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
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EM-24 | EM-131 |
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EM Short Name
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i-Tree Eco: Carbon storage & sequestration, USA | InVEST marine water quality, Hood Canal, WA, USA |
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EM Full Name
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i-Tree Eco carbon storage and sequestration (trees), USA | InVEST (Integrated Valuation of Envl. Services and Tradeoffs) marine water quality, Hood Canal, WA, USA |
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EM Source or Collection
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i-Tree | USDA Forest Service | InVEST |
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EM Source Document ID
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195 | 205 |
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Document Author
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Nowak, D. J., Greenfield, E. J., Hoehn, R. E. and Lapoint, E. | Toft, J. E., Burke, J. L., Carey, M. P., Kim, C. K., Marsik, M., Sutherland, D. A., Arkema, K. K., Guerry, A. D., Levin, P. S., Minello, T. J., Plummer, M., Ruckelshaus, M. H., and Townsend, H. M. |
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Document Year
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2013 | 2013 |
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Document Title
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Carbon storage and sequestration by trees in urban and community areas of the United States | From mountains to sound: modelling the sensitivity of dungeness crab and Pacific oyster to land–sea interactions in Hood Canal,WA |
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Document Status
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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 journal manuscript |
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EM ID
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EM-24 | EM-131 |
| Not applicable | https://www.naturalcapitalproject.org/invest/ | |
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Contact Name
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David J. Nowak | J.E. Toft |
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Contact Address
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USDA Forest Service, Northern Research Station, Syracuse, NY 13210, USA | Not reported |
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Contact Email
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dnowak@fs.fed.us | jetoft@stanford.edu |
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EM ID
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EM-24 | EM-131 |
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Summary Description
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ABSTRACT: "Carbon storage and sequestration by urban trees in the United States was quantified to assess the magnitude and role of urban forests in relation to climate change. Urban tree field data from 28 cities and 6 states were used to determine the average carbon density per unit of tree cover. These data were applied to statewide urban tree cover measurements to determine total urban forest carbon storage and annual sequestration by state and nationally. Urban whole tree carbon storage densities average 7.69 kg C m^2 of tree cover and sequestration densities average 0.28 kg C m^2 of tree cover per year. Total tree carbon storage in U.S. urban areas (c. 2005) is estimated at 643 million tonnes ($50.5 billion value; 95% CI = 597 million and 690 million tonnes) and annual sequestration is estimated at 25.6 million tonnes ($2.0 billion value; 95% CI = 23.7 million to 27.4 million tonnes)." | Marine Water Quality Model. Please note: This ESML entry describes a specific, published application of an InVEST model. Different versions (e.g. different tiers) or more recent versions of this model may be available at the InVEST website. AUTHOR'S DESCRIPTION: "We used outputs from the freshwater models as inputs to the marine water quality model.We adapted a box model that has been successfully applied in Puget Sound (Babson et al., 2006; Sutherland et al., 2011) to simulate seasonal and interannual variations in salinity, water temperature, and nitrates in the Canal." (p. 4) |
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Specific Policy or Decision Context Cited
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Not reported | Land use change |
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Biophysical Context
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Urban areas 3.0% of land in U.S. and Urban/community land (5.3%) in 2000. | No additional description provided |
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EM Scenario Drivers
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No scenarios presented | future land use and land cover; Climate change |
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EM ID
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EM-24 | EM-131 |
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Method Only, Application of Method or Model Run
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Method + Application | Method + Application (multiple runs exist) |
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New or Pre-existing EM?
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Application of existing model | Application of existing 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-24 | EM-131 |
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Document ID for related EM
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None | None |
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EM ID for related EM
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None | None |
EM Modeling Approach
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EM ID
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EM-24 | EM-131 |
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EM Temporal Extent
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1989-2010 | varies by run, see runs for values |
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EM Time Dependence
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time-dependent | time-stationary |
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EM Time Reference (Future/Past)
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future time | Not applicable |
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EM Time Continuity
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discrete | Not applicable |
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EM Temporal Grain Size Value
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1 | Not applicable |
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EM Temporal Grain Size Unit
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Year | Not applicable |
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EM ID
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EM-24 | EM-131 |
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Bounding Type
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Geopolitical | Physiographic or ecological |
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Spatial Extent Name
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United States | Hood Canal |
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Spatial Extent Area (Magnitude)
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>1,000,000 km^2 | 100-1000 km^2 |
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EM ID
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EM-24 | EM-131 |
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EM Spatial Distribution
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spatially distributed (in at least some cases) | spatially distributed (in at least some cases) |
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Spatial Grain Type
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area, for pixel or radial feature | other (specify), for irregular (e.g., stream reach, lake basin) |
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Spatial Grain Size
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1 m^2 | Not reported |
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EM ID
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EM-24 | EM-131 |
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EM Computational Approach
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Numeric | Analytic |
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EM Determinism
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deterministic | deterministic |
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Statistical Estimation of EM
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EM ID
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EM-24 | EM-131 |
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Model Calibration Reported?
em.detail.calibrationHelp
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No | No |
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Model Goodness of Fit Reported?
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No | No |
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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 | No |
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Model Uncertainty Analysis Reported?
em.detail.uncertaintyAnalysisHelp
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Yes ?Comment:An error of sampling was reported, but not an error of estimation Estimation error was unknown and reported as likely larger than the error of sampling. |
No |
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Model Sensitivity Analysis Reported?
em.detail.sensAnalysisHelp
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No | No |
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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-24 | EM-131 |
Comment:EM presents carbon storage and sequestration rates for country and by individual state |
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Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
| EM-24 | EM-131 |
| None |
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Centroid Lat/Long (Decimal Degree)
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EM ID
em.detail.idHelp
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EM-24 | EM-131 |
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Centroid Latitude
em.detail.ddLatHelp
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40.16 | 47.8 |
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Centroid Longitude
em.detail.ddLongHelp
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-99.79 | -122.7 |
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Centroid Datum
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WGS84 | NAD83 |
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Centroid Coordinates Status
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Estimated | Estimated |
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EM ID
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EM-24 | EM-131 |
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EM Environmental Sub-Class
em.detail.emEnvironmentalSubclassHelp
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Forests | Created Greenspace | Near Coastal Marine and Estuarine |
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Specific Environment Type
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Urban forests | glacier-carver saltwater fjord |
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EM Ecological Scale
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Zone within an ecosystem | 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-24 | EM-131 |
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EM Organismal Scale
em.detail.orgScaleHelp
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Species ?Comment:Trees were identified to species for the differential growth and biomass estimates part of the analysis. |
Not applicable |
Taxonomic level and name of organisms or groups identified
| EM-24 | EM-131 |
| None Available | None Available |
EnviroAtlas URL
| EM-24 | EM-131 |
| GAP Ecological Systems, Average Annual Precipitation | None Available |
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-24 | EM-131 |
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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-24 | EM-131 |
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