EcoService Models Library (ESML)
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: Wild bee community change over a 26 year chronosequence of restored tallgrass prairie, IL, USA (EM-788)
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EM Identity and Description
EM Identification (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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EM Short Name
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Rate of Fire Spread | Wild bees over 26 yrs of restored prairie, IL, USA | Recreational fishery index, USA | VELMA v. 2.0 disturbance | IPaC, USFWS, USA | CommunityViz, Albany county, Wyoming |
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EM Full Name
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Rate of Fire Spread | Wild bee community change over a 26 year chronosequence of restored tallgrass prairie, IL, USA | Recreational fishery index for streams and rivers, USA | VELMA (Visualizing Ecosystems for Land Management Assessment) version 2.0 disturbance | Information for Planning and Conservation tool, USFWS, U.S. | Wyoming Community Viz TM Partnership Phase I Pilot: Aquifer Protection and Community Viz TM in Albany County, Wyoming. |
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EM Source or Collection
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* | None | US EPA | US EPA | * | * |
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EM Source Document ID
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306 | 401 | 414 | 366 |
451 ?Comment:Assume peer reviewed at least internally by USFWS |
479 ?Comment:Published as a report by the University of Wyoming, but no record of peer review. |
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Document Author
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Rothermel, Richard C. | Griffin, S. R, B. Bruninga-Socolar, M. A. Kerr, J. Gibbs and R. Winfree | Lomnicky. G.A., Hughes, R.M., Peck, D.V., and P.L. Ringold | McKane, R. B., A. Brookes, K. Djang, M. Stieglitz, A. G. Abdelnour, F. Pan, J. J. Halama, P. B. Pettus and D. L. Phillips | U.S. Fish and Wildlife Service | Lieske, S. N., Mullen, S., Knapp, M., & Hamerlinck, J. D. |
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Document Year
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1972 | 2017 | 2021 | 2014 | None | 2003 |
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Document Title
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A Mathematical model for predicting fire spread in wildland fuels | Wild bee community change over a 26-year chronosequence of restored tallgrass prairie | Correspondence between a recreational fishery index and ecological condition for U.S.A. streams and rivers. | VELMA Version 2.0 User Manual and Technical Documentation | Information for Planning and Consultation (IPaC | Wyoming Community Viz TM Partnership Phase I Pilot: Aquifer Protection and Community Viz TM in Albany County, Wyoming |
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Document Status
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Documented, not peer reviewed | Peer reviewed and published | * | * | Other or unclear (explain in Comment) | Not peer reviewed but is published (explain in Comment) |
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Comments on Status
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Published USDA Forest Service report | Published journal manuscript | * | Published report | Published report | Published report |
Software and Access (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
| http://firelab.org/project/farsite | Not applicable | * | https://www.epa.gov/water-research/visualizing-ecosystem-land-management-assessments-velma-model-20 | https://ipac.ecosphere.fws.gov/ | https://communityviz.com/ | |
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Contact Name
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Charles McHugh | Sean R. Griffin | Gregg Lomnicky | Robert B. McKane | USFWS | Scott Lieske |
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Contact Address
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RMRS Missoula Fire Sciences Laboratory, 5775 US Highway 10 West, Missoula, MT 59808 | Department of Ecology, Evolution, and Natural Resources, Rutgers University, New Brunswick, NJ 08901, U.S.A. | 200 SW 35th St., Corvallis, OR, 97333 | U.S. EPA, Office of Research and Development, National Health and Environmental Effects Research Laboratory, Western Ecology Division, Corvallis, Oregon 97333 | 911 NE 11th Avenue Portland, OR 97232 | Department of Agricultural & Applied Economics University of Wyoming, Laramie WY 82071 |
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Contact Email
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cmchugh@fs.fed.us | srgriffin108@gmail.com | lomnicky.gregg@epa.gov | mckane.bob@epa.gov | fwhq_ipac@fws.gov | lieske@uwyo.edu |
EM Description (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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Summary Description
