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-260 |
EM-697 ![]() |
EM Short Name
em.detail.shortNameHelp
?
|
Coral taxa and land development, St.Croix, VI, USA | Floral resources on landfill sites, United Kingdom |
EM Full Name
em.detail.fullNameHelp
?
|
Coral taxa richness and land development, St.Croix, Virgin Islands, USA | Floral resources on landfill sites, East Midlands, United Kingdom |
EM Source or Collection
em.detail.emSourceOrCollectionHelp
?
|
US EPA | None |
EM Source Document ID
|
96 | 389 |
Document Author
em.detail.documentAuthorHelp
?
|
Oliver, L. M., Lehrter, J. C. and Fisher, W. S. | Tarrant S., J. Ollerton, M. L Rahman, J. Tarrant, and D. McCollin |
Document Year
em.detail.documentYearHelp
?
|
2011 | 2013 |
Document Title
em.detail.sourceIdHelp
?
|
Relating landscape development intensity to coral reef condition in the watersheds of St. Croix, US Virgin Islands | Grassland restoration on landfill sites in the East Midlands, United Kingdom: An evaluation of floral resources and pollinating insects |
Document Status
em.detail.statusCategoryHelp
?
|
Peer reviewed and published | Peer reviewed and published |
Comments on Status
em.detail.commentsOnStatusHelp
?
|
Published journal manuscript | Published journal manuscript |
EM ID
em.detail.idHelp
?
|
EM-260 |
EM-697 ![]() |
Not applicable | Not applicable | |
Contact Name
em.detail.contactNameHelp
?
|
Leah Oliver | Sam Tarrant |
Contact Address
|
National Health and Environmental Research Effects Laboratory | RSPB UK Headquarters, The Lodge, Sandy, Bedfordshire SG19 2DL, U.K. |
Contact Email
|
leah.oliver@epa.gov | sam.tarrant@rspb.org.uk |
EM ID
em.detail.idHelp
?
|
EM-260 |
EM-697 ![]() |
Summary Description
em.detail.summaryDescriptionHelp
?
|
AUTHOR'S DESCRIPTION: "In this exploratory comparison, stony coral condition was related to watershed LULC and LDI values. We also compared the capacity of other potential human activity indicators to predict coral reef condition using multivariate analysis." (294) | ABSTRACT: "...Restored landfill sites are a significant potential reserve of semi-natural habitat, so their conservation value for supporting populations of pollinating insects was here examined by assessing whether the plant and pollinator assemblages of restored landfill sites are comparable to reference sites of existing wildlife value. Floral characteristics of the vegetation and the species richness and abundance of flower-visiting insect assemblages were compared between nine pairs of restored landfill sites and reference sites in the East Midlands of the United Kingdom, using standardized methods over two field seasons. …" AUTHOR'S DESCRIPTION: "The selection criteria for the landfill sites were greater than or equal to 50% of the site restored (to avoid undue influence from ongoing landfilling operations), greater than or equal to 0.5 ha in area and restored for greater than or equal to 4 years to allow establishment of vegetation. Comparison reference sites were the closest grassland sites of recognized nature conservation value, being designated as either Local Nature Reserves (LNRs) or Sites of Special Scientific Interest (SSSI)…All sites were surveyed three times each during the fieldwork season, in Spring, Summer, and Autumn. Paired sites were sampled on consecutive days whenever weather conditions permitted to reduce temporal bias. Standardized plant surveys were used (Dicks et al. 2002; Potts et al. 2006). Transects (100 × 2m) were centered from the approximate middle of the site and orientated using randomized bearing tables. All flowering plants were identified to species level… A “floral cover” method to represent available floral resources was used which combines floral abundance with inflorescence size. Mean area of the floral unit from above was measured for each flowering plant species and then multiplied by their frequencies." "Insect pollinated flowering plant species composition and floral abundance between sites by type were represented by non-metric multidimensional scaling (NMDS)...This method is sensitive to showing outliers and the distance between points shows the relative similarity (McCune & Grace 2002; Ollerton et al. 2009)." (This data is not entered into ESML) |
Specific Policy or Decision Context Cited
em.detail.policyDecisionContextHelp
?
|
Not applicable | None identified |
Biophysical Context
|
nearshore; <1.5 km offshore; <12 m depth | No additional description provided |
EM Scenario Drivers
em.detail.scenarioDriverHelp
?
|
Not applicable | No scenarios presented |
EM ID
em.detail.idHelp
?
|
EM-260 |
EM-697 ![]() |
Method Only, Application of Method or Model Run
em.detail.methodOrAppHelp
?
|
Method + Application | Method + Application (multiple runs exist) View EM Runs |
New or Pre-existing EM?
em.detail.newOrExistHelp
?
|
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-260 |
EM-697 ![]() |
Document ID for related EM
em.detail.relatedEmDocumentIdHelp
?
