EcoService Models Library (ESML)
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Compare EMs
Which comparison is best for me?EM Variables by Variable Role
One quick way to compare ecological models (EMs) is by comparing their variables. Predictor variables show what kinds of influences a model is able to account for, and what kinds of data it requires. Response variables show what information a model is capable of estimating.
This first comparison shows the names (and units) of each EM’s variables, side-by-side, sorted by variable role. Variable roles in ESML are as follows:
- Predictor Variables
- Time- or Space-Varying Variables
- Constants and Parameters
- Intermediate (Computed) Variables
- Response Variables
- Computed Response Variables
- Measured Response Variables
EM Variables by Category
A second way to use variables to compare EMs is by focusing on the kind of information each variable represents. The top-level categories in the ESML Variable Classification Hierarchy are as follows:
- Policy Regarding Use or Management of Ecosystem Resources
- Land Surface (or Water Body Bed) Cover, Use or Substrate
- Human Demographic Data
- Human-Produced Stressor or Enhancer of Ecosystem Goods and Services Production
- Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services
- Non-monetary Indicators of Human Demand, Use or Benefit of Ecosystem Goods and Services
- Monetary Values
Besides understanding model similarities, sorting the variables for each EM by these 7 categories makes it easier to see if the compared models can be linked using similar variables. For example, if one model estimates an ecosystem attribute (in Category 5), such as water clarity, as a response variable, and a second model uses a similar attribute (also in Category 5) as a predictor of recreational use, the two models can potentially be used in tandem. This comparison makes it easier to spot potential model linkages.
All EM Descriptors
This selection allows a more detailed comparison of EMs by model characteristics other than their variables. The 50-or-so EM descriptors for each model are presented, side-by-side, in the following categories:
- EM Identity and Description
- EM Modeling Approach
- EM Locations, Environments, Ecology
- EM Ecosystem Goods and Services (EGS) potentially modeled, by classification system
EM Descriptors by Modeling Concepts
This feature guides the user through the use of the following seven concepts for comparing and selecting EMs:
- Conceptual Model
- Modeling Objective
- Modeling Context
- Potential for Model Linkage
- Feasibility of Model Use
- Model Certainty
- Model Structural Information
Though presented separately, these concepts are interdependent, and information presented under one concept may have relevance to other concepts as well.
EM Identity and Description
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EM ID
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EM-374 | EM-449 |
EM-618 |
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EM Short Name
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InVEST carbon storage and sequestration (v3.2.0) | Decrease in erosion (shoreline), St. Croix, USVI | WaterWorld v2, Santa Basin, Peru |
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EM Full Name
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InVEST v3.2.0 Carbon storage and sequestration | Decrease in erosion (shoreline) by reef, St. Croix, USVI | WaterWorld v2, Santa Basin, Peru |
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EM Source or Collection
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InVEST | US EPA | None |
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EM Source Document ID
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315 | 335 | 368 |
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Document Author
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The Natural Capital Project | Yee, S. H., Dittmar, J. A., and L. M. Oliver | Van Soesbergen, A. and M. Mulligan |
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Document Year
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2015 | 2014 | 2018 |
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Document Title
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Carbon storage and sequestration - InVEST (v3.2.0) | Comparison of methods for quantifying reef ecosystem services: A case study mapping services for St. Croix, USVI | Potential outcomes of multi-variable climate change on water resources in the Santa Basin, Peru |
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Document Status
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Peer reviewed and published | Peer reviewed and published | Peer reviewed and published |
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Comments on Status
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Website | Published journal manuscript | Published journal manuscript |
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EM ID
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EM-374 | EM-449 |
EM-618 |
| https://www.naturalcapitalproject.org/invest/ | Not applicable | www.policysupport.org/waterworld | |
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Contact Name
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The Natural Capital Project | Susan H. Yee | Arnout van Soesbergen |
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Contact Address
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371 Serra Mall Stanford University Stanford, CA 94305-5020 USA | US EPA, Office of Research and Development, NHEERL, Gulf Ecology Division, Gulf Breeze, FL 32561, USA | Environmental Dynamics Research Group, Dept. of Geography, King's College London, Strand, London WC2R 2LS, UK |
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Contact Email
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invest@naturalcapitalproject.org | yee.susan@epa.gov | arnout.van_soesbergen@kcl.ac.uk |
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EM ID
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EM-374 | EM-449 |
EM-618 |
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Summary Description
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Please note: This ESML entry describes an InVEST model version that was current as of 2015. More recent versions may be available at the InVEST website. ABSTRACT: "Terrestrial ecosystems, which store more carbon than the atmosphere, are vital to influencing carbon dioxide-driven climate change. The InVEST model uses maps of land use and land cover types and data on wood harvest rates, harvested product degradation rates, and stocks in four carbon pools (aboveground biomass, belowground biomass, soil, dead organic matter) to estimate the amount of carbon currently stored in a landscape or the amount of carbon sequestered over time. Additional data on the market or social value of sequestered carbon and its annual rate of change, and a discount rate can be used in an optional model that estimates the value of this environmental service to society. Limitations of the model include an oversimplified carbon cycle, an assumed linear change in carbon sequestration over time, and potentially inaccurate discounting rates." AUTHOR'S DESCRIPTION: "A fifth optional pool included in the model applies to parcels that produce harvested wood products (HWPs) such as firewood or charcoal or more long-lived products such as house timbers or furniture. Tracking carbon in this pool is useful because it represents the amount of carbon kept from the atmosphere