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-667 |
EM-1004 |
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EM Short Name
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Alewife derived nutrients, Connecticut, USA | GI toolkit users guide |
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EM Full Name
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Alewife derived nutrients in stream food web, Connecticut, USA | Green Infrastructure valuation toolkit users guide |
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EM Source or Collection
em.detail.emSourceOrCollectionHelp
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None | None |
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EM Source Document ID
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384 | 474 |
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Document Author
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Walters, A. W., R. T. Barnes, and D. M. Post | Genecon LLP. |
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Document Year
em.detail.documentYearHelp
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2009 | 2010 |
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Document Title
em.detail.sourceIdHelp
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Anadromous alewives (Alosa pseudoharengus) contribute marine-derived nutrients to coastal stream food webs | Building natural value for sustainable economic development The green infrastructure valuation toolkit user guide |
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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
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Published journal manuscript | Published report |
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EM ID
em.detail.idHelp
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EM-667 |
EM-1004 |
| Not applicable | https://www.merseyforest.org.uk/services/gi-val/ | |
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Contact Name
em.detail.contactNameHelp
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Annika W. Walters | The Mercey Forest |
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Contact Address
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Dept. of Ecology and Evolutionary Biology, Yale University, New Haven, CT 06511, USA | Moss Ln, Woolston, Warrington WA3 6QX, United Kingdom |
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Contact Email
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annika.walters@yale.edu | mail@merseyforest.org.uk |
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EM ID
em.detail.idHelp
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EM-667 |
EM-1004 |
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Summary Description
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ABSTRACT: "Diadromous fish are an important link between marine and freshwater food webs. Pacific salmon (Oncorhynchus spp.) strongly impact nutrient dynamics in inland waters and anadromous alewife (Alosa pseudoharengus) may play a similar ecological role along the Atlantic coast. The annual spawning migration of anadromous alewife contributes, on average, 1050 g of nitrogen and 120 g of phosphorus to Bride Brook, Connecticut, USA, through excretion and mortality each year... There was no significant effect of this nutrient influx on water chemistry, leaf decomposition, or periphyton accrual. Dam removal and fish ladder construction will allow anadromous alewife to regain access to historical freshwater spawning habitats, potentially impacting food web dynamics and nutrient cycling in coastal freshwater systems." | [The toolkit provides a very helpful introduction to the evidence demonstrating the benefits of green infrastructure interventions. It offers a structured argument that speaks the language of regeneration and economic developments. The 11 economic benefits structure provides a relatively simple high level means of presenting and communicating the benefits of green infrastructure projects in economic contexts, although it also brings some risks of double-counting (see Limitations below). The toolkit provides a structured approach to value green infrastructure benefits in monetary, quantitative and qualitative terms, with equal weight being applied to each of these three ways to present existing evidence. It can add value to and inform the decision-making process, particularly when used at an early stage to get broad brush figures and weigh pros and cons.The toolkit relies on current state-of-the-art evidence and valuation techniques for green infrastructure benefits. However, the toolkit also highlights the need for considerable improvement and expansion of the evidence base to enable future iterations to provide improved valuations. The toolkit helps make green infrastructure benefits ‘visible’ to potential funders. The inclusion of environmental benefits in cost benefit analysis is currently very difficult, often requiring professional assistance. Such assistance is frequently beyond the means of many groups seeking project funding. The toolkit is aimed at filling this gap, providing a means of scoping out the indicative benefits of green infrastructure using tools and approaches accessible to many projects and groups. However, whilst the toolkit provides a means of undertaking a broad Value for Money assessment, it must but emphasised that this is only indicative and cannot replace more rigorous formal project appraisal techniques.] |
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Specific Policy or Decision Context Cited
em.detail.policyDecisionContextHelp
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None identified | None |
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Biophysical Context
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Alewife spawning runs typically occur Mid March - May. | N/A |
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EM Scenario Drivers
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No scenarios presented | N/A |
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EM ID
em.detail.idHelp
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EM-667 |
EM-1004 |
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Method Only, Application of Method or Model Run
em.detail.methodOrAppHelp
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Method + Application (multiple runs exist) View EM Runs | Method Only |
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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-667 |
EM-1004 |
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Document ID for related EM
em.detail.relatedEmDocumentIdHelp
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Doc-383 | None |