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ABSTRACT: "The development of a mathematical model for predicting rate of fire spread and intensity applicable to a wide range of wildland fuels is presented from the conceptual stage through evaluation and demonstration of results to hypothetical fuel models. The model was developed for and is now being used as a basis for appraising fire spread and intensity in the National Fire Danger Rating System. The initial work was done using fuel arrays composed of uniform size particles. Three fuel sizes were tested over a wide range of bulk densities. These were 0.026-inch-square cut excelsior, 114-inch sticks, and 112-inch sticks. The problem of mixed fuel sizes was then resolved by weighting the various particle sizes that compose actual fuel arrays by either surface area or loading, depending upon the feature of the fire being predicted. The model is complete in the sense that no prior knowledge of a fuel's burning characteristics is required. All that is necessary are inputs describing the physical and chemical makeup of the fuel and the environmental conditions in which it is expected to burn. Inputs include fuel loading, fuel depth, fuel particle surface-area-to-volume ratio, fuel particle heat content, fuel particle moisture and mineral content, and the moisture content at which extinction can be expected. Environmental inputs are mean wind velocity and slope of terrain. For heterogeneous mixtures, the fuel properties are entered for each particle size. The model as originally conceived was for dead fuels in a uniform stratum contiguous to the ground, such as litter or grass. It has been found to be useful, however, for fuels ranging from pine needle litter to heavy logging slash and for California brush fields." **FARSITE4 will no longer be supported or available for download or further supported. FlamMap6 now includes FARSITE.** | ABSTRACT: "Restoration efforts often focus on plants, but additionally require the establishment and long-term persistence of diverse groups of nontarget organisms, such as bees, for important ecosystem functions and meeting restoration goals. We investigated long-term patterns in the response of bees to habitat restoration by sampling bee communities along a 26-year chronosequence of restored tallgrass prairie in north-central Illinois, U.S.A. Specifically, we examined how bee communities changed over time since restoration in terms of (1) abundance and richness, (2) community composition, and (3) the two components of beta diversity, one-to-one species replacement, and changes in species richness. Bee abundance and raw richness increased with restoration age from the low level of the pre-restoration (agricultural) sites to the target level of the remnant prairie within the first 2–3 years after restoration, and these high levels were maintained throughout the entire restoration chronosequence. Bee community composition of the youngest restored sites differed from that of prairie remnants, but 5–7 years post-restoration the community composition of restored prairie converged with that of remnants. Landscape context, particularly nearby wooded land, was found to affect abundance, rarefied richness, and community composition. Partitioning overall beta diversity between sites into species replacement and richness effects revealed that the main driver of community change over time was the gradual accumulation of species, rather than one-to-one species replacement. At the spatial and temporal scales we studied, we conclude that prairie restoration efforts targeting plants also successfully restore bee communities." | ABSTRACT: [Sport fishing is an important recreational and economic activity, especially in Australia, Europe and North America, and the condition of sport fish populations is a key ecological indicator of water body condition for millions of anglers and the public. Despite its importance as an ecological indicator representing the status of sport fish populations, an index for measuring this ecosystem service has not been quantified by analyzing actual fish taxa, size and abundance data across the U.S.A. Therefore, we used game fish data collected from 1,561 stream and river sites located throughout the conterminous U.S.A. combined with specific fish species and size dollar weights to calculate site-specific recreational fishery index (RFI) scores. We then regressed those scores against 38 potential site-specific environmental predictor variables, as well as site-specific fish assemblage condition (multimetric index; MMI) scores based on entire fish assemblages, to determine the factors most associated with the RFI scores. We found weak correlations between RFI and MMI scores and weak to moderate correlations with environmental variables, which varied in importance with each of 9 ecoregions. We conclude that the RFI is a useful indicator of a stream ecosystem service, which should be of greater interest to the U.S.A. public and traditional fishery management agencies than are MMIs, which tend to be more useful for ecologists, environmentalists and environmental quality agencies.] | VELMA – Visualizing Ecosystems for Land Management Assessments - is a spatially distributed, eco-hydrological model that links a land surface hydrology model with a terrestrial biogeochemistry model for simulating the integrated responses of vegetation, soil, and water resources to interacting stressors. For example, VELMA can simulate how changes in climate and land use interact to affect soil water storage, surface and subsurface runoff, vertical drainage, evapotranspiration, vegetation and soil carbon and nitrogen dynamics, and transport of nitrate, ammonium, and dissolved organic carbon and nitrogen to water bodies. VELMA differs from other existing eco-hydrology models in its simplicity, flexibility, and theoretical foundation. The model has a user-friendly Graphics User Interface (GUI) for easy input of model parameter values. In addition, advanced visualization of simulation results can enhance understanding of results and underlying concepts. VELMA’s