applicable |
EM Temporal Grain Size Unit
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Not applicable | Not applicable | Not applicable |
EM ID
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EM-193 | EM-704 | EM-967 |
Bounding Type
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Geopolitical | Multiple unrelated locations (e.g., meta-analysis) | Not applicable |
Spatial Extent Name
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Bilbao Metropolitan Greenbelt | CREP (Conservation Reserve Enhancement Program | Not applicable |
Spatial Extent Area (Magnitude)
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100-1000 km^2 | 10,000-100,000 km^2 | Not applicable |
EM ID
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EM-193 | EM-704 | EM-967 |
EM Spatial Distribution
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spatially distributed (in at least some cases) | spatially distributed (in at least some cases) | spatially lumped (in all cases) |
Spatial Grain Type
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area, for pixel or radial feature | other (specify), for irregular (e.g., stream reach, lake basin) | Not applicable |
Spatial Grain Size
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2 m x 2 m | multiple, individual, irregular sites | Not applicable |
EM ID
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EM-193 | EM-704 | EM-967 |
EM Computational Approach
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Analytic | Analytic | Other or unclear (comment) |
EM Determinism
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deterministic | deterministic | Not applicable |
Statistical Estimation of EM
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EM ID
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EM-193 | EM-704 | EM-967 |
Model Calibration Reported?
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No | Unclear | Not applicable |
Model Goodness of Fit Reported?
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No | No | Not applicable |
Goodness of Fit (metric| value | unit)
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None | None | None |
Model Operational Validation Reported?
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Yes | No | Not applicable |
Model Uncertainty Analysis Reported?
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No | No | Not applicable |
Model Sensitivity Analysis Reported?
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No | No | Not applicable |
Model Sensitivity Analysis Include Interactions?
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Not applicable | Not applicable | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
EM-193 | EM-704 | EM-967 |
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None |
Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
EM-193 | EM-704 | EM-967 |
None | None | None |
Centroid Lat/Long (Decimal Degree)
EM ID
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EM-193 | EM-704 | EM-967 |
Centroid Latitude
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43.25 | 42.62 | Not applicable |
Centroid Longitude
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-2.92 | -93.84 | Not applicable |
Centroid Datum
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WGS84 | WGS84 | Not applicable |
Centroid Coordinates Status
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Provided | Estimated | Not applicable |
EM ID
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EM-193 | EM-704 | EM-967 |
EM Environmental Sub-Class
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Aquatic Environment (sub-classes not fully specified) | Rivers and Streams | Near Coastal Marine and Estuarine | Terrestrial Environment (sub-classes not fully specified) | Forests | Agroecosystems | Created Greenspace | Grasslands | Scrubland/Shrubland | Inland Wetlands | Agroecosystems | Grasslands | Aquatic Environment (sub-classes not fully specified) | Rivers and Streams | Inland Wetlands | Lakes and Ponds | Near Coastal Marine and Estuarine | Open Ocean and Seas | Ground Water | Terrestrial Environment (sub-classes not fully specified) | Forests | Agroecosystems | Created Greenspace | Grasslands | Scrubland/Shrubland | Barren | Tundra | Ice and Snow | Atmosphere |
Specific Environment Type
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none | Wetlands buffered by grassland within agroecosystems | None |
EM Ecological Scale
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Ecological scale is finer than that of the Environmental Sub-class | Ecological scale corresponds to the Environmental Sub-class | Not applicable |
Scale of differentiation of organisms modeled
EM ID
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EM-193 | EM-704 | EM-967 |
EM Organismal Scale
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Not applicable | Individual or population, within a species |
Other (Comment) ?Comment:ESA designations include species and Ecological Significan Units of species |
Taxonomic level and name of organisms or groups identified
EM-193 | EM-704 | EM-967 |
None Available |
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None Available |
EnviroAtlas URL
EM-193 | EM-704 | EM-967 |
Percent IUCN Status II, Percent GAP Status 1 & 2 | Acres of Land Enrolled in the Conservation Reserve Program (CRP) | GAP Ecological Systems, Percent GAP Status 1 & 2 |
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-193 | EM-704 | EM-967 |
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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-193 | EM-704 | EM-967 |
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