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EM ID for related EM
em.detail.relatedEmEmIdHelp
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EM-661 | EM-665 | EM-666 | EM-672 | EM-674 | EM-673 | None |
EM Modeling Approach
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EM ID
em.detail.idHelp
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EM-667 |
EM-1004 |
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EM Temporal Extent
em.detail.tempExtentHelp
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1979-2009 | Not applicable |
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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)
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Not applicable | Not applicable |
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EM Time Continuity
em.detail.continueDiscreteHelp
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Not applicable | Not applicable |
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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-667 |
EM-1004 |
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Bounding Type
em.detail.boundingTypeHelp
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Watershed/Catchment/HUC | Not applicable |
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Spatial Extent Name
em.detail.extentNameHelp
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Bride Brook | Not applicable |
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Spatial Extent Area (Magnitude)
em.detail.extentAreaHelp
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1-10 ha | Not applicable |
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EM ID
em.detail.idHelp
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EM-667 |
EM-1004 |
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EM Spatial Distribution
em.detail.distributeLumpHelp
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spatially lumped (in all cases) | spatially distributed (in at least some cases) |
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Spatial Grain Type
em.detail.spGrainTypeHelp
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Not applicable | area, for pixel or radial feature |
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Spatial Grain Size
em.detail.spGrainSizeHelp
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Not applicable | Not reported |
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EM ID
em.detail.idHelp
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EM-667 |
EM-1004 |
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EM Computational Approach
em.detail.emComputationalApproachHelp
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Analytic | Numeric |
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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-667 |
EM-1004 |
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Model Calibration Reported?
em.detail.calibrationHelp
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Yes ?Comment:The fish counter (for alewife numbers) was calibrated. |
Not applicable |
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Model Goodness of Fit Reported?
em.detail.goodnessFitHelp
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No | Not applicable |
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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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No | Not applicable |
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Model Uncertainty Analysis Reported?
em.detail.uncertaintyAnalysisHelp
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No | Not applicable |
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Model Sensitivity Analysis Reported?
em.detail.sensAnalysisHelp
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No | Not applicable |
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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])
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EM-667 |
EM-1004 |
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None |
Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
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EM-667 |
EM-1004 |
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None |
Centroid Lat/Long (Decimal Degree)
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EM ID
em.detail.idHelp
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EM-667 |
EM-1004 |
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Centroid Latitude
em.detail.ddLatHelp
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41.32 | Not applicable |
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Centroid Longitude
em.detail.ddLongHelp
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-72.24 | Not applicable |
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Centroid Datum
em.detail.datumHelp
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WGS84 | Not applicable |
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Centroid Coordinates Status
em.detail.coordinateStatusHelp
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Provided | Not applicable |
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EM ID
em.detail.idHelp
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EM-667 |
EM-1004 |
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EM Environmental Sub-Class
em.detail.emEnvironmentalSubclassHelp
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Rivers and Streams | Not applicable |
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Specific Environment Type
em.detail.specificEnvTypeHelp
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Coastal stream | Multiple |
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EM Ecological Scale
em.detail.ecoScaleHelp
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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
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EM ID
em.detail.idHelp
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EM-667 |
EM-1004 |
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EM Organismal Scale
em.detail.orgScaleHelp
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Individual or population, within a species | Not applicable |
Taxonomic level and name of organisms or groups identified
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EM-667 |
EM-1004 |
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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)
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EM-667 |
EM-1004 |
| None | 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)
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EM-667 |
EM-1004 |
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None |
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