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-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
EM Short Name
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EnviroAtlas-Air pollutant removal | RHyME2, Upper Mississippi River basin, USA | AnnAGNPS, Kaskaskia River watershed, IL, USA | Fish species habitat value, Tampa Bay, FL, USA | FORCLIM v2.9, Santiam watershed, OR, USA | Fish species richness, Puerto Rico, USA | DeNitrification-DeComposition simulation (DNDC) v.8.9 flux simulation, Ireland | Alewife derived nutrients, Connecticut, USA | Atlantis ecosystem harvest submodel | GI toolkit users guide | NU-WRF, USA |
EM Full Name
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US EPA EnviroAtlas - Pollutants (air) removed annually by tree cover; Example is shown for Durham NC and vicinity, USA | RHyME2 (Regional Hydrologic Modeling for Environmental Evaluation), Upper Mississippi River basin, USA | AnnAGNPS (Annualized Agricultural Non-Point Source Pollution Model), Kaskaskia River watershed, IL, USA | Fish species habitat value, Tampa Bay, FL, USA | FORCLIM (FORests in a changing CLIMate) v2.9, Santiam watershed, OR, USA | Fish species richness, Puerto Rico, USA | DeNitrification-DeComposition simulation of N2O flux Ireland | Alewife derived nutrients in stream food web, Connecticut, USA | Lessons in modelling and management of marine ecosystems: the Atlantis experience | Green Infrastructure valuation toolkit users guide | Nasa Unified Weather Research and Forcasing model |
EM Source or Collection
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US EPA | EnviroAtlas | i-Tree ?Comment:EnviroAtlas uses an application of the i-Tree Eco model. |
US EPA | US EPA | US EPA | US EPA | None | None | None | None | None | None |
EM Source Document ID
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223 | 123 | 137 | 187 |
23 ?Comment:Related document ID 22 is a secondary source providing tree species specific parameters in appendix. |
355 | 358 | 384 | 463 | 474 | 484 |
Document Author
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US EPA Office of Research and Development - National Exposure Research Laboratory | Tran, L. T., O’Neill, R. V., Smith, E. R., Bruins, R. J. F. and Harden, C. | Yuan, Y., Mehaffey, M. H., Lopez, R. D., Bingner, R. L., Bruins, R., Erickson, C. and Jackson, M. | Fulford, R., Yoskowitz, D., Russell, M., Dantin, D., and Rogers, J. | Busing, R. T., Solomon, A. M., McKane, R. B. and Burdick, C. A. | Pittman, S.J., Christensen, J.D., Caldow, C., Menza, C., and M.E. Monaco | Abdalla, M., Yeluripati, J., Smith, P., Burke, J., Williams, M. | Walters, A. W., R. T. Barnes, and D. M. Post | Fulton, E.A., Link, J.S., Kaplan, I.C., Savina‐Rolland, M., Johnson, P., Ainsworth, C., Horne, P., Gorton, R., Gamble, R.J., Smith, A.D. and Smith, D.C. | Genecon LLP. | Peters-Lidard, Christa et al. Sujay V. Kumar, , Jossy P. Jacob b , Thomas Clune f , Wei-Kuo Tao g , Mian Chin h , Arthur Hou I , Jonathan L. Case j , Dongchul Kim k , Kyu-Myong Kim l , William Lau m, Yuqiong Liu n , Jainn Shi o , David Starr g , Qian Tan h , Zhining Tao k , Benjamin F. Zaitchik p , Bradley Zavodsky q , Sara Q. Zhang r , Milija Zupanski |
Document Year
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2013 | 2013 | 2011 | 2016 | 2007 | 2007 | 2010 | 2009 | 2011 | 2010 | 2015 |
Document Title
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EnviroAtlas - Featured Community | Application of hierarchy theory to cross-scale hydrologic modeling of nutrient loads | AnnAGNPS model application for nitrogen loading assessment for the Future Midwest Landscape study | Habitat and recreational fishing opportunity in Tampa Bay: Linking ecological and ecosystem services to human beneficiaries | Forest dynamics in Oregon landscapes: evaluation and application of an individual-based model | Predictive mapping of fish species richness across shallow-water seascapes in the Caribbean | Testing DayCent and DNDC model simulations of N2O fluxes and assessing the impacts of climate change on the gas flux and biomass production from a humid pasture | Anadromous alewives (Alosa pseudoharengus) contribute marine-derived nutrients to coastal stream food webs | Lessons in modelling and management of marine ecosystems: the Atlantis experience | Building natural value for sustainable economic development The green infrastructure valuation toolkit user guide | Integrated modeling of aerosol, cloud, precipitation and land processes at satellite-resolved scales |
Document Status
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Peer reviewed and published | Peer reviewed and published | Peer reviewed and published | Peer reviewed and published | Peer reviewed and published | Peer reviewed and published | Peer reviewed and published | Peer reviewed and published | Peer reviewed and published | Peer reviewed and published | Peer reviewed and published |
Comments on Status
