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-449 |
EM-660 |
EM-841 | EM-937 |
|
EM Short Name
em.detail.shortNameHelp
?
|
Decrease in erosion (shoreline), St. Croix, USVI | RUM: Valuing fishing quality, Michigan, USA | Brown-headed cowbird abundance, Piedmont, USA | EPA national stormwater calculator tool |
|
EM Full Name
em.detail.fullNameHelp
?
|
Decrease in erosion (shoreline) by reef, St. Croix, USVI | Random utility model (RUM) Valuing Recreational fishing quality in streams and rivers, Michigan, USA | Brown-headed cowbird abundance, Piedmont ecoregion, USA | Environmental Protection Agency National stormwater calculator tool |
|
EM Source or Collection
em.detail.emSourceOrCollectionHelp
?
|
US EPA | None | None | US EPA |
|
EM Source Document ID
|
335 |
382 ?Comment:Data collected from Michigan Recreational Angler Survey, a mail survey administered monthly to random sample of Michigan fishing license holders since July 2008. Data available taken from 2008-2010. |
405 |
428 ?Comment:This is a tool available on the web for downloading to personal computers. A manual is also available for further documentation of the tool. |
|
Document Author
em.detail.documentAuthorHelp
?
|
Yee, S. H., Dittmar, J. A., and L. M. Oliver | Melstrom, R. T., Lupi, F., Esselman, P.C., and R. J. Stevenson | Riffel, S., Scognamillo, D., and L. W. Burger | Rossman, L.A., Bernagros, J.T., Barr, C.M., and M.A. Simon |
|
Document Year
em.detail.documentYearHelp
?
|
2014 | 2014 | 2008 | 2022 |
|
Document Title
em.detail.sourceIdHelp
?
|
Comparison of methods for quantifying reef ecosystem services: A case study mapping services for St. Croix, USVI | Valuing recreational fishing quality at rivers and streams | Effects of the Conservation Reserve Program on northern bobwhite and grassland birds | EPA National Stormwater Calculator Web App users guide-Version 3.4.0. |
|
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 journal manuscript | Published journal manuscript | Published journal manuscript | Published EPA report |
|
EM ID
em.detail.idHelp
?
|
EM-449 |
EM-660 |
EM-841 | EM-937 |
| Not applicable | Not applicable | Not applicable | https://www.epa.gov/water-research/national-stormwatercalculator | |
|
Contact Name
em.detail.contactNameHelp
?
|
Susan H. Yee | Richard Melstrom | Sam Riffell | Lewis Rossman |
|
Contact Address
|
US EPA, Office of Research and Development, NHEERL, Gulf Ecology Division, Gulf Breeze, FL 32561, USA | Department of Agricultural Economics, Oklahoma State Univ., Stillwater, Oklahoma, USA | Department of Wildlife & Fisheries, Mississippi State University, Mississippi State, MS 39762, USA | Center for environmental solutions and emergency response, Cincinnati, Ohio |
|
Contact Email
|
yee.susan@epa.gov | melstrom@okstate.edu | sriffell@cfr.msstate.edu | n.a. |
|
EM ID
em.detail.idHelp
?
|
EM-449 |
EM-660 |
EM-841 | EM-937 |
|
Summary Description
em.detail.summaryDescriptionHelp
?
