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-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
EM Short Name
em.detail.shortNameHelp
?
|
EnviroAtlas - Natural biological nitrogen fixation | InVEST nutrient retention, Hood Canal, WA, USA | Salmon habitat values, west coast of Canada | Coastal protection in Belize |
EM Full Name
em.detail.fullNameHelp
?
|
US EPA EnviroAtlas - BNF (Natural biological nitrogen fixation), USA | InVEST (Integrated Valuation of Envl. Services and Tradeoffs) nutrient retention, Hood Canal, WA, USA | Value of habitat quality changes for salmon populations, South Thompson watershed, west coast of Canada | Coastal Protection provided by Coral, Seagrasses and Mangroves in Belize: |
EM Source or Collection
em.detail.emSourceOrCollectionHelp
?
|
US EPA | EnviroAtlas | InVEST | None | InVEST |
EM Source Document ID
|
262 ?Comment:EnviroAtlas maps BNF based on a correlation with AET modeled by Cleveland et al. 1999, and modified by land use (% natural vs. ag/developed) within each HUC. AET was modeled using climate and land use parameters (equation from Sanford and Selnick 2013). For full citations of these related models, see below, "Document ID for related EM. |
205 | 286 | 350 |
Document Author
em.detail.documentAuthorHelp
?
|
US EPA Office of Research and Development - National Exposure Research Laboratory | 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. | Knowler, D.J., MacGregor, B.W., Bradford, M.J., Peterman, R.M | Guannel, G., Arkema, K., Ruggiero, P., and G. Verutes |
Document Year
em.detail.documentYearHelp
?
|
2013 | 2013 | 2003 | 2016 |
Document Title
em.detail.sourceIdHelp
?
|
EnviroAtlas - National | From mountains to sound: modelling the sensitivity of dungeness crab and Pacific oyster to land–sea interactions in Hood Canal,WA | Valuing freshwater salmon habitat on the west coast of Canada | The Power of Three: Coral Reefs, Seagrasses and Mangroves Protect Coastal Regions and Increase Their Resilience |
Document Status
em.detail.statusCategoryHelp
?
|
Peer reviewed and published | Peer reviewed and published | Peer reviewed and published | Peer reviewed and published |
Comments on Status
em.detail.commentsOnStatusHelp
?
|
Published on US EPA EnviroAtlas website | Published journal manuscript | Published journal manuscript | Published journal manuscript |
EM ID
em.detail.idHelp
?
|
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
https://www.epa.gov/enviroatlas | https://www.naturalcapitalproject.org/invest/ | Not applicable | Not identified in paper | |
Contact Name
em.detail.contactNameHelp
?
|
EnviroAtlas Team ?Comment:Additional contact: Jana Compton, EPA |
J.E. Toft | Duncan Knowler | Greg Guannel |
Contact Address
|
Not reported | The Natural Capital Project, Stanford University, 371 Serra Mall, Stanford, CA 94305-5020, USA | School of Resource and Environmental Management, Simon Fraser University, Burnaby, Canada BC V5H 1S6 | The Nature Conservancy, Coral Gables, FL. USA |
Contact Email
|
enviroatlas@epa.gov | jetoft@stanford.edu | djk@sfu.ca | greg.guannel@gmail.com |
EM ID
em.detail.idHelp
?
|
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
Summary Description
em.detail.summaryDescriptionHelp
?
|
DATA FACT SHEET: "This EnviroAtlas national map displays the rate of biological nitrogen (N) fixation (BNF) in natural/semi-natural ecosystems within each watershed (12-digit HUC) in the conterminous United States (excluding Hawaii and Alaska) for the year 2006. These data are based on the modeled relationship of BNF with actual evapotranspiration (AET) in natural/semi-natural ecosystems. The mean rate of BNF is for the 12-digit HUC, not to natural/semi-natural lands within the HUC." "BNF in natural/semi-natural ecosystems was estimated using a correlation with actual evapotranspiration (AET). This correlation is based on a global meta-analysis of BNF in natural/semi-natural ecosystems. AET estimates for 2006 were calculated using a regression equation describing the correlation of AET with climate and land use/land cover variables in the conterminous US. Data describing annual average minimum and maximum daily temperatures and total precipitation at the 2.5 arcmin (~4 km) scale for 2006 were acquired from the PRISM climate dataset. The National Land Cover Database (NLCD) for 2006 was acquired from the USGS at the scale of 30 x 30 m. BNF in natural/semi-natural ecosystems within individual 12-digit HUCs was modeled with an equation describing the statistical relationship between BNF (kg N ha-1 yr-1) and actual evapotranspiration (AET; cm yr–1) and scaled to the proportion of non-developed and non-agricultural land in the 12-digit HUC." EnviroAtlas maps BNF based on a correlation with AET modeled by Cleveland et al. 1999, and modified by land use (% natural vs. ag/developed) within each HUC. AET was modeled using climate and land use parameters (equation from Sanford and Selnick 2013). For full citations of these related models, see below, "Document ID for related EM." | InVEST Nutrient Retention 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 modelled discharge and total nitrogen for the 153 perennial sub-watersheds in Hood Canal based on spatial variation in hydrological factors, land and water use, and vegetation.To do this, we reparameterized a set of fresh water models available in the InVEST tool (Tallis and