|
None | None |
EM ID for related EM
em.detail.relatedEmEmIdHelp
?
|
None | EM-709 |
EM Modeling Approach
EM ID
em.detail.idHelp
?
|
EM-260 |
EM-697 ![]() |
EM Temporal Extent
em.detail.tempExtentHelp
?
|
2006-2007 | 2007-2008 |
EM Time Dependence
em.detail.timeDependencyHelp
?
|
time-stationary | time-stationary |
EM Time Reference (Future/Past)
em.detail.futurePastHelp
?
|
Not applicable | Not applicable |
EM Time Continuity
em.detail.continueDiscreteHelp
?
|
Not applicable | Not applicable |
EM Temporal Grain Size Value
em.detail.tempGrainSizeHelp
?
|
Not applicable | Not applicable |
EM Temporal Grain Size Unit
em.detail.tempGrainSizeUnitHelp
?
|
Not applicable | Not applicable |
EM ID
em.detail.idHelp
?
|
EM-260 |
EM-697 ![]() |
Bounding Type
em.detail.boundingTypeHelp
?
|
Physiographic or Ecological | Multiple unrelated locations (e.g., meta-analysis) |
Spatial Extent Name
em.detail.extentNameHelp
?
|
St.Croix, U.S. Virgin Islands | East Midlands |
Spatial Extent Area (Magnitude)
em.detail.extentAreaHelp
?
|
10-100 km^2 | 1000-10,000 km^2. |
EM ID
em.detail.idHelp
?
|
EM-260 |
EM-697 ![]() |
EM Spatial Distribution
em.detail.distributeLumpHelp
?
|
spatially lumped (in all cases) | spatially distributed (in at least some cases) |
Spatial Grain Type
em.detail.spGrainTypeHelp
?
|
Not applicable | other (specify), for irregular (e.g., stream reach, lake basin) |
Spatial Grain Size
em.detail.spGrainSizeHelp
?
|
Not applicable | multiple unrelated locations |
EM ID
em.detail.idHelp
?
|
EM-260 |
EM-697 ![]() |
EM Computational Approach
em.detail.emComputationalApproachHelp
?
|
Analytic | Analytic |
EM Determinism
em.detail.deterStochHelp
?
|
deterministic | deterministic |
Statistical Estimation of EM
em.detail.statisticalEstimationHelp
?
|
|
|
EM ID
em.detail.idHelp
?
|
EM-260 |
EM-697 ![]() |
Model Calibration Reported?
em.detail.calibrationHelp
?
|
Yes | Not applicable |
Model Goodness of Fit Reported?
em.detail.goodnessFitHelp
?
|
Yes | Not applicable |
Goodness of Fit (metric| value | unit)
em.detail.goodnessFitValuesHelp
?
|
|
None |
Model Operational Validation Reported?
em.detail.validationHelp
?
|
No | Not applicable |
Model Uncertainty Analysis Reported?
em.detail.uncertaintyAnalysisHelp
?
|
Yes | Not applicable |
Model Sensitivity Analysis Reported?
em.detail.sensAnalysisHelp
?
|
No | Not applicable |
Model Sensitivity Analysis Include Interactions?
em.detail.interactionConsiderHelp
?
|
Not applicable | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
EM-260 |
EM-697 ![]() |
None |
|
Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
EM-260 |
EM-697 ![]() |
|
None |
Centroid Lat/Long (Decimal Degree)
EM ID
em.detail.idHelp
?
|
EM-260 |
EM-697 ![]() |
Centroid Latitude
em.detail.ddLatHelp
?
|
17.75 | 52.22 |
Centroid Longitude
em.detail.ddLongHelp
?
|
-64.75 | -0.91 |
Centroid Datum
em.detail.datumHelp
?
|
NAD83 | WGS84 |
Centroid Coordinates Status
em.detail.coordinateStatusHelp
?
|
Estimated | Estimated |
EM ID
em.detail.idHelp
?
|
EM-260 |
EM-697 ![]() |
EM Environmental Sub-Class
em.detail.emEnvironmentalSubclassHelp
?
|
Near Coastal Marine and Estuarine | Created Greenspace | Grasslands |
Specific Environment Type
em.detail.specificEnvTypeHelp
?
|
stony coral reef | restored landfills and grasslands |
EM Ecological Scale
em.detail.ecoScaleHelp
?
|
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
EM ID
em.detail.idHelp
?
|
EM-260 |
EM-697 ![]() |
EM Organismal Scale
em.detail.orgScaleHelp
?
|
Guild or Assemblage | Individual or population, within a species |
Taxonomic level and name of organisms or groups identified
EM-260 |
EM-697 ![]() |
|
|
EnviroAtlas URL
EM-260 |
EM-697 ![]() |
None Available | GAP Ecological Systems |
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-260 |
EM-697 ![]() |
|
|
<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-260 |
EM-697 ![]() |
|
None |