|
ABSTRACT: "...We investigated and compared a number of existing methods for quantifying ecological integrity, shoreline protection, recreational opportunities, fisheries production, and the potential for natural products discovery from reefs. Methods were applied to mapping potential ecosystem services production around St. Croix, U.S. Virgin Islands. Overall, we found that a number of different methods produced similar predictions." AUTHOR'S DESCRIPTION: "A number of methods have been developed for linking biophysical attributes of reef condition, such as reef structural complexity, fish biomass, or species richness, to provisioning of ecosystem goods and services (Principe et al., 2012). We investigated the feasibility of using existing methods and data for mapping production of reef ecosystem goods and services. We applied these methods toward mapping potential ecosystem goods and services production in St. Croix, U.S. Virgin Islands (USVI)...For each of the five categories of ecosystem services, we chose a suite of models and indices for estimating potential production based on relative ease of implementation, consisting of well-defined parameters, and likely availability of input data, to maximize potential for transferability to other locations. For each method, we assembled the necessary reef condition and environmental data as spatial data layers for St. Croix (Table1). The coastal zone surrounding St. Croix was divided into 10x10 m grid cells, and production functions were applied to quantify ecosystem services provisioning in each grid cell...Shoreline protection as an ecosystem service has been defined in a number of ways including protection from shoreline erosion...and can thus be estimated as % Decrease in erosion due to reef = 1 - (Ho/H)^2.5 where Ho is the attenuated wave height due to the presence of the reef and H is wave height in the absence of the reef." | ABSTRACT: " This paper describes an economic model that links the demand for recreational stream fishing to fish biomass. Useful measures of fishing quality are often difficult to obtain. In the past, economists have linked the demand for fishing sites to species presence‐absence indicators or average self‐reported catch rates. The demand model presented here takes advantage of a unique data set of statewide biomass estimates for several popular game fish species in Michigan, including trout, bass and walleye. These data are combined with fishing trip information from a 2008–2010 survey of Michigan anglers in order to estimate a demand model. Fishing sites are defined by hydrologic unit boundaries and information on fish assemblages so that each site corresponds to the area of a small subwatershed, about 100–200 square miles in size. The random utility model choice set includes nearly all fishable streams in the state. The results indicate a significant relationship between the site choice behavior of anglers and the biomass of certain species. Anglers are more likely to visit streams in watersheds high in fish abundance, particularly for brook trout and walleye. The paper includes estimates of the economic value of several quality change and site loss scenarios. " | 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. " | "Abstract: EPA’s National Stormwater Calculator (SWC) is a software application tool that estimates the annual amount of rainwater and frequency of runoff from a specific site using green infrastructure as low impact development controls. The SWC is designed for use by anyone interested in reducing runoff from a property, including site developers, landscape architects, urban planners, and homeowners. This User’s guide contains information on the SWC web application. SWC Version 3.4 contains has updated historical meteorological data (from 1970 - 2006 to 1990 - 2019), updated Bureau of Labor Statistics Cost Data (from 2018 to 2020), and the 5.1.015 Stormwater Management Model (SWMM) engine (from 5.1.007). Evaporation was calculated by the Hargreaves method (EPA, 2015), based on historical or future daily temperature data." |
|
Specific Policy or Decision Context Cited
em.detail.policyDecisionContextHelp
?
|
None identified | None identified | None reported | None given |
|
Biophysical Context
|
No additional description provided | stream and river reaches of Michigan | Conservation Reserve Program lands left to go fallow | Sites up to 12 acres |
|
EM Scenario Drivers
em.detail.scenarioDriverHelp
?
|
No scenarios presented | targeted sport fish biomass | N/A | Climate change scenarios |
|
EM ID
em.detail.idHelp
?
|
EM-449 |
EM-660 |
EM-841 | EM-937 |
|
Method Only, Application of Method or Model Run
em.detail.methodOrAppHelp
?
|
Method + Application | Method + Application (multiple runs exist) View EM Runs | Method + Application | Method Only |
|
New or Pre-existing EM?
em.detail.newOrExistHelp
?
|
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
em.detail.idHelp
?
|
EM-449 |
EM-660 |
EM-841 | EM-937 |
|
Document ID for related EM
em.detail.relatedEmDocumentIdHelp
?
|
Doc-335 | None | Doc-405 | None |
|
EM ID for related EM
em.detail.relatedEmEmIdHelp
?
|
EM-447 | EM-448 | None | EM-831 | EM-838 | EM-839 | EM-842 | EM-843 | EM-844 | EM-845 | EM-846 | EM-847 | None |
EM Modeling Approach
|
EM ID
em.detail.idHelp
?
|
EM-449 |
EM-660 |
EM-841 | EM-937 |
|
EM Temporal Extent
em.detail.tempExtentHelp
?
|
2006-2007, 2010 | 2008-2010 | 2008 | Not applicable |
|
EM Time Dependence
em.detail.timeDependencyHelp
?
|
time-stationary | time-stationary | time-stationary | time-stationary |
|
EM Time Reference (Future/Past)
em.detail.futurePastHelp
?
|
Not applicable | Not applicable | Not applicable | Not applicable |
|
EM Time Continuity
em.detail.continueDiscreteHelp
?
|
Not applicable | Not applicable | Not applicable | Not applicable |
|
EM Temporal Grain Size Value
em.detail.tempGrainSizeHelp
?
|
Not applicable | Not applicable | Not applicable | Not applicable |
|
EM Temporal Grain Size Unit
em.detail.tempGrainSizeUnitHelp
?
|
Not applicable | Not applicable | Not applicable | Not applicable |
|
EM ID
em.detail.idHelp
?
|
EM-449 |
EM-660 |
EM-841 | EM-937 |
|
Bounding Type
em.detail.boundingTypeHelp
?
|
Physiographic or ecological | Watershed/Catchment/HUC | Physiographic or ecological | Not applicable |
|
Spatial Extent Name
em.detail.extentNameHelp
?
