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-137 | EM-154 | EM-260 |
EM Short Name
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i-Tree Hydro v4.0 | Mangrove development, Tampa Bay, FL, USA | Coral taxa and land development, St.Croix, VI, USA |
EM Full Name
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i-Tree Hydro v4.0 (default data option) | Mangrove wetland development, Tampa Bay, FL, USA | Coral taxa richness and land development, St.Croix, Virgin Islands, USA |
EM Source or Collection
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i-Tree | USDA Forest Service | US EPA | US EPA |
EM Source Document ID
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198 | 97 | 96 |
Document Author
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USDA Forest Service | Osland, M. J., Spivak, A. C., Nestlerode, J. A., Lessmann, J. M., Almario, A. E., Heitmuller, P. T., Russell, M. J., Krauss, K. W., Alvarez, F., Dantin, D. D., Harvey, J. E., From, A. S., Cormier, N. and Stagg, C.L. | Oliver, L. M., Lehrter, J. C. and Fisher, W. S. |
Document Year
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Not Reported | 2012 | 2011 |
Document Title
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i-Tree Hydro User's Manual v. 4.0 | Ecosystem development after mangrove wetland creation: plant–soil change across a 20-year chronosequence | Relating landscape development intensity to coral reef condition in the watersheds of St. Croix, US Virgin Islands |
Document Status
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Peer reviewed and published | Peer reviewed and published | Peer reviewed and published |
Comments on Status
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Webpage | Published journal manuscript | Published journal manuscript |
EM ID
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EM-137 | EM-154 | EM-260 |
http://www.itreetools.org | Not applicable | Not applicable | |
Contact Name
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Not applicable | Michael Osland | Leah Oliver |
Contact Address
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Not applicable | U.S. Environmental Protection Agency, Gulf Ecology Division, gulf Breeze, FL 32561 | National Health and Environmental Research Effects Laboratory |
Contact Email
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Not applicable | mosland@usgs.gov | leah.oliver@epa.gov |
EM ID
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EM-137 | EM-154 | EM-260 |
Summary Description
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ABSTRACT: "i-Tree Hydro is the first urban hydrology model that is specifically designed to model vegetation effects and to be calibrated against measured stream flow data. It is designed to model the effects of changes in urban tree cover and impervious surfaces on hourly stream flows and water quality at the watershed level." AUTHOR'S DESCRIPTION: "The purpose of i-Tree Hydro is to simulate hourly changes in stream flow (and water quality) given changes in tree and impervious cover in the watershed. The following is an overview of the process: 1) Determine your watershed of analysis and stream gauge station. i-Tree Hydro works on a watershed basis with the watershed determined as the total drainage area upstream from a measured stream gauge. Stream gauge availability varies. 2) Download national digital elevation data. Once the area and location of the watershed are known, digital elevation data are downloaded from the USGS for an area that encompasses the entire watershed. ArcGIS software is then used to create a digital elevation map and to determine the exact boundary for the watershed upstream from the gauge station location. 3) Determine cover attributes of the watershed and gather other required data. i-Tree Canopy and other sources can be used to determine the tree cover, shrub cover, impervious surface and other cover types. Information about other aspects of the watershed such as proportion of evergreen trees and shrubs, leaf area index, and a variety of hydrologic parameters must be collected. 4) Get started with Hydro. Once these input data are ready, they are loaded into Hydro to begin analysis. 5) Calibrate the model. The Hydro model contains an auto-calibration routine that tries to find the best fit between the stream flow predicted by the model and the stream flow measured at the stream gauge station given the various inputs. The model can also be manually calibrated to improve the fit by changing the parameters as needed. 6) Model new scenarios: Once the model is properly calibrated, tree and impervious cover parameters can be changed to illustrate the impact on stream flow and water quality." | ABSTRACT: "Mangrove wetland restoration and creation effortsare increasingly proposed as mechanisms to compensate for mangrove wetland losses. However, ecosystem development and functional equivalence in restored and created mangrove wetlands are poorly understood. We compared a 20-year chronosequence of created tidal wetland sites in Tampa Bay, Florida (USA) to natural reference mangrove wetlands. Across the chronosequence, our sites represent the succession from salt marsh to mangrove forest communities. Our results identify important soil and plant structural differences between the created and natural reference wetland sites; however, they also depict a positive developmental trajectory for the created wetland sites that reflects tightly coupled plant-soil development. Because upland soils and/or dredge spoils were used to create the new mangrove habitats, the soils at younger created sites and at lower depths (10–30 cm) had higher bulk densities, higher sand content, lower soil organic matter (SOM), lower total carbon (TC), and lower total nitrogen (TN) than did natural reference wetland soils. However, in the upper soil layer (0–10 cm), SOM, TC, and TN increased with created wetland site age simultaneously with mangrove forest growth. The rate of created wetland soil C accumulation was comparable to literature values for natural mangrove wetlands. Notably, the time to equivalence for the upper soil layer of created mangrove wetlands appears to be faster than for many other wetland ecosystem types. Collectively, our findings characterize the rate and trajectory of above- and below-ground changes associated with ecosystem development in created mangrove wetlands; this is valuable information for environmental managers planning to sustain existing mangrove wetlands or mitigate for mangrove wetland losses." | 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) |
Specific Policy or Decision Context Cited
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None identified | Not applicable | Not applicable |
Biophysical Context
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No additional description provided | mangrove forest,Salt marsh, estuary, sea level, | nearshore; <1.5 km offshore; <12 m depth |
EM Scenario Drivers
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No scenarios presented | Not applicable | Not applicable |
EM ID
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EM-137 | EM-154 | EM-260 |
Method Only, Application of Method or Model Run
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Method Only | Method + Application | Method + Application |
New or Pre-existing EM?