Polasky, 2009; Kareiva et al., 2011)" (2) "We used the InVEST Nutrient Retention model to quantify the total nitrogen load for each subwatershed. Inputs to the Nutrient Retention model include water yield, land use and land cover, and nutrient loading and filtration rates (Table 1; Conte et al., 2011; Tallis et al., 2011). The nutrient model quantifies natural and anthropogenic sources of total nitrogen within each subwatershed, allowing managers to identify subwatersheds potentially at risk of contributing excessive nitrogen loads given the predicted development and climate future." ( P. 4) | ABSTRACT: "In this paper, we present a framework for valuing benefits for fisheries from protecting areas from degradation, using the example of the Strait of Georgia coho salmon fishery in southern British Columbia, Canada. Our study improves upon previous methods used to value fish habitat in two major respects. First, we use a bioeconomic model of the coho fishery to derive estimates of value that are consistent with economic theory. Second, we estimate the value of changing the quality of fish habitat by using empirical analyses to link fish population dynamics with indices of land use in surrounding watersheds." | AUTHOR'S DESCRIPTION: "Natural habitats have the ability to protect coastal communities against the impacts of waves and storms, yet it is unclear how different habitats complement each other to reduce those impacts. Here, we investigate the individual and combined coastal protection services supplied by live corals on reefs, seagrass meadows, and mangrove forests during both non-storm and storm conditions, and under present and future sea-level conditions. Using idealized profiles of fringing and barrier reefs, we quantify the services supplied by these habitats using various metrics of inundation and erosion. We find that, together, live corals, seagrasses, and mangroves supply more protection services than any individual habitat or any combination of two habitats. Specifically, we find that, while mangroves are the most effective at protecting the coast under non-storm and storm conditions, live corals and seagrasses also moderate the impact of waves and storms, thereby further reducing the vulnerability of coastal regions. Also, in addition to structural differences, the amount of service supplied by habitats in our analysis is highly dependent on the geomorphic setting, habitat location and forcing conditions: live corals in the fringing reef profile supply more protection services than seagrasses; seagrasses in the barrier reef profile supply more protection services than live corals; and seagrasses, in our simulations, can even compensate for the long-term degradation of the barrier reef. Results of this study demonstrate the importance of taking integrated and place-based approaches when quantifying and managing for the coastal protection services supplied by ecosystems." |
Specific Policy or Decision Context Cited
em.detail.policyDecisionContextHelp
?
|
None Identified | Land use change | None identified | Future rock lobster fisheries management |
Biophysical Context
|
No additional description provided | No additional description provided | No additional description provided | barrier reef and fringing reef in nearshore coastal marine system |
EM Scenario Drivers
em.detail.scenarioDriverHelp
?
|
No scenarios presented | Future land use and land cover; climate change | Habitat quality | Reef type, Sea level increase, storm conditions, seagrass conditions, coral conditions, vegetation types and conditions |
EM ID
em.detail.idHelp
?
|
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
Method Only, Application of Method or Model Run
em.detail.methodOrAppHelp
?
|
Method + Application | Method + Application (multiple runs exist) View EM Runs | Method + Application (multiple runs exist) View EM Runs | Method + Application (multiple runs exist) View EM Runs |
New or Pre-existing EM?
em.detail.newOrExistHelp
?
|
New or revised model | Application of existing 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
em.detail.idHelp
?
|
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
Document ID for related EM
em.detail.relatedEmDocumentIdHelp
?
|
Doc-346 | Doc-347 ?Comment:EnviroAtlas maps BNF based on a correlation with AET modeled by Cleveland et al. 1999, and modified by land use (% natural vs. ag/developed) within each HUC. AET was modeled using climate and land use parameters (equation from Sanford and Selnick 2013). For full citations of these related models, see below, "Document ID for related EM. |
Doc-309 | Doc-338 | None | None |
EM ID for related EM
em.detail.relatedEmEmIdHelp
?
|
None | EM-363 | EM-438 | EM-179 | EM-183 | EM-180 | EM-181 | None |
EM Modeling Approach
EM ID
em.detail.idHelp
?
|
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
EM Temporal Extent
em.detail.tempExtentHelp
?
|
2006-2010 | 2005-7; 2035-45 | 1989-1999 | 2005-2013 |
EM Time Dependence
em.detail.timeDependencyHelp
?
|
time-stationary | time-stationary | time-stationary | time-dependent |
EM Time Reference (Future/Past)
em.detail.futurePastHelp
?
|
Not applicable | Not applicable | Not applicable | Not applicable |
EM Time Continuity
em.detail.continueDiscreteHelp
?
|
Not applicable | Not applicable | Not applicable | discrete |
EM Temporal Grain Size Value
em.detail.tempGrainSizeHelp
?