visualization and interactivity features are packaged in an open-source, open-platform programming environment (Java / Eclipse). The development team for VELMA version 2.0 includes Dr. Bob McKane and coworkers at the U.S. Environmental Protection Agency’s Western Ecology Division, Dr. Marc Stieglitz and coworkers at the Georgia Institute of Technology, and Dr. Feifei Pan at the University of North Texas. AUTHOR'S DESCRIPTION: "Understanding how disturbances such as harvest, fire and fertilization affect ecosystem services has been a major motivation in the development of VELMA. For example, how do disturbances such as forest harvest or the application of agronomic fertilizers affect hydrological and biogeochemical processes controlling water quality and quantity, carbon sequestration, production of greenhouse gases, etc.? Abdelnour et al. (2011, 2013) have already demonstrated the use of VELMA v1.0 to simulate the effects of forest clearcutting on ecohydrological processes that regulate a variety of ecosystem services. With the addition of a tissue-specific plant biomass (LSR) simulator and an enhanced GUI, VELMA v2.0 significantly expands the detail, flexibility, and ease of use for simulating disturbance effects. Currently available disturbance models include: - BurnDisturbanceModel, effects of fire. - GrazeDisturbanceModel, effects of grazing. - FertilizeLsrDisturbanceModel, effects of fertilizer applications. - HarvestLsrDisturbanceModel, effects of biomass harvest. Each of these disturbance models specifies where and when a disturbance event will occur. The Burn, Graze and Harvest models have options for specifying how much of each plant tissue and detritus pool (leaves, stems, roots) will be removed and where it goes (offsite and/or to a specified onsite C and N pools). The Fertilize model has options for applying nitrogen as ammonium, nitrate, urea and/or manure." | IPaC is a project planning tool that streamlines the USFWS environmental review process. Explores species and habitat: See if any listed species, critical habitat, migratory birds or other natural resources may be impacted by your project. Using the map tool, explore other resources in your location, such as wetlands, wildlife refuges, GAP land cover, and other important biological resources. Conduct a regulatory review: Log in and define a project to get an official species list and evaluate potential impacts on resources managed by the U.S. Fish and Wildlife Service. Follow IPaC's Endangered Species Act (ESA) Review process—a streamlined, step-by-step consultation process available in select areas for certain project types, agencies, and species. Build a Consultation Package: Consultation Package Builder (CPB) replaces and improves on the original Impact Analysis by providing an interactive, step-by-step process to help you prepare a full consultation package leveraging U.S. Fish and Wildlife Service data and recommendations, including conservation measures designed to help you avoid or minimize effects to listed species. | The Wyoming Community VizTM Partnership was established in 2001 to promote the use of geographic information system-based planning support systems and related decision support technologies in community land-use planning and economic development activities in the State of Wyoming. Partnership members include several state agencies, local governments and several nongovernment organizations. Partnership coordination is provided by the Wyoming Rural Development Council. Research and technical support is coordinated by the Wyoming Geographic Information Science Center’s Spatial Decision Support System Research Program at the University of Wyoming. In June 2002, the Partnership initiated a three-phase plan to promote Community VizTM based planning support systems in Wyoming. Phase I of the Partnership plan was a “proof of concept” pilot project set in Albany County in southeastern Wyoming. The goal of the project was to demonstrate the application of Community VizTM to a Wyoming-specific issue (in this case, aquifer protection) and to determine potential challenges for broader adoption in terms of data requirements, computing infrastructure and technological expertise. The results of the Phase I pilot project are detailed in this report. Efforts are currently underway to secure funding for Phase II of the plan, which expands the use of Community VizTM into four additional Wyoming communities. Specific Phase II objectives are to expand the type and number of issues addressed by Community VizTM and increase the use of Community VizTM in the planning process. As a part of Phase II the Partnership will create a technical assistance network aimed at assisting communities with the technical challenges in applying the software to their planning issues. The third phase will expand the program to more communities in the state, maintain the technical assistance network, and monitor the impact of Community VizTM on the planning process. |
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Specific Policy or Decision Context Cited
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* | None identified | * | * | Determination of Effects on ESA listed taxa. | None provided |
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Biophysical Context
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Not applicable | The Nachusa Grasslands consists of over 1,900 ha of restored prairie plantings, prairie remnants, and other habitats such as wetlands and oak savanna. The area is generally mesic with an average annual precipitation of 975 mm, and most precipitation occurs during the growing season. | None | No additional description provided | N/A | Groundwater recharge area, City of Laramie |