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Published on US EPA EnviroAtlas website | Published journal manuscript | Published journal manuscript | Published journal manuscript | Published journal manuscript | Published journal manuscript | Published journal manuscript | Published journal manuscript | Published journal manuscript | Published report | None |
EM ID
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EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
https://www.epa.gov/enviroatlas | Not applicable | https://www.ars.usda.gov/southeast-area/oxford-ms/national-sedimentation-laboratory/watershed-physical-processes-research/docs/annagnps-pollutant-loading-model/ | Not applicable | Not applicable | Not applicable | http://www.dndc.sr.unh.edu | Not applicable | https://research.csiro.au/atlantis/home/links/ | https://www.merseyforest.org.uk/services/gi-val/ | None | |
Contact Name
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EnviroAtlas Team | Liem Tran | Yongping Yuan | Richard Fulford | Richard T. Busing | Simon Pittman | M. Abdalla | Annika W. Walters | Elizabeth Fulton | The Mercey Forest | Christa |
Contact Address
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Not reported | Department of Geography, University of Tennessee, 1000 Phillip Fulmer Way, Knoxville, TN 37996-0925, USA | U.S. Environmental Protection Agency Office of Research and Development, Environmental Sciences Division, 944 East Harmon Ave., Las Vegas, NV 89119, USA | USEPA Gulf Ecology Division, Gulf Breeze, FL 32561 | U.S. Geological Survey, 200 SW 35th Street, Corvallis, Oregon 97333 USA | 1305 East-West Highway, Silver Spring, MD 20910, USA | Dept. of Botany, School of Natural Science, Trinity College Dublin, Dublin2, Ireland | Dept. of Ecology and Evolutionary Biology, Yale University, New Haven, CT 06511, USA | Division of Marine and Atmospheric Research, GPO Box 1538, Hobart, Tas. | Moss Ln, Woolston, Warrington WA3 6QX, United Kingdom | Hydrospheric and Biospheric Sciences Division, Code 610HB, NASA Goddard Space Flight Center, Greenbelt, MD 20771, USA |
Contact Email
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enviroatlas@epa.gov | ltran1@utk.edu | yuan.yongping@epa.gov | Fulford.Richard@epa.gov | rtbusing@aol.com | simon.pittman@noaa.gov | abdallm@tcd.ie | annika.walters@yale.edu | beth.fulton@csiro.au | mail@merseyforest.org.uk | christa.peters@nasa.gov |
EM ID
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EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
Summary Description
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The Air Pollutant Removal model has been used to create coverages for several US communities. An example for Durham, NC is shown in this entry. ABSTRACT: "This EnviroAtlas dataset presents environmental benefits of the urban forest in 193 block groups in Durham, North Carolina. ... pollution removal ... are calculated for each block group using i-Tree models (www.itreetools.org), local weather data, pollution data, EPA provided city boundary and land cover data, and U.S. Census derived block group boundary data. This dataset was produced by the US Forest Service to support research and online mapping activities related to EnviroAtlas." METADATA: The maps, estimate and illustrate the variation in the amount of six airborne pollutants, carbon monoxide (CO), ozone (O3), sulfur dioxide (SO2), nitrogen dioxide (NO2), particulate matter (PM10), and particulate matter (PM2.5), removed by trees. PM10 is for particulate matter greater than 2.5 microns and less than 10 microns. DATA FACT SHEET: "The data for this map are based on the land cover derived for each EnviroAtlas community and the pollution removal models in i-Tree, a toolkit developed by the USDA Forest Service. The land cover data were created from aerial photography through remote sensing methods; tree cover was then summarized as the percentage of each census block group. The i-Tree pollution removal module uses the tree cover data by block group, the closest hourly meteorological monitoring data for the community, and the closest pollution monitoring data... hourly estimates of pollution removal by trees were combined with atmospheric data to estimate hourly percent air quality improvement due to pollution removal for each pollutant." | ABSTRACT: "We describe a framework called Regional Hydrologic Modeling for Environmental Evaluation (RHyME2) for hydrologic modeling across scales. Rooted from hierarchy theory, RHyME2 acknowledges the rate-based hierarchical structure of hydrological systems. Operationally, hierarchical constraints are accounted for and explicitly described in models put together into RHyME2. We illustrate RHyME2with a two-module model to quantify annual nutrient loads in stream networks and watersheds at regional and subregional levels. High values of R2 (>0.95) and the Nash–Sutcliffe model efficiency coefficient (>0.85) and a systematic connection between the two modules show that the hierarchy theory-based RHyME2 framework can be used effectively for developing and connecting hydrologic models to analyze the dynamics of hydrologic systems." Two EMs will be entered in EPF-Library: 1. Regional scale module (Upper Mississippi River Basin) - this entry 2. Subregional scale module (St. Croix River Basin) | AUTHORS' DESCRIPTION: "AnnAGNPS is an advanced simulation model developed by the USDA-ARS and Natural Resource Conservation Services (NRCS) to help evaluate watershed response to agricultural management practices. It is a continuous simulation, daily time step, pollutant loading model designed to simulate water, sediment and chemical movement from agricultural watersheds.p. 198" | ABSTRACT: "Estimating value of estuarine habitat to human beneficiaries requires that we understand how habitat alteration impacts function through both production and delivery of ecosystem goods and services (EGS). Here we expand on the habitat valuation technique of Bell (1997) with an estimate of recreational angler willingness-to-pay combined with estimates of angler effort, fish population size, and fish and angler distribution. Results suggest species-specific fishery value is impacted by angler interest and stock status, as the most targeted fish (spotted seatrout) did not have the highest specific value (fish−1). Reduced population size and higher size at capture resulted in higher specific value for common snook. Habitat value estimated from recreational fishing value and fish-angler distributions supported an association between seagrass and habitat value, yet this relationship was also impacted by distance to access points. This analysis does not provide complete valuation of habitat as it considers only one service (fishing), but demonstrates a methodology to consider functional equivalency of all habitat features as a part of a habitat mosaic rather than in isolation, as well as how to consider both EGS production and delivery to humans (e.g., anglers) in any habitat valuation, which are critical for a transition to ecosystem management." | ABSTRACT: "The FORCLIM model of forest dynamics was tested against field survey data for its ability to simulate basal area and composition of old forests across broad climatic gradients in western Oregon, USA. The model was also tested for its ability to capture successional trends in ecoregions of the west Cascade Range. It was then applied to simulate present and future (1990-2050) forest landscape dynamics of a watershed in the west Cascades. Various regimes of climate change and harvesting in the watershed were considered in the landscape application." AUTHOR'S DESCRIPTION: "Effects of different management histories on the landscape were incorporated using the land management (conservation, plan, or development trend) and forest age categories…the plan trend was an intermediate alternative, representing the continuation of current policies and trends, whereas the conservation and development trends were possible alternatives…Non-forested areas were given a forest age of zero; forested areas were assigned to one of eight forest age classes: >0-20 yr, 21-40 yr, 41-60 yr, 61-80 yr, 81-200 yr, 201-400 yr, and >600 yr in 1990…two climate change scenarios were used, representing lower and upper extremes projected by a set of global climate models: (1) minor warming with drier summers, and (2) major warming with wetter conditions…For the first scenario, temperature was increased by 0.5°C in 2025 and by 1.5°C in 2045. Precipitation from October to March was increased 2% in 2025 and decreased 2% in 2045. Precipitation from April to September was decreased 4% in 2025 and 7% in 2045. For the second scenario, temperature was by increased 2.6°C in 2025 and by 3.2°C in 2045. Precipitation from October to March was increased 18% in 2025 and 22% in 2045. Precipitation from April to September was increased 14% in 2025 and 9% in 2045. | ABSTRACT: "Effective management of coral reef ecosystems requires accurate, quantitative and spatially explicit information on patterns of species richness at spatial scales relevant to the management process. We combined empirical modelling techniques, remotely sensed data, field observations and GIS to develop a novel multi-scale approach for predicting fish species richness across a compositionally and topographically complex mosaic of marine habitat types in the U.S. Caribbean. First, the performance of three different modelling techniques (multiple linear regression, neural networks and regression trees) was compared using data from southwestern Puerto Rico and evaluated using multiple measures of predictive accuracy. Second, the best performing model was selected. Third, the generality of the best performing model was assessed through application to two geographically distinct coral reef ecosystems in the neighbouring