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New or revised model | New or revised 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-137 | EM-154 | EM-260 |
Document ID for related EM
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Doc-190 | Doc-223 | None | None |
EM ID for related EM
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EM-109 | EM-142 | EM-51 | None | None |
EM Modeling Approach
EM ID
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EM-137 | EM-154 | EM-260 |
EM Temporal Extent
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Not applicable | 1990-2010 | 2006-2007 |
EM Time Dependence
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time-dependent | time-dependent | time-stationary |
EM Time Reference (Future/Past)
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Not applicable | future time | Not applicable |
EM Time Continuity
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discrete | continuous | Not applicable |
EM Temporal Grain Size Value
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1 | Not applicable | Not applicable |
EM Temporal Grain Size Unit
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Hour | Not applicable | Not applicable |
EM ID
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EM-137 | EM-154 | EM-260 |
Bounding Type
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Not applicable | Physiographic or Ecological | Physiographic or Ecological |
Spatial Extent Name
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Not applicable | Tampa Bay | St.Croix, U.S. Virgin Islands |
Spatial Extent Area (Magnitude)
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Not applicable | 100-1000 km^2 | 10-100 km^2 |
EM ID
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EM-137 | EM-154 | EM-260 |
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) |
Spatial Grain Type
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area, for pixel or radial feature | area, for pixel or radial feature | Not applicable |
Spatial Grain Size
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30 x 30 m | m^2 | Not applicable |
EM ID
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EM-137 | EM-154 | EM-260 |
EM Computational Approach
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Numeric | 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-137 | EM-154 | EM-260 |
Model Calibration Reported?
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Not applicable | No | Yes |
Model Goodness of Fit Reported?
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Not applicable | No | Yes |
Goodness of Fit (metric| value | unit)
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None | None |
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Model Operational Validation Reported?
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Not applicable | No | No |
Model Uncertainty Analysis Reported?
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Not applicable | Yes | Yes |
Model Sensitivity Analysis Reported?
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Not applicable | Yes | No |
Model Sensitivity Analysis Include Interactions?
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Not applicable | No | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
EM-137 | EM-154 | EM-260 |
None |
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None |
Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
EM-137 | EM-154 | EM-260 |
None |
Comment:Realm: Tropical Atlantic Region: West Tropical Atlantic Province: Tropical Northwestern Atlantic Ecoregion: Floridian |
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Centroid Lat/Long (Decimal Degree)
EM ID
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EM-137 | EM-154 | EM-260 |
Centroid Latitude
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-9999 | 27.8 | 17.75 |
Centroid Longitude
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-9999 | -82.4 | -64.75 |
Centroid Datum
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Not applicable | WGS84 | NAD83 |
Centroid Coordinates Status
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Not applicable | Estimated | Estimated |
EM ID
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EM-137 | EM-154 | EM-260 |
EM Environmental Sub-Class
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Rivers and Streams | Ground Water | Created Greenspace | Near Coastal Marine and Estuarine | Near Coastal Marine and Estuarine |
Specific Environment Type
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Urban watersheds | Created Mangrove wetlands | stony coral reef |
EM Ecological Scale
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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
EM ID
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EM-137 | EM-154 | EM-260 |
EM Organismal Scale
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Community | Not applicable | Guild or Assemblage |
Taxonomic level and name of organisms or groups identified
EM-137 | EM-154 | EM-260 |
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-137 | EM-154 | EM-260 |
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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-137 | EM-154 | EM-260 |
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