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-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
EM Short Name
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WESP: Riparian & stream habitat, ID, USA | WESP: Irrigation water, ID, USA | Mourning dove abundance, Piedmont region, USA | OpenNSPECT v. 1.2 |
EM Full Name
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WESP: Riparian and stream habitat focus projects, ID, USA | WESP: Irrigation return water treatment, Idaho, USA | Mourning dove abundance, Piedmont ecoregion, USA | OpenNSPECT v. 1.2 |
EM Source or Collection
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None | None | None | None |
EM Source Document ID
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393 ?Comment:Additional data came from electronic appendix provided by author Chris Murphy. |
393 ?Comment:Additional data came from electronic appendix provided by author Chris Murphy. |
405 | 431 |
Document Author
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Murphy, C. and T. Weekley | Murphy, C. and T. Weekley | Riffel, S., Scognamillo, D., and L. W. Burger | Eslinger, David L., H. Jamieson Carter, Matt Pendleton, Shan Burkhalter, Margaret Allen |
Document Year
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2012 | 2012 | 2008 | 2012 |
Document Title
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Measuring outcomes of wetland restoration, enhancement, and creation in Idaho-- Assessing potential functions, values, and condition in a watershed context. | Measuring outcomes of wetland restoration, enhancement, and creation in Idaho-- Assessing potential functions, values, and condition in a watershed context. | Effects of the Conservation Reserve Program on northern bobwhite and grassland birds | “OpenNSPECT: The Open-source Nonpoint Source Pollution and Erosion Comparison Tool.” NOAA Office for Coastal Management, Charleston, South Carolina. Accessed (11/2022) at https://coast.noaa.gov/digitalcoast/tools/opennspect.html |
Document Status
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Peer reviewed and published | Peer reviewed and published | Peer reviewed and published | Peer reviewed and published |
Comments on Status
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Published report | Published report | Published journal manuscript | Webpage |
EM ID
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EM-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
Not applicable | Not applicable | Not applicable | https://coast.noaa.gov/digitalcoast/tools/opennspect.html | |
Contact Name
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Chris Murphy | Chris Murphy | Sam Riffell | Not reported |
Contact Address
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Idaho Dept. Fish and Game, Wildlife Bureau, Habitat Section, Boise, ID | Idaho Dept. Fish and Game, Wildlife Bureau, Habitat Section, Boise, ID | Department of Wildlife & Fisheries, Mississippi State University, Mississippi State, MS 39762, USA | NOAA Coastal Services Center, 2234 South Hobson Avenue Charleston, South Carolina 29405-2413 |
Contact Email
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chris.murphy@idfg.idaho.gov | chris.murphy@idfg.idaho.gov | sriffell@cfr.msstate.edu | Not reported |
EM ID
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EM-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
Summary Description
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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. | 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. | ABSTRACT:"The Conservation Reserve Program (CRP) has converted just over 36 million acres of cropland into potential wildlife habitat, primarily grassland. Thus, the CRP should benefit grassland songbirds, a group of species that is declining across the United States and is of conservation concern. Additionally, the CRP is an important part of multi-agency, regional efforts to restore northern bobwhite populations. However, comprehensive assessments of the wildlife benefits of CRP at regional scales are lacking. We used Breeding Bird Survey and National Resources Inventory data to assess the potential for the CRP to benefit northern bobwhite and other grassland birds with overlapping ranges and similar habitat associations. We built regression models for 15 species in seven different ecological regions. Forty-nine of 108 total models contained significant CRP effects (P < 0.05), and 48 of the 49 contained positive effects. Responses to CRP varied across ecological regions. Only eastern meadowlark was positively related to CRP in all the ecological regions, and western meadowlark was the only species never related to CRP. CRP was a strong predictor of bird abundance compared to other land cover types. The potential for CRP habitat as a regional conservation tool to benefit declining grassland bird populations should continue to be assessed at a variety of spatial scales. We caution that bird-CRP relations varied from region to region and among species. Because the NRI provides relatively coarse resolution information on CRP, more detailed information about CRP habitats (spatial arrangement, age of the habitat (time since planting), specific conservation practices used) should be included in future assessments to fully understand where and to what extent CRP can benefit grassland birds. " | "This open-source version of the Nonpoint Source Pollution and Erosion Comparison Tool is used to investigate potential water quality impacts from climate change and development to other land uses. The downloadable tool is designed to be broadly applicable for coastal and noncoastal areas alike. Tool functions simulate erosion, pollution, and the accumulation from overland flow. OpenNSPECT uses spatial elevation data to calculate flow direction and flow accumulation throughout a watershed. To do this, land cover, precipitation, and soils data are processed to estimate runoff volume at both the local and watershed levels. Coefficients representing the contribution of each land cover class to the expected pollutant load are also applied to land cover data to approximate total pollutant loads. These coefficients are taken from published sources or can be derived from local water quality studies. The output layers display estimates of runoff volume, pollutant loads, pollutant concentration, and total sediment yield. Requires MapWindow GIS v.4.8.8 (open source software)" |
Specific Policy or Decision Context Cited
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None identified | None identified | None reported | None identified |
Biophysical Context
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restored, enhanced and created wetlands | restored, enhanced and created wetlands | Conservation Reserve Program lands left to go fallow | No additional description provided |
EM Scenario Drivers
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Sites, function or habitat focus | Sites, function or habitat focus | N/A | No scenarios presented |
EM ID
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EM-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
Method Only, Application of Method or Model Run
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Method + Application (multiple runs exist) View EM Runs | Method + Application (multiple runs exist) View EM Runs | Method + Application | Method Only |
New or Pre-existing EM?
