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
em.detail.idHelp
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EM-937 |
EM-992 |
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EM Short Name
em.detail.shortNameHelp
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EPA national stormwater calculator tool | DAISY model, Taastrup, Copenhagen |
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EM Full Name
em.detail.fullNameHelp
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Environmental Protection Agency National stormwater calculator tool | Ecosystem function and service quantification and valuation in a conventional winter wheat production system with DAISY model in Denmark |
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EM Source or Collection
em.detail.emSourceOrCollectionHelp
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US EPA | None |
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EM Source Document ID
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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. |
464 |
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Document Author
em.detail.documentAuthorHelp
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Rossman, L.A., Bernagros, J.T., Barr, C.M., and M.A. Simon | Ghaley, B. B., & Porter, J. R. |
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Document Year
em.detail.documentYearHelp
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2022 | 2014 |
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Document Title
em.detail.sourceIdHelp
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EPA National Stormwater Calculator Web App users guide-Version 3.4.0. | Ecosystem function and service quantification and valuation in a conventional winter wheat production system with DAISY model in Denmark |
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Document Status
em.detail.statusCategoryHelp
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Peer reviewed and published | Peer reviewed and published |
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Comments on Status
em.detail.commentsOnStatusHelp
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Published EPA report | Published journal manuscript |
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EM ID
em.detail.idHelp
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EM-937 |
EM-992 |
| https://www.epa.gov/water-research/national-stormwatercalculator | Not applicable | |
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Contact Name
em.detail.contactNameHelp
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Lewis Rossman | Bhim Bahadur Ghaley |
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Contact Address
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Center for environmental solutions and emergency response, Cincinnati, Ohio | Department of Plant and Environmental Sciences, Faculty of Science, University of Copenhagen, Højbakkegård Allé 30, DK-2630 Taastrup, Denmark. |
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Contact Email
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n.a. | bbg@life.ku.dk |
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EM ID
em.detail.idHelp
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EM-937 |
EM-992 |
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Summary Description
em.detail.summaryDescriptionHelp
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"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." | With inevitable link between ecosystem function (EF), ecosystem services (ES) and agricultural productivity, there is a need for quantification and valuation of EF and ES in agro-ecosystems. Management practices have significant effects on soil organic matter (SOM), affecting productivity, EF and ES provision. The objective was to quantify two EF: soil water storage and nitrogen mineralization and three ES: food and fodder production and carbon sequestration, in a conventional winter wheat production system at 2.6% SOM compared to 50% lower (1.3%) and 50% higher (3.9%) SOM in Denmark by DAISY model. At 2.6% SOM, the food and fodder production was 6.49 and 6.86 t ha−1 year−1 respectively whereas carbon sequestration and soil water storage was 9.73 t ha−1 year−1 and 684 mm ha−1 year−1 respectively and nitrogen mineralisation was 83.58 kg ha−1 year−1. At 2.6% SOM, the two EF and three ES values were US$ 177 and US$ 2542 ha−1 year−1 respectively equivalent to US$ 96 and US$1370 million year−1 respectively in Denmark. The EF and ES quantities and values were positively correlated with SOM content. Hence, the quantification and valuation of EF and ES provides an empirical tool for optimising the EF and ES provision for agricultural productivity. |
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Specific Policy or Decision Context Cited
em.detail.policyDecisionContextHelp
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None given | None identified |
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Biophysical Context
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Sites up to 12 acres | Agro-ecosystem test farm, Copenhagen, Denmark. |
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EM Scenario Drivers
em.detail.scenarioDriverHelp
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Climate change scenarios | A soil organic matter value of 1.3% was used for this model run |
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EM ID
em.detail.idHelp
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EM-937 |
EM-992 |
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Method Only, Application of Method or Model Run
em.detail.methodOrAppHelp
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Method Only | Method + Application (multiple runs exist) View EM Runs |
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New or Pre-existing EM?