U.S. Virgin Islands. Overall, regression trees outperformed multiple linear regression and neural networks. The best performing regression tree model of fish species richness (high, medium, low classes) in southwestern Puerto Rico exhibited an overall map accuracy of 75%; 83.4% when only high and low species richness areas were evaluated. In agreement with well recognised ecological relationships, areas of high fish species richness were predicted for the most bathymetrically complex areas with high mean rugosity and high bathymetric variance quantified at two different spatial extents (≤0.01 km2). Water depth and the amount of seagrasses and hard-bottom habitat in the seascape were of secondary importance. This model also provided good predictions in two geographically distinct regions indicating a high level of generality in the habitat variables selected. Results indicated that accurate predictions of fish species richness could be achieved in future studies using remotely sensed measures of topographic complexity alone. This integration of empirical modelling techniques with spatial technologies provides an important new tool in support of ecosystem-based management for coral reef ecosystems." | Simulation models are one of the approaches used to investigate greenhouse gas emissions and potential effects of global warming on terrestrial ecosystems. DayCent which is the daily time-step version of the CENTURY biogeochemical model, and DNDC (the DeNitrification–DeComposition model) were tested against observed nitrous oxide flux data from a field experiment on cut and extensively grazed pasture located at the Teagasc Oak Park Research Centre, Co. Carlow, Ireland. The soil was classified as a free draining sandy clay loam soil with a pH of 7.3 and a mean organic carbon and nitrogen content at 0–20 cm of 38 and 4.4 g kg−1 dry soil, respectively. The aims of this study were to validate DayCent and DNDC models for estimating N2O emissions from fertilized humid pasture, and to investigate the impacts of future climate change on N2O fluxes and biomass production. Measurements of N2O flux were carried out from November 2003 to November 2004 using static chambers. Three climate scenarios, a baseline of measured climatic data from the weather station at Carlow, and high and low temperature sensitivity scenarios predicted by the Community Climate Change Consortium For Ireland (C4I) based on the Hadley Centre Global Climate Model (HadCM3) and the Intergovernment Panel on Climate Change (IPCC) A1B emission scenario were investigated. DNDC overestimated the measured flux with relative deviations of +132 and +258% due to overestimation of the effects of SOC. DayCent, though requiring some calibration for Irish conditions, simulated N2O fluxes more consistently than did DNDC. | ABSTRACT: "Diadromous fish are an important link between marine and freshwater food webs. Pacific salmon (Oncorhynchus spp.) strongly impact nutrient dynamics in inland waters and anadromous alewife (Alosa pseudoharengus) may play a similar ecological role along the Atlantic coast. The annual spawning migration of anadromous alewife contributes, on average, 1050 g of nitrogen and 120 g of phosphorus to Bride Brook, Connecticut, USA, through excretion and mortality each year... There was no significant effect of this nutrient influx on water chemistry, leaf decomposition, or periphyton accrual. Dam removal and fish ladder construction will allow anadromous alewife to regain access to historical freshwater spawning habitats, potentially impacting food web dynamics and nutrient cycling in coastal freshwater systems." | Models are key tools for integrating a wide range of system information in a common framework. Attempts to model exploited marine ecosystems can increase understanding of system dynamics; identify major processes, drivers and responses; highlight major gaps in knowledge; and provide a mechanism to ‘road test’ management strategies before implementing them in reality. The Atlantis modelling framework has been used in these roles for a decade and is regularly being modified and applied to new questions (e.g. it is being coupled to climate, biophysical and economic models to help consider climate change impacts, monitoring schemes and multiple use management). This study describes some common lessons learned from its implementation, particularly in regard to when these tools are most effective and the likely form of best practices for ecosystem-based management (EBM). Most importantly, it highlighted that no single management lever is sufficient to address the many trade-offs associated with EBM and that the mix of measures needed to successfully implement EBM will differ between systems and will change through time. Although it is doubtful that any single management action will be based solely on Atlantis, this modelling approach continues to provide important insights for managers