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Application of existing model | 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-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
Document ID for related EM
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Doc-390 | Doc-390 | Doc-405 | None |
EM ID for related EM
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EM-706 | EM-729 | EM-730 | EM-734 | EM-743 | EM-749 | EM-750 | EM-756 | EM-757 | EM-758 | EM-759 | EM-760 | EM-761 | EM-763 | EM-764 | EM-766 | EM-767 | EM-732 | EM-737 | EM-738 | EM-739 | EM-741 | EM-742 | EM-751 | EM-768 | EM-718 | EM-734 | EM-760 | EM-761 | EM-763 | EM-764 | EM-766 | EM-767 | EM-768 | EM-831 | EM-838 | EM-839 | EM-840 | EM-841 | EM-842 | EM-844 | EM-845 | EM-846 | EM-847 | EM-940 |
EM Modeling Approach
EM ID
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EM-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
EM Temporal Extent
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2010-2011 | 2010-2012 | 2008 | Not applicable |
EM Time Dependence
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time-dependent | time-dependent | time-stationary | time-stationary |
EM Time Reference (Future/Past)
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past time | past time | Not applicable | Not applicable |
EM Time Continuity
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Not applicable | Not applicable | Not applicable | Not applicable |
EM Temporal Grain Size Value
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Not applicable | Not applicable | Not applicable | Not applicable |
EM Temporal Grain Size Unit
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Not applicable | Not applicable | Not applicable | Not applicable |
EM ID
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EM-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
Bounding Type
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Multiple unrelated locations (e.g., meta-analysis) | Multiple unrelated locations (e.g., meta-analysis) | Physiographic or ecological | Not applicable |
Spatial Extent Name
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Wetlands in idaho | Wetlands in idaho | Piedmont Ecoregion | Not applicable |
Spatial Extent Area (Magnitude)
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100,000-1,000,000 km^2 | 100,000-1,000,000 km^2 | 100,000-1,000,000 km^2 | Not applicable |
EM ID
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EM-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
EM Spatial Distribution
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spatially lumped (in all cases) | spatially lumped (in all cases) | spatially lumped (in all cases) | spatially distributed (in at least some cases) |
Spatial Grain Type
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Not applicable | Not applicable | Not applicable | area, for pixel or radial feature |
Spatial Grain Size
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Not applicable | Not applicable | Not applicable | 30 m |
EM ID
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EM-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
EM Computational Approach
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Numeric | Numeric | Analytic | Analytic |
EM Determinism
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deterministic | deterministic | deterministic | deterministic |
Statistical Estimation of EM
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EM ID
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EM-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
Model Calibration Reported?
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No | No | Yes | Not applicable |
Model Goodness of Fit Reported?
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No | No | No | Not applicable |
Goodness of Fit (metric| value | unit)
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None | None | None | None |
Model Operational Validation Reported?
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No | No | No | Not applicable |
Model Uncertainty Analysis Reported?
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No | No | No | Not applicable |
Model Sensitivity Analysis Reported?
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No | No | Yes | Not applicable |
Model Sensitivity Analysis Include Interactions?
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Not applicable | Not applicable | Unclear | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
EM-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
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None |
Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
EM-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
None | None | None | None |
Centroid Lat/Long (Decimal Degree)
EM ID
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EM-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
Centroid Latitude
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44.06 | 44.06 | 36.23 | Not applicable |
Centroid Longitude
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-114.69 | -114.69 | -81.9 | Not applicable |
Centroid Datum
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WGS84 | WGS84 | WGS84 | Not applicable |
Centroid Coordinates Status
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Estimated | Estimated | Estimated | Not applicable |
EM ID
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EM-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
EM Environmental Sub-Class
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Inland Wetlands | Inland Wetlands | Grasslands | Aquatic Environment (sub-classes not fully specified) | Near Coastal Marine and Estuarine | Terrestrial Environment (sub-classes not fully specified) |
Specific Environment Type
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created, restored and enhanced wetlands | created, restored and enhanced wetlands | grasslands | Coastal and non-coastal |
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 | Ecological scale is finer than that of the Environmental Sub-class |
Scale of differentiation of organisms modeled
EM ID
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EM-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
EM Organismal Scale
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Not applicable | Not applicable | Species | Not applicable |
Taxonomic level and name of organisms or groups identified
EM-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
None Available | None Available |
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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-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
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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-718 ![]() |
EM-743 ![]() |
EM-843 | EM-938 |
None | None |
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None |