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
EM ID
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EM-65 | EM-185 | EM-684 |
EM Short Name
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Green biomass production, Central French Alps | Blue crabs and SAV, Chesapeake Bay, USA | Beach visitation, Barnstable, MA, USA |
EM Full Name
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Green biomass production, Central French Alps | Blue crabs and submerged aquatic vegetation interaction, Chesapeake Bay, USA | Beach visitation, Barnstable, Massachusetts, USA |
EM Source or Collection
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EU Biodiversity Action 5 | None | US EPA |
EM Source Document ID
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260 |
292 ?Comment:Conference paper |
386 |
Document Author
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Lavorel, S., Grigulis, K., Lamarque, P., Colace, M-P, Garden, D., Girel, J., Pellet, G., and Douzet, R. | Mykoniatis, N. and Ready, R. | Lyon, Sarina F., Nathaniel H. Merrill, Kate K. Mulvaney, and Marisa J. Mazzotta |
Document Year
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2011 | 2013 | 2018 |
Document Title
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Using plant functional traits to understand the landscape distribution of multiple ecosystem services | Evaluating habitat-fishery interactions: The case of submerged aquatic vegetation and blue crab fishery in the Chesapeake Bay | Valuing coastal beaches and closures using benefit transfer: An application to Barnstable, Massachusetts |
Document Status
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Peer reviewed and published | Not formally documented | Peer reviewed and published |
Comments on Status
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Published journal manuscript | Conference proceedings | Published journal manuscript |
EM ID
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EM-65 | EM-185 | EM-684 |
Not applicable | Not applicable | Not applicable | |
Contact Name
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Sandra Lavorel | Nikolaos Mykoniatis | Kate K, Mulvaney |
Contact Address
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Laboratoire d’Ecologie Alpine, UMR 5553 CNRS Université Joseph Fourier, BP 53, 38041 Grenoble Cedex 9, France | Department of Agricultural Economics, Sociology and Education The Pennsylvania State University | Not reported |
Contact Email
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sandra.lavorel@ujf-grenoble.fr | Not reported | Mulvaney.Kate@EPA.gov |
EM ID
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EM-65 | EM-185 | EM-684 |
Summary Description
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ABSTRACT: "Here, we propose a new approach for the analysis, mapping and understanding of multiple ES delivery in landscapes. Spatially explicit single ES models based on plant traits and abiotic characteristics are combined to identify ‘hot’ and ‘cold’ spots of multiple ES delivery, and the land use and biotic determinants of such distributions. We demonstrate the value of this trait-based approach as compared to a pure land-use approach for a pastoral landscape from the central French Alps, and highlight how it improves understanding of ecological constraints to, and opportunities for, the delivery of multiple services. Vegetative height and leaf traits such as leaf dry matter content were response traits strongly influenced by land use and abiotic environment, with follow-on effects on several ecosystem properties (e.g., green biomass production), and could therefore be used as functional markers of ES." AUTHOR'S DESCRIPTION: "Variation in green biomass production was modelled using…traits community-weighted mean (CWM) and functional divergence (FD) and abiotic variables (continuous variables; trait + abiotic) following Diaz et al. (2007). …The comparison between this model and the land-use alone model identifies the need for site-based information beyond a land use or land cover proxy, and the comparison with the land use + abiotic model assesses the value of additional ecological (trait) information…Green biomass production for each pixel was calculated and mapped using model estimates for…regression coefficients on abiotic variables and traits. For each pixel these calculations were applied to mapped estimates of abiotic variables and trait CWM and FD. This step is critically novel as compared to a direct application of the model by Diaz et al. (2007) in that we explicitly modelled the responses of trait community-weighted means and functional divergences to environment prior to evaluating their effects on ecosystem properties. Such an approach is the key to the explicit representation of functional variation across the landscape, as opposed to the use of unique trait values within each land use (see Albert et al. 2010)." | ABSTRACT: "This paper investigates habitat-fisheries interaction between two important resources in the Chesapeake Bay: blue crabs and Submerged Aquatic Vegetation (SAV). A habitat can be essential to a species (the species is driven to extinction without it), facultative (more habitat means more of the species, but species can exist at some level without any of the habitat) or irrelevant (more habitat is not associated with more of the species). An empirical bioeconomic model that nests the essential-habitat model into its facultative-habitat counterpart is estimated. Two alternative approaches are used to test whether SAV matters for the crab stock. Our results indicate that, if we do not have perfect information on habitat-fisheries linkages, the right approach would be to run the more general facultative-habitat model instead of the essential- habitat one." | ABSTRACT: "Each year, millions of Americans visit beaches for recreation, resulting in significant social welfare benefits and economic activity. Considering the high use of coastal beaches for recreation, closures due to bacterial contamination have the potential to greatly impact coastal visitors and communities. We used readily-available information to develop two transferable models that, together, provide estimates for the value of a beach day as well as the lost value due to a beach closure. We modeled visitation for beaches in Barnstable, Massachusetts on Cape Cod through panel regressions to predict visitation by type of day, for the season, and for lost visits when a closure was posted. We used a meta-analysis of existing studies conducted throughout the United States to estimate a consumer surplus value of a beach visit of around $22 for our study area, accounting for water quality at beaches by using past closure history. We applied this value through a benefit transfer to estimate the value of a beach day, and combined it with lost town revenue from parking to estimate losses in the event of a closure. The results indicate a high value for beaches as a public resource and show significant losses to the town when beaches are closed due to an exceedance in bacterial concentrations." AUTHOR'S DESCRIPTION: "...We needed beach visitation estimates to assess the number of people who would be impacted by beach closures. We modeled visits by combining daily parking counts with other factors that help explain variations in attendance, including weather, day of the week or point within a season, and physical differences in sites (Kreitler et al. 2013). We designed the resulting model to estimate visitation for uncounted days as well as for beaches without counts on a given day. When combined with estimates of value per day, the visitation model can be used to value a lost beach day while accounting for beach size, time of season, and other factors...Since our count data of visitation for all four beaches are relatively large numbers (mean = 490, SD = 440), we used a log-linear regression model as opposed to a count data model. We selected a random effects model to account for time invariant variables such as parking spaces, modeling differences across beaches based on this variable…" Equation 2, page 15, provides the econometric regression. |