when making natural resource management decisions. | [The toolkit provides a very helpful introduction to the evidence demonstrating the benefits of green infrastructure interventions. It offers a structured argument that speaks the language of regeneration and economic developments. The 11 economic benefits structure provides a relatively simple high level means of presenting and communicating the benefits of green infrastructure projects in economic contexts, although it also brings some risks of double-counting (see Limitations below). The toolkit provides a structured approach to value green infrastructure benefits in monetary, quantitative and qualitative terms, with equal weight being applied to each of these three ways to present existing evidence. It can add value to and inform the decision-making process, particularly when used at an early stage to get broad brush figures and weigh pros and cons.The toolkit relies on current state-of-the-art evidence and valuation techniques for green infrastructure benefits. However, the toolkit also highlights the need for considerable improvement and expansion of the evidence base to enable future iterations to provide improved valuations. The toolkit helps make green infrastructure benefits ‘visible’ to potential funders. The inclusion of environmental benefits in cost benefit analysis is currently very difficult, often requiring professional assistance. Such assistance is frequently beyond the means of many groups seeking project funding. The toolkit is aimed at filling this gap, providing a means of scoping out the indicative benefits of green infrastructure using tools and approaches accessible to many projects and groups. However, whilst the toolkit provides a means of undertaking a broad Value for Money assessment, it must but emphasised that this is only indicative and cannot replace more rigorous formal project appraisal techniques.] | ABSTRACT: "With support from NASA's Modeling and Analysis Program, we have recently developed the NASA Unified-Weather Research and Forecasting model (NU-WRF). NU-WRF is an observation-driven integrated modeling system that represents aerosol, cloud, precipitation and land processes at satelliteresolved scales. “Satellite-resolved” scales (roughly 1e25 km), bridge the continuum between local (microscale), regional (mesoscale) and global (synoptic) processes. NU-WRF is a superset of the National Center for Atmospheric Research (NCAR) Advanced Research WRF (ARW) dynamical core model, achieved by fully integrating the GSFC Land Information System (LIS, already coupled to WRF), the WRF/Chem enabled version of the Goddard Chemistry Aerosols Radiation Transport (GOCART) model, the Goddard Satellite Data Simulation Unit (G-SDSU), and custom boundary/initial condition preprocessors into a single software release, with source code available by agreement with NASA/GSFC. Full coupling between aerosol, cloud, precipitation and land processes is critical for predicting local and regional water and energy cycles " |
Specific Policy or Decision Context Cited
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None identified | Not reported | Not reported | None identifed | None identified | None provided | climate change | None identified | None identified | None | None |
Biophysical Context
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No additional description provided | No additional description provided | Upper Mississipi River basin, elevation 142-194m, | shallow bay (mean 3.7m), transition zone between warm temperate and tropical biogeographic provinces. Highly urbanized watershed | No additional description provided | Hard and soft benthic habitat types approximately to the 33m isobath | Agricultural field, Ann rainfall 824mm, mean air temp 9.4°C | Alewife spawning runs typically occur Mid March - May. | NA | N/A | None |
EM Scenario Drivers
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No scenarios presented | No scenarios presented | Alternative agricultural land use (type and crop management (fertilizer application) towards a future biofuel target | No scenarios presented | Land Management (3); Climate Change (3) | No scenarios presented | fertilization | No scenarios presented | No scenarios presented | N/A | None |
EM ID
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EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
Method Only, Application of Method or Model Run
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Method + Application (multiple runs exist) View EM Runs | Method + Application | Method + Application | Method + Application (multiple runs exist) View EM Runs |
Method + Application (multiple runs exist) View EM Runs ?Comment:Runs differentiated by scenario combination. |
Method + Application | Method + Application | Method + Application (multiple runs exist) View EM Runs | Method Only | Method Only | None |
New or Pre-existing EM?