|
Not applicable | Not applicable | Not applicable | 1 |
EM Temporal Grain Size Unit
em.detail.tempGrainSizeUnitHelp
?
|
Not applicable | Not applicable | Not applicable | Second |
EM ID
em.detail.idHelp
?
|
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
Bounding Type
em.detail.boundingTypeHelp
?
|
Geopolitical | Watershed/Catchment/HUC | Physiographic or ecological | Geopolitical |
Spatial Extent Name
em.detail.extentNameHelp
?
|
counterminous United States | Hood Canal | South Thompson watershed | Coast of Belize |
Spatial Extent Area (Magnitude)
em.detail.extentAreaHelp
?
|
>1,000,000 km^2 | 100,000-1,000,000 km^2 | 1000-10,000 km^2. | 100-1000 km^2 |
EM ID
em.detail.idHelp
?
|
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
EM Spatial Distribution
em.detail.distributeLumpHelp
?
|
spatially distributed (in at least some cases) ?Comment:Watersheds (12-digit HUCs). |
spatially distributed (in at least some cases) | spatially lumped (in all cases) | spatially distributed (in at least some cases) |
Spatial Grain Type
em.detail.spGrainTypeHelp
?
|
other (specify), for irregular (e.g., stream reach, lake basin) | area, for pixel or radial feature | Not applicable | length, for linear feature (e.g., stream mile) |
Spatial Grain Size
em.detail.spGrainSizeHelp
?
|
irregular | 30 m x 30 m | Not applicable | 1 meter |
EM ID
em.detail.idHelp
?
|
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
EM Computational Approach
em.detail.emComputationalApproachHelp
?
|
Analytic | Other or unclear (comment) | Analytic | Analytic |
EM Determinism
em.detail.deterStochHelp
?
|
deterministic | deterministic | deterministic | deterministic |
Statistical Estimation of EM
em.detail.statisticalEstimationHelp
?
|
|
|
|
|
EM ID
em.detail.idHelp
?
|
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
Model Calibration Reported?
em.detail.calibrationHelp
?
|
No | Yes | Yes | No |
Model Goodness of Fit Reported?
em.detail.goodnessFitHelp
?
|
No | No | No | No |
Goodness of Fit (metric| value | unit)
em.detail.goodnessFitValuesHelp
?
|
None | None | None | None |
Model Operational Validation Reported?
em.detail.validationHelp
?
|
No | Yes | No |
No ?Comment:Used the SWAN model (see below for referenece) with Generation 1 or 2 wind-wave formulations to validate the wave development portion of the model. Booij N, Ris RC, Holthuijsen LH. A third-generation wave model for coastal regions 1. Model description and validation. J Geophys Res. American Geophysical Union; 1999;104: 7649?7666. |
Model Uncertainty Analysis Reported?
em.detail.uncertaintyAnalysisHelp
?
|
No | No | No | No |
Model Sensitivity Analysis Reported?
em.detail.sensAnalysisHelp
?
|
No | Yes | Yes | No |
Model Sensitivity Analysis Include Interactions?
em.detail.interactionConsiderHelp
?
|
Not applicable | No | No | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
|
|
|
|
Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
None |
|
|
|
Centroid Lat/Long (Decimal Degree)
EM ID
em.detail.idHelp
?
|
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
Centroid Latitude
em.detail.ddLatHelp
?
|
39.5 | 47.8 | 49.29 | 18.63 |
Centroid Longitude
em.detail.ddLongHelp
?
|
-98.35 | -122.7 | -123.8 | -88.22 |
Centroid Datum
em.detail.datumHelp
?
|
WGS84 | WGS84 | WGS84 | WGS84 |
Centroid Coordinates Status
em.detail.coordinateStatusHelp
?
|
Estimated | Estimated | Estimated | Estimated |
EM ID
em.detail.idHelp
?
|
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
EM Environmental Sub-Class
em.detail.emEnvironmentalSubclassHelp
?
|
Terrestrial Environment (sub-classes not fully specified) | Near Coastal Marine and Estuarine | Rivers and Streams | Near Coastal Marine and Estuarine | Near Coastal Marine and Estuarine |
Specific Environment Type
em.detail.specificEnvTypeHelp
?
|
Terrestrial | glacier-carved saltwater fjord | Rivers and streams | coral reefs |
EM Ecological Scale
em.detail.ecoScaleHelp
?
|
Ecological scale is finer than that of the Environmental Sub-class | Ecological scale is finer than that of the Environmental Sub-class | 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
EM ID
em.detail.idHelp
?
|
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
EM Organismal Scale
em.detail.orgScaleHelp
?
|
Not applicable | Not applicable |
Other (Comment) ?Comment:Coho salmon stock |
Guild or Assemblage |
Taxonomic level and name of organisms or groups identified
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
None Available | None Available |
|
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)
EM-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
|
|
|
|
<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-63 |
EM-112 ![]() |
EM-177 ![]() |
EM-542 ![]() |
|
None |
|
|