Specific Policy or Decision Context Cited
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None identified | Not applicable | To assess the number of people who would be impacted by beach closures. |
Biophysical Context
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Elevation ranges from 1552 to 2442 m, on predominately south-facing slopes | Submerged Aquatic Vegetation (SAV), eelgrass | Four separate beaches within the community of Barnstable |
EM Scenario Drivers
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No scenarios presented | Essential or Facultative habitat | No scenarios presented |
EM ID
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EM-65 | EM-185 | EM-684 |
Method Only, Application of Method or Model Run
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Method + Application | Method + Application | Method + Application |
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
EM ID
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EM-65 | EM-185 | EM-684 |
Document ID for related EM
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Doc-260 | Doc-227 | Doc-386 | Doc-387 |
EM ID for related EM
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EM-66 | EM-68 | EM-69 | EM-70 | EM-71 | EM-79 | EM-80 | EM-81 | EM-82 | EM-83 | EM-106 | EM-682 | EM-685 | EM-683 | EM-686 |
EM Modeling Approach
EM ID
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EM-65 | EM-185 | EM-684 |
EM Temporal Extent
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2007-2009 | 1993-2011 | 2011 - 2016 |
EM Time Dependence
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time-stationary | time-dependent | time-dependent |
EM Time Reference (Future/Past)
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Not applicable | past time | past time |
EM Time Continuity
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Not applicable | discrete | discrete |
EM Temporal Grain Size Value
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Not applicable | 1 | 1 |
EM Temporal Grain Size Unit
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Not applicable | Year | Day |
EM ID
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EM-65 | EM-185 | EM-684 |
Bounding Type
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Physiographic or Ecological | Physiographic or ecological | Physiographic or ecological |
Spatial Extent Name
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Central French Alps | Chesapeake Bay | Barnstable beaches (Craigville Beach, Kalmus Beach, Keyes Memorial Beach, and Veteran’s Park Beach) |
Spatial Extent Area (Magnitude)
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10-100 km^2 | 10,000-100,000 km^2 | 10-100 ha |
EM ID
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EM-65 | EM-185 | EM-684 |
EM Spatial Distribution
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spatially distributed (in at least some cases) | spatially lumped (in all cases) | spatially distributed (in at least some cases) |
Spatial Grain Type
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area, for pixel or radial feature | Not applicable | length, for linear feature (e.g., stream mile) |
Spatial Grain Size
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20 m x 20 m | Not applicable | by beach site |
EM ID
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EM-65 | EM-185 | EM-684 |
EM Computational Approach
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Analytic | Analytic | Analytic |
EM Determinism
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deterministic | deterministic | deterministic |
Statistical Estimation of EM
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EM ID
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EM-65 | EM-185 | EM-684 |
Model Calibration Reported?
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No | Yes | Yes |
Model Goodness of Fit Reported?
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Yes | Yes | No |
Goodness of Fit (metric| value | unit)
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None | None |
Model Operational Validation Reported?
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Yes | Yes | No |
Model Uncertainty Analysis Reported?
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No | Yes | No |
Model Sensitivity Analysis Reported?
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No | Yes | Yes |
Model Sensitivity Analysis Include Interactions?
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Not applicable | Yes | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
EM-65 | EM-185 | EM-684 |
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Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
EM-65 | EM-185 | EM-684 |
None |
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Centroid Lat/Long (Decimal Degree)
EM ID
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EM-65 | EM-185 | EM-684 |
Centroid Latitude
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45.05 | 36.99 | 41.64 |
Centroid Longitude
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6.4 | -75.95 | -70.29 |
Centroid Datum
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WGS84 | WGS84 | WGS84 |
Centroid Coordinates Status
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Provided | Estimated | Estimated |
EM ID
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EM-65 | EM-185 | EM-684 |
EM Environmental Sub-Class
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Agroecosystems | Grasslands | None | Near Coastal Marine and Estuarine |
Specific Environment Type
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Subalpine terraces, grasslands, and meadows | Yes | Saltwater beach |
EM Ecological Scale
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Not applicable | Yes | Ecological scale corresponds to the Environmental Sub-class |
Scale of differentiation of organisms modeled
EM ID
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EM-65 | EM-185 | EM-684 |
EM Organismal Scale
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Community | Yes | Not applicable |
Taxonomic level and name of organisms or groups identified
EM-65 | EM-185 | EM-684 |
None Available | None Available | None Available |
EnviroAtlas URL
EM-65 | EM-185 | EM-684 |
GAP Ecological Systems | None Available | Average Annual Precipitation |
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-65 | EM-185 | EM-684 |
None | 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-65 | EM-185 | EM-684 |
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None |
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