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Application of existing model | New or revised model | New or revised model | New or revised model | Application of existing model | New or revised model | Application of existing model | New or revised model | Application of existing model | New or revised model | None |
Related EMs (for example, other versions or derivations of this EM) described in ESML
EM ID
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EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
Document ID for related EM
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Doc-345 | Doc-123 | Doc-142 | None |
Doc-22 | Doc-23 ?Comment:Related document ID 22 is a secondary source providing tree species specific parameters in appendix. |
Doc-355 | None | Doc-383 | Doc-456 | Doc-459 | Doc-461 | Doc-463 | None | None |
EM ID for related EM
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None | None | None | None | EM-146 | EM-186 | EM-224 | EM-698 | EM-699 | EM-593 | EM-661 | EM-665 | EM-666 | EM-672 | EM-674 | EM-673 | EM-978 | EM-981 | EM-983 | EM-985 | EM-990 | None | None |
EM Modeling Approach
EM ID
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EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
EM Temporal Extent
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2008-2010 | 1987-1997 | 1980-2006 | 2006-2011 | 1990-2050 | 2000-2005 | 1961-1990 | 1979-2009 | Not applicable | Not applicable | 2015 |
EM Time Dependence
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time-dependent | time-stationary | time-stationary | time-stationary | time-dependent | time-stationary | time-dependent | time-stationary | time-dependent | time-dependent | Not applicable |
EM Time Reference (Future/Past)
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future time | Not applicable | Not applicable | Not applicable | future time | Not applicable | both | Not applicable | Not applicable | Not applicable | Not applicable |
EM Time Continuity
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discrete | Not applicable | Not applicable | Not applicable | discrete | Not applicable | discrete | Not applicable | continuous | Not applicable | Not applicable |
EM Temporal Grain Size Value
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1 | Not applicable | Not applicable | Not applicable | 1 | Not applicable | 1 | Not applicable | Not applicable | Not applicable | Not applicable |
EM Temporal Grain Size Unit
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Hour | Not applicable | Not applicable | Not applicable | Year | Not applicable | Day | Not applicable | Not applicable | Not applicable | Not applicable |
EM ID
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EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
Bounding Type
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Geopolitical | Watershed/Catchment/HUC | Watershed/Catchment/HUC | Physiographic or Ecological | Watershed/Catchment/HUC | Physiographic or ecological | Point or points | Watershed/Catchment/HUC | Not applicable | Not applicable | No location (no locational reference given) |
Spatial Extent Name
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Durham NC and vicinity | Upper Mississippi River basin; St. Croix River Watershed | East Fork Kaskaskia River watershed basin | Tampa Bay | South Santiam watershed | SW Puerto Rico, | Oak Park Research centre | Bride Brook | Not applicable | Not applicable | None |
Spatial Extent Area (Magnitude)
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100-1000 km^2 | 100,000-1,000,000 km^2 | 100-1000 km^2 | 1000-10,000 km^2. | 100-1000 km^2 | 100-1000 km^2 | 1-10 ha | 1-10 ha | Not applicable | Not applicable | None |
EM ID
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EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
EM Spatial Distribution
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spatially distributed (in at least some cases) ?Comment:Spatial grain type is census block group. |
spatially distributed (in at least some cases) | spatially distributed (in at least some cases) | spatially distributed (in at least some cases) | spatially distributed (in at least some cases) | spatially distributed (in at least some cases) | spatially lumped (in all cases) | spatially lumped (in all cases) | Not applicable | spatially distributed (in at least some cases) | other or unclear (comment) |
Spatial Grain Type
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other (specify), for irregular (e.g., stream reach, lake basin) | NHDplus v1 | length, for linear feature (e.g., stream mile) | area, for pixel or radial feature | area, for pixel or radial feature | area, for pixel or radial feature | Not applicable | Not applicable | Not applicable | area, for pixel or radial feature | Not applicable |
Spatial Grain Size
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irregular | NHDplus v1 | 1 km^2 | 1 km^2 | 0.08 ha | not reported | Not applicable | Not applicable | Not applicable | Not reported | Not applicable |
EM ID
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EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
EM Computational Approach
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Numeric | Numeric | Numeric | Analytic | Numeric | Analytic | Numeric | Analytic | Analytic | Numeric | * |
EM Determinism
em.detail.deterStochHelp
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deterministic | deterministic | deterministic | deterministic | deterministic | deterministic | deterministic | deterministic | deterministic | deterministic | None |
Statistical Estimation of EM
em.detail.statisticalEstimationHelp
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None |
EM ID
em.detail.idHelp
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EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
Model Calibration Reported?
em.detail.calibrationHelp
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Unclear | Yes | No | No | No | No | Yes |
Yes ?Comment:The fish counter (for alewife numbers) was calibrated. |
Not applicable | Not applicable | None |
Model Goodness of Fit Reported?