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EM Scenario Drivers
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* | No scenarios presented | N/A | * | N/A | Continuation of trends |
EM Relationship to Other EMs or Applications
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EM ID
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New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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Method Only, Application of Method or Model Run
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Method Only | Method + Application (multiple runs exist) | Method + Application | Method Only | Method Only | Model Run Associated with a Specific EM Application |
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New or Pre-existing EM?
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New or revised model | New or revised model | New or revised model | New or revised model | New or revised model | Continuation of trends |
Related EMs (for example, other versions or derivations of this EM) described in ESML
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EM ID
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New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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Document ID for related EM
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None | None | None | Doc-13 | Doc-317 | Doc-366 | Doc-359 | None | Doc-473 |
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EM ID for related EM
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None | None | None | EM-883 | EM-884 | EM-375 | EM-379 | EM-380 | EM-605 | EM-892 | None | None |
EM Modeling Approach
EM Relationship to Time (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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EM Temporal Extent
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Not applicable | 1988-2014 | 2013-2014 | Not applicable | Not applicable | 2050 |
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EM Time Dependence
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Not applicable | time-stationary | time-dependent | time-dependent | * | * |
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EM Time Reference (Future/Past)
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* | Not applicable | past time | * | * | * |
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EM Time Continuity
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* | Not applicable | discrete | discrete | * | * |
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EM Temporal Grain Size Value
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* | Not applicable | 1 | 1 | * | * |
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EM Temporal Grain Size Unit
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* | Not applicable | Year | Day | * | * |
EM spatial extent (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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Bounding Type
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Not applicable | Physiographic or ecological | Geopolitical | Not applicable | Not applicable | Watershed/Catchment/HUC |
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Spatial Extent Name
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Not applicable | Nachusa Grasslands | United States | Not applicable | Not applicable | Laramie City's aquifer protection area |
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Spatial Extent Area (Magnitude)
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Not applicable | 10-100 km^2 | >1,000,000 km^2 | Not applicable | Not applicable | * |
Spatial Distribution of Computations (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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EM Spatial Distribution
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Not applicable | spatially distributed (in at least some cases) | * | * | spatially lumped (in all cases) | spatially lumped (in all cases) |
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Spatial Grain Type
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Not applicable | other (specify), for irregular (e.g., stream reach, lake basin) | length, for linear feature (e.g., stream mile) | area, for pixel or radial feature | Not applicable | Not applicable |
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Spatial Grain Size
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Not applicable | Area varies by site | stream reach (site) | user defined | Not applicable | Not applicable |
EM Structure and Computation Approach (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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EM Computational Approach
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* | Analytic | * | Numeric | Other or unclear (comment) | Numeric |
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EM Determinism
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* | deterministic | * | * | Not applicable | * |
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Statistical Estimation of EM
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* | * |
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* |
Model Checking Procedures Used (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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Model Calibration Reported?
