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-92 | EM-449 | EM-937 |
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EM Short Name
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Runoff potential of pesticides, Europe | Decrease in erosion (shoreline), St. Croix, USVI | EPA national stormwater calculator tool |
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EM Full Name
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Runoff potential of pesticides, Europe | Decrease in erosion (shoreline) by reef, St. Croix, USVI | Environmental Protection Agency National stormwater calculator tool |
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EM Source or Collection
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None | US EPA | US EPA |
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EM Source Document ID
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254 | 335 |
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. |
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Document Author
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Schriever, C. A., and Liess, M. | Yee, S. H., Dittmar, J. A., and L. M. Oliver | Rossman, L.A., Bernagros, J.T., Barr, C.M., and M.A. Simon |
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Document Year
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2007 | 2014 | 2022 |
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Document Title
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Mapping ecological risk of agricultural pesticide runoff | Comparison of methods for quantifying reef ecosystem services: A case study mapping services for St. Croix, USVI | EPA National Stormwater Calculator Web App users guide-Version 3.4.0. |
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Document Status
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Peer reviewed and published | Peer reviewed and published | Peer reviewed and published |
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Comments on Status
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Published journal manuscript | Published journal manuscript | Published EPA report |
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EM ID
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EM-92 | EM-449 | EM-937 |
| Not applicable | Not applicable | https://www.epa.gov/water-research/national-stormwatercalculator | |
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Contact Name
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Carola Alexandra Schriever | Susan H. Yee | Lewis Rossman |
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Contact Address
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Helmholtz Centre for Environmental Research - UFZ, Department of System Ecotoxicology, Permoserstrasse 15, 04318 Leipzig, Germany | US EPA, Office of Research and Development, NHEERL, Gulf Ecology Division, Gulf Breeze, FL 32561, USA | Center for environmental solutions and emergency response, Cincinnati, Ohio |
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Contact Email
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carola.schriever@ufz.de | yee.susan@epa.gov | n.a. |
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EM ID
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EM-92 | EM-449 | EM-937 |
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Summary Description
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ABSTRACT: "The approach is based on the runoff potential (RP) of stream sites, by a spatially explicit calculation based on pesticide use, precipitation, topography, land use and soil characteristics in the near-stream environment. The underlying simplified model complies with the limited availability and resolution of data at larger scales." AUTHOR'S DESCRIPTION: "The RP is based on a mathematical model that describes runoff losses of a compound with generalized properties and which was developed from a proposal by the Organisation for Economic Co-operation and Development (OECD) for estimating dissolved runoff inputs of a pesticide into surface waters (OECD, 1998)...The runoff model underlying RP calculates the dissolved amount of a generic substance that was applied in the near environment of a stream site and that is expected to reach the stream site during one rainfall event. The dissolved amount results from a single application in the near-stream environment (i.e., a two-sided 100-m stream corridor extending for 1500 m upstream of the site) and is the amount of applied substance in the designated corridor reduced due to the influence of the site-specific key environmental factors precipitation, soil characteristics, topography, and plant interception." | 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: 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." |
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Specific Policy or Decision Context Cited
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European Commission Water Framework Directive (WFD, Directive 2000/60/EC) | None identified | None given |
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Biophysical Context
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Not applicable | No additional description provided | Sites up to 12 acres |
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EM Scenario Drivers
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No scenarios presented | No scenarios presented | Climate change scenarios |
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EM ID
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EM-92 | EM-449 | EM-937 |
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Method Only, Application of Method or Model Run
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Method + Application | Method + Application | Method Only |
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New or Pre-existing EM?
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New or revised model | Application of existing model | New or revised model |
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-92 | EM-449 | EM-937 |
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Document ID for related EM
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Doc-255 | Doc-256 | Doc-257 | Doc-335 | None |
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EM ID for related EM
em.detail.relatedEmEmIdHelp
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None | EM-447 | EM-448 | None |
EM Modeling Approach
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EM ID
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EM-92 | EM-449 | EM-937 |
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EM Temporal Extent
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2000 | 2006-2007, 2010 | Not applicable |
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EM Time Dependence
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time-dependent | time-stationary | time-stationary |
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EM Time Reference (Future/Past)
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future time | Not applicable | Not applicable |
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EM Time Continuity
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discrete | Not applicable | Not applicable |
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EM Temporal Grain Size Value
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1 | Not applicable | Not applicable |
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EM Temporal Grain Size Unit
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Day | Not applicable | Not applicable |
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EM ID
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EM-92 | EM-449 | EM-937 |
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Bounding Type
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Geopolitical | Physiographic or ecological | Not applicable |
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Spatial Extent Name
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EU-15 | Coastal zone surrounding St. Croix | Not applicable |
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Spatial Extent Area (Magnitude)
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>1,000,000 km^2 | 100-1000 km^2 | Not applicable |
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EM ID
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EM-92 | EM-449 | EM-937 |
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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) |
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Spatial Grain Type
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area, for pixel or radial feature | area, for pixel or radial feature | Not applicable |
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Spatial Grain Size
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10 km x 10 km | 10 m x 10 m | Not applicable |
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EM ID
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EM-92 | EM-449 | EM-937 |
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EM Computational Approach
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Analytic | Analytic | Analytic |
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EM Determinism
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deterministic | deterministic | deterministic |
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Statistical Estimation of EM
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EM ID
em.detail.idHelp
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EM-92 | EM-449 | EM-937 |
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Model Calibration Reported?
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No | Yes | Not applicable |
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Model Goodness of Fit Reported?
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No | No | Not applicable |
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Goodness of Fit (metric| value | unit)
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None | None | None |
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Model Operational Validation Reported?
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No | Yes | Not applicable |
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Model Uncertainty Analysis Reported?
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Yes | No | Not applicable |
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Model Sensitivity Analysis Reported?
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Yes | No | Not applicable |
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Model Sensitivity Analysis Include Interactions?
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No | Not applicable | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
| EM-92 | EM-449 | EM-937 |
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None |
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Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
| EM-92 | EM-449 | EM-937 |
| None |
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None |
Centroid Lat/Long (Decimal Degree)
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EM ID
em.detail.idHelp
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EM-92 | EM-449 | EM-937 |
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Centroid Latitude
em.detail.ddLatHelp
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50.01 | 17.73 | Not applicable |
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Centroid Longitude
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4.67 | -64.77 | Not applicable |
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Centroid Datum
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WGS84 | WGS84 | Not applicable |
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Centroid Coordinates Status
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Estimated | Estimated | Not applicable |
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EM ID
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EM-92 | EM-449 | EM-937 |
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EM Environmental Sub-Class
em.detail.emEnvironmentalSubclassHelp
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Rivers and Streams | Forests | Agroecosystems | Grasslands | Scrubland/Shrubland | Near Coastal Marine and Estuarine | Terrestrial Environment (sub-classes not fully specified) |
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Specific Environment Type
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Arable lands in near-stream environments | Coral reefs | Terrrestrial landcover |
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EM Ecological Scale
em.detail.ecoScaleHelp
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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 is finer than that of the Environmental Sub-class |
Scale of differentiation of organisms modeled
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EM ID
em.detail.idHelp
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EM-92 | EM-449 | EM-937 |
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EM Organismal Scale
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Not applicable | Not applicable | Not applicable |
Taxonomic level and name of organisms or groups identified
| EM-92 | EM-449 | EM-937 |
| 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-92 | EM-449 | EM-937 |
| None |
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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-92 | EM-449 | EM-937 |
| None |
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