em.detail.goodnessFitHelp
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No | Yes | No | No | No | Yes |
Yes ?Comment:Actual value was not given, just that results were very poor. Simulation results were 258% of observed |
No | Not applicable | Not applicable | None |
Goodness of Fit (metric| value | unit)
em.detail.goodnessFitValuesHelp
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None |
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None | None | None |
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None | None | None | None |
Model Operational Validation Reported?
em.detail.validationHelp
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No | No | Yes | No | No | Yes | Yes | No | Not applicable | Not applicable | None |
Model Uncertainty Analysis Reported?
em.detail.uncertaintyAnalysisHelp
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No | No | Yes | No | No | No | No | No | Not applicable | Not applicable | None |
Model Sensitivity Analysis Reported?
em.detail.sensAnalysisHelp
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No |
No ?Comment:Some model coefficients serve, by their magnitude, to indicate the proportional impact on the final result of variation in the parameters they modify. |
Unclear | No | No | Yes | No | No | Not applicable | Not applicable | None |
Model Sensitivity Analysis Include Interactions?
em.detail.interactionConsiderHelp
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Not applicable | Not applicable | Not applicable | Not applicable | N/A | No | Not applicable | Not applicable | Not applicable | Not applicable | None |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
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None |
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None | None | None |
Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
None | None | None |
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None |
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None |
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None | None | None |
Centroid Lat/Long (Decimal Degree)
EM ID
em.detail.idHelp
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EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
Centroid Latitude
em.detail.ddLatHelp
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35.99 | 42.5 | 38.69 | 27.74 | 44.24 | 17.9 | 52.86 | 41.32 | Not applicable | Not applicable | None |
Centroid Longitude
em.detail.ddLongHelp
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-78.96 | -90.63 | -89.1 | -82.57 | -122.24 | 67.11 | 6.54 | -72.24 | Not applicable | Not applicable | None |
Centroid Datum
em.detail.datumHelp
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None provided | WGS84 | WGS84 | WGS84 | None provided | WGS84 | None provided | WGS84 | Not applicable | Not applicable | None |
Centroid Coordinates Status
em.detail.coordinateStatusHelp
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Estimated | Estimated | Provided | Estimated | Provided | Estimated | Provided | Provided | Not applicable | Not applicable | None |
EM ID
em.detail.idHelp
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EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
EM Environmental Sub-Class
em.detail.emEnvironmentalSubclassHelp
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Created Greenspace | Atmosphere | Aquatic Environment (sub-classes not fully specified) | Rivers and Streams | Inland Wetlands | Terrestrial Environment (sub-classes not fully specified) | Agroecosystems | Atmosphere | Agroecosystems | Near Coastal Marine and Estuarine | Forests | Near Coastal Marine and Estuarine | Agroecosystems | Rivers and Streams | Aquatic Environment (sub-classes not fully specified) | Rivers and Streams | Inland Wetlands | Lakes and Ponds | Near Coastal Marine and Estuarine | Open Ocean and Seas | Not applicable | Atmosphere |
Specific Environment Type
em.detail.specificEnvTypeHelp
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Urban and vicinity | None | Row crop agriculture in Kaskaskia river basin | Habitat Zones (Low, Med, High, Optimal) around seagrass and emergent marsh | primarily Conifer Forest | shallow coral reefs | farm pasture | Coastal stream | Multiple | Multiple | Regional wealther |
EM Ecological Scale
em.detail.ecoScaleHelp
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Ecological scale is finer than that of the Environmental Sub-class | Ecosystem | Ecological scale corresponds to the Environmental Sub-class | Zone within an ecosystem | 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 | Ecological scale corresponds to the Environmental Sub-class | Ecological scale corresponds to 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
em.detail.idHelp
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EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
EM Organismal Scale
em.detail.orgScaleHelp
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Not applicable | Not applicable | Not applicable | Species | Species | Guild or Assemblage | Not applicable | Individual or population, within a species | Not applicable | Not applicable | Not applicable |
Taxonomic level and name of organisms or groups identified
EM-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
None Available | None Available | None Available |
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None Available |
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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-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
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None |
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None | None |
<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-59 ![]() |
EM-91 | EM-97 |
EM-102 ![]() |
EM-208 ![]() |
EM-590 | EM-598 |
EM-667 ![]() |
EM-991 | EM-1004 | EM-1022 |
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None |
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None |
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None | None | None |