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Not applicable | No | * | Not applicable | Not applicable | Unclear |
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Model Goodness of Fit Reported?
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Not applicable | No | * | Not applicable | Not applicable | * |
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Goodness of Fit (metric| value | unit)
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* | None | * | * | * | * |
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Model Operational Validation Reported?
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* | No | * | Not applicable | Not applicable | Unclear |
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Model Uncertainty Analysis Reported?
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Not applicable | No | * | Not applicable | Not applicable | Unclear |
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Model Sensitivity Analysis Reported?
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Not applicable | No | * | Not applicable | Not applicable | Unclear |
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Model Sensitivity Analysis Include Interactions?
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* | Not applicable | * | * | * | * |
EM Locations, Environments, Ecology
Location of EM Application (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
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| New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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* | * |
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Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
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| New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
| * | None | * | * | * | * |
Centroid Lat/Long (Decimal Degree)
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EM ID
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New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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Centroid Latitude
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-9999 | 41.89 | 36.21 | Not applicable | Not applicable | 41.31 |
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Centroid Longitude
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-9999 | -89.34 | -113.76 | Not applicable | Not applicable | -105.46 |
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Centroid Datum
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Not applicable | WGS84 | * | Not applicable | Not applicable | * |
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Centroid Coordinates Status
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Not applicable | Provided | Estimated | Not applicable | Not applicable | Estimated |
Environments and Scales Modeled (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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EM Environmental Sub-Class
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Terrestrial Environment (sub-classes not fully specified) | Agroecosystems | Grasslands | Rivers and Streams | Terrestrial Environment (sub-classes not fully specified) | Aquatic Environment (sub-classes not fully specified) | Rivers and Streams | Inland Wetlands | Lakes and Ponds | Near Coastal Marine and Estuarine | Open Ocean and Seas | Ground Water | Terrestrial Environment (sub-classes not fully specified) | Forests | Agroecosystems | Created Greenspace | Grasslands | Scrubland/Shrubland | Barren | Tundra | Ice and Snow | Atmosphere | Ground Water | Terrestrial Environment (sub-classes not fully specified) |
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Specific Environment Type
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Not applicable | Restored prairie, prairie remnants, and cropland | reach | Terrestrial environment sub-classes | None | watershed |
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EM Ecological Scale
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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 | Ecological scale is finer than that of the Environmental Sub-class | Not applicable | * |
Organisms modeled (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
Scale of differentiation of organisms modeled
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EM ID
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New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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EM Organismal Scale
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Not applicable | Species | Guild or Assemblage | Not applicable |
Other (Comment) ?Comment:ESA designations include species and Ecological Significan Units of species |
Not applicable |
Taxonomic level and name of organisms or groups identified
taxonomyHelp
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| New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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* | * | * | * |
EnviroAtlas URL
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| New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
| Average Annual Precipitation | GAP Ecological Systems | None Available | Carbon storage by tree biomass (kg/m2), Ecosystem Markets: Imperiled Species and Habitats | GAP Ecological Systems, Percent GAP Status 1 & 2 | Dasymetric Allocation of Population, Total Annual Reduced Nitrogen Deposition, Employment Rate |
EM Ecosystem Goods and Services (EGS) potentially modeled, by classification system
* Note that run information is shown only where run data differ from the "parent" entry shown at left
CICES v 4.3 - Common International Classification of Ecosystem Services (Section > Division > Group > Class)
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| New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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(Environmental Subclass > Ecological End-Product (EEP) > EEP Subclass > EEP Modifier)
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| New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
| * | None |
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EM Variable Names (and Units)
* Note that for runs, variable name is displayed only where data for that variable differed by run AND those differences were reported in the source document. Where differences occurred but were not reported, the variable is not listed. Click on variable name to view details.
Predictor
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Intermediate
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EM ID
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New or revised model | EM-788 | New or revised model | New or revised model | New or revised model | Continuation of trends |
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Intermediate (Computed) Variables (and Units)
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None | * |
Response
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