|
Coastal zone surrounding St. Croix | HUCS in Michigan | Piedmont Ecoregion | Not applicable |
|
Spatial Extent Area (Magnitude)
em.detail.extentAreaHelp
?
|
100-1000 km^2 | 100,000-1,000,000 km^2 | 100,000-1,000,000 km^2 | Not applicable |
|
EM ID
em.detail.idHelp
?
|
EM-449 |
EM-660 |
EM-841 | EM-937 |
|
EM Spatial Distribution
em.detail.distributeLumpHelp
?
|
spatially distributed (in at least some cases) | spatially distributed (in at least some cases) | spatially lumped (in all cases) | spatially lumped (in all cases) |
|
Spatial Grain Type
em.detail.spGrainTypeHelp
?
|
area, for pixel or radial feature | other (specify), for irregular (e.g., stream reach, lake basin) | Not applicable | Not applicable |
|
Spatial Grain Size
em.detail.spGrainSizeHelp
?
|
10 m x 10 m | reach in HUC | Not applicable | Not applicable |
|
EM ID
em.detail.idHelp
?
|
EM-449 |
EM-660 |
EM-841 | EM-937 |
|
EM Computational Approach
em.detail.emComputationalApproachHelp
?
|
Analytic | Numeric | Analytic | Analytic |
|
EM Determinism
em.detail.deterStochHelp
?
|
deterministic | deterministic | deterministic | deterministic |
|
Statistical Estimation of EM
em.detail.statisticalEstimationHelp
?
|
|
|
|
|
|
EM ID
em.detail.idHelp
?
|
EM-449 |
EM-660 |
EM-841 | EM-937 |
|
Model Calibration Reported?
em.detail.calibrationHelp
?
|
Yes | No | Yes | Not applicable |
|
Model Goodness of Fit Reported?
em.detail.goodnessFitHelp
?
|
No | Yes | No | Not applicable |
|
Goodness of Fit (metric| value | unit)
em.detail.goodnessFitValuesHelp
?
|
None |
|
None | None |
|
Model Operational Validation Reported?
em.detail.validationHelp
?
|
Yes | No | No | Not applicable |
|
Model Uncertainty Analysis Reported?
em.detail.uncertaintyAnalysisHelp
?
|
No | No | No | Not applicable |
|
Model Sensitivity Analysis Reported?
em.detail.sensAnalysisHelp
?
|
No | No | Yes | Not applicable |
|
Model Sensitivity Analysis Include Interactions?
em.detail.interactionConsiderHelp
?
|
Not applicable | Not applicable | Unclear | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
| EM-449 |
EM-660 |
EM-841 | EM-937 |
| None |
|
|
|
Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
| EM-449 |
EM-660 |
EM-841 | EM-937 |
|
None | None | None |
Centroid Lat/Long (Decimal Degree)
|
EM ID
em.detail.idHelp
?
|
EM-449 |
EM-660 |
EM-841 | EM-937 |
|
Centroid Latitude
em.detail.ddLatHelp
?
|
17.73 | 45.12 | 36.23 | Not applicable |
|
Centroid Longitude
em.detail.ddLongHelp
?
|
-64.77 | 85.18 | -81.9 | Not applicable |
|
Centroid Datum
em.detail.datumHelp
?
|
WGS84 | WGS84 | WGS84 | Not applicable |
|
Centroid Coordinates Status
em.detail.coordinateStatusHelp
?
|
Estimated | Estimated | Estimated | Not applicable |
|
EM ID
em.detail.idHelp
?
|
EM-449 |
EM-660 |
EM-841 | EM-937 |
|
EM Environmental Sub-Class
em.detail.emEnvironmentalSubclassHelp
?
|
Near Coastal Marine and Estuarine | Rivers and Streams | Grasslands | Terrestrial Environment (sub-classes not fully specified) |
|
Specific Environment Type
em.detail.specificEnvTypeHelp
?
|
Coral reefs | stream reaches | grasslands | Terrrestrial landcover |
|
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-449 |
EM-660 |
EM-841 | EM-937 |
|
EM Organismal Scale
em.detail.orgScaleHelp
?
|
Not applicable | Not applicable | Species | Not applicable |
Taxonomic level and name of organisms or groups identified
| EM-449 |
EM-660 |
EM-841 | EM-937 |
| 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-449 |
EM-660 |
EM-841 | EM-937 |
|
|
|
None |
<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-449 |
EM-660 |
EM-841 | EM-937 |
|
|
|
|
Home
Search EMs
My
EMs
Learn about
ESML
Show Criteria
Hide Criteria