em.detail.newOrExistHelp
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New or revised 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
em.detail.idHelp
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EM-937 |
EM-992 |
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Document ID for related EM
em.detail.relatedEmDocumentIdHelp
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None | None |
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EM ID for related EM
em.detail.relatedEmEmIdHelp
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None | None |
EM Modeling Approach
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EM ID
em.detail.idHelp
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EM-937 |
EM-992 |
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EM Temporal Extent
em.detail.tempExtentHelp
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Not applicable | 2003-2013 |
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EM Time Dependence
em.detail.timeDependencyHelp
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time-stationary | time-dependent |
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EM Time Reference (Future/Past)
em.detail.futurePastHelp
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Not applicable | past time |
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EM Time Continuity
em.detail.continueDiscreteHelp
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Not applicable | continuous |
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EM Temporal Grain Size Value
em.detail.tempGrainSizeHelp
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Not applicable | Not applicable |
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EM Temporal Grain Size Unit
em.detail.tempGrainSizeUnitHelp
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Not applicable | Not applicable |
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EM ID
em.detail.idHelp
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EM-937 |
EM-992 |
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Bounding Type
em.detail.boundingTypeHelp
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Not applicable | Physiographic or ecological |
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Spatial Extent Name
em.detail.extentNameHelp
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Not applicable | Taastrup experimental farm |
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Spatial Extent Area (Magnitude)
em.detail.extentAreaHelp
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Not applicable | 1-10 km^2 |
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EM ID
em.detail.idHelp
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EM-937 |
EM-992 |
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EM Spatial Distribution
em.detail.distributeLumpHelp
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spatially lumped (in all cases) | other or unclear (comment) |
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Spatial Grain Type
em.detail.spGrainTypeHelp
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Not applicable | Not applicable |
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Spatial Grain Size
em.detail.spGrainSizeHelp
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Not applicable | Not applicable |
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EM ID
em.detail.idHelp
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EM-937 |
EM-992 |
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EM Computational Approach
em.detail.emComputationalApproachHelp
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Analytic | Analytic |
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EM Determinism
em.detail.deterStochHelp
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deterministic | deterministic |
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Statistical Estimation of EM
em.detail.statisticalEstimationHelp
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EM ID
em.detail.idHelp
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EM-937 |
EM-992 |
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Model Calibration Reported?
em.detail.calibrationHelp
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Not applicable | Unclear |
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Model Goodness of Fit Reported?
em.detail.goodnessFitHelp
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Not applicable | Unclear |
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Goodness of Fit (metric| value | unit)
em.detail.goodnessFitValuesHelp
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None | None |
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Model Operational Validation Reported?
em.detail.validationHelp
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Not applicable | Yes |
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Model Uncertainty Analysis Reported?
em.detail.uncertaintyAnalysisHelp
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Not applicable | Unclear |
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Model Sensitivity Analysis Reported?
em.detail.sensAnalysisHelp
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Not applicable | Unclear |
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Model Sensitivity Analysis Include Interactions?
em.detail.interactionConsiderHelp
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Not applicable | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
| EM-937 |
EM-992 |
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Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
| EM-937 |
EM-992 |
| None | None |
Centroid Lat/Long (Decimal Degree)
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EM ID
em.detail.idHelp
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EM-937 |
EM-992 |
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Centroid Latitude
em.detail.ddLatHelp
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Not applicable | 55.4 |
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Centroid Longitude
em.detail.ddLongHelp
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Not applicable | 12.18 |
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Centroid Datum
em.detail.datumHelp
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Not applicable | None provided |
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Centroid Coordinates Status
em.detail.coordinateStatusHelp
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Not applicable | Provided |
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EM ID
em.detail.idHelp
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EM-937 |
EM-992 |
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EM Environmental Sub-Class
em.detail.emEnvironmentalSubclassHelp
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Terrestrial Environment (sub-classes not fully specified) | Agroecosystems |
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Specific Environment Type
em.detail.specificEnvTypeHelp
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Terrrestrial landcover | Agroecosystems |
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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 corresponds to the Environmental Sub-class |
Scale of differentiation of organisms modeled
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EM ID
em.detail.idHelp
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EM-937 |
EM-992 |
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EM Organismal Scale
em.detail.orgScaleHelp
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Not applicable |
Guild or Assemblage ?Comment:Microbrial biomass is lumped together, but specific crops are presented. |
Taxonomic level and name of organisms or groups identified
| EM-937 |
EM-992 |
| None Available |
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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-937 |
EM-992 |
| None |
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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-937 |
EM-992 |
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