by a given product." | ABSTRACT: "...We investigated and compared a number of existing methods for quantifying ecological integrity, shoreline protection, recreational opportunities, fisheries production, and the potential for natural products discovery from reefs. Methods were applied to mapping potential ecosystem services production around St. Croix, U.S. Virgin Islands. Overall, we found that a number of different methods produced similar predictions." AUTHOR'S DESCRIPTION: "A number of methods have been developed for linking biophysical attributes of reef condition, such as reef structural complexity, fish biomass, or species richness, to provisioning of ecosystem goods and services (Principe et al., 2012). We investigated the feasibility of using existing methods and data for mapping production of reef ecosystem goods and services. We applied these methods toward mapping potential ecosystem goods and services production in St. Croix, U.S. Virgin Islands (USVI)...For each of the five categories of ecosystem services, we chose a suite of models and indices for estimating potential production based on relative ease of implementation, consisting of well-defined parameters, and likely availability of input data, to maximize potential for transferability to other locations. For each method, we assembled the necessary reef condition and environmental data as spatial data layers for St. Croix (Table1). The coastal zone surrounding St. Croix was divided into 10x10 m grid cells, and production functions were applied to quantify ecosystem services provisioning in each grid cell...Shoreline protection as an ecosystem service has been defined in a number of ways including protection from shoreline erosion...and can thus be estimated as % Decrease in erosion due to reef = 1 - (Ho/H)^2.5 where Ho is the attenuated wave height due to the presence of the reef and H is wave height in the absence of the reef." | ABSTRACT: "Water resources in the Santa basin in the Peruvian Andes are increasingly under pressure from climate change and population increases. Impacts of temperature-driven glacier retreat on stream flow are better studied than those from precipitation changes, yet present and future water resources are mostly dependent on precipitation which is more difficult to predict with climate models. This study combines a broad range of projections from climate models with a hydrological model (WaterWorld), showing a general trend towards an increase in water availability due to precipitation increases over the basin. However, high uncertainties in these projections necessitate the need for basin-wide policies aimed at increased adaptability." AUTHOR'S DESCRIPTION: "WaterWorld is a fully distributed, process-based hydrological model that utilises remotely sensed and globally available datasets to support hydrological analysis and decision-making at national and local scales globally, with a particular focus on un-gauged and/or data-poor environments, which makes it highly suited to this study. The model (version 2) currently runs on either 10 degree tiles, large river basins or countries at 1-km2 resolution or 1 degree tiles at 1-ha resolution utilising different datasets. It simulates a hydrological baseline as a mean for the period 1950-2000 and can be used to calculate the hydrological impact of scenarios of climate change, land use change, land management options, impacts of extractives (oil & gas and mining) and impacts of changes in population and demography as well as combinations of these. The model is ‘self parameterising’ (Mulligan, 2013a) in the sense that all data required for model application anywhere in the world is provided with the model, removing a key barrier to model application. However, if users have better data than those provided, it is possible to upload these to WaterWorld as GIS files and use them instead. Results can be viewed visually within the web browser or downloaded as GIS maps. The model’s equations and processes are described in more detail in Mulligan and Burke (2005) and Mulligan (2013b). The model parameters are not routinely calibrated to observed flows as it is designed for hydrological scenario analysis in which the physical basis of its parameters must be retained and the model is also often used in un-gauged basins. Calibration is inappropriate under these circumstances (Sivapalan et al., 2003). The freely available nature of the model means that anyone can apply it and replicate the results shown here. WaterWorld’s (V2) snow and ice module is capable of simulating the processes of melt water production, snow fall and snow pack, making this version highly suited to the current application. The model component is based on a full energy-balance for snow accumulation and melting based on Walter et al., (2005) with input data provided globally by the SimTerra database (Mulligan, 2011) upon which the model r |
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Specific Policy or Decision Context Cited
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None identified | None identified | None identified |
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Biophysical Context
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Not applicable | No additional description provided | Large river valley located on the western slope of the Peruvian Andes between the Cordilleras Blanca and Negra. Precipitation is distinctly seasonal. |
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EM Scenario Drivers
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Optional future scenarios for changed LULC and wood harvest | No scenarios presented | Scenarios base on high growth and 3.5oC warming by 2100, and scenarios based on moderate growth and 2.5oC warming by 2100 |
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EM ID
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EM-374 | EM-449 |
EM-618 |
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Method Only, Application of Method or Model Run
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Method Only | Method + Application | Method + Application (multiple runs exist) View EM Runs |
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New or Pre-existing EM?
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New or revised model | Application of existing model | Application of existing model |
Related EMs (for example, other versions or derivations of this EM) described in ESML
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EM ID
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EM-374 | EM-449 |
EM-618 |
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Document ID for related EM
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Doc-309 | Doc-335 | None |
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EM ID for related EM
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EM-349 | EM-447 | EM-448 | None |
EM Modeling Approach
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EM ID
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EM-374 | EM-449 |
EM-618 |
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EM Temporal Extent
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Not applicable | 2006-2007, 2010 | 1950-2071 |
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EM Time Dependence
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time-dependent | time-stationary | time-dependent |
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EM Time Reference (Future/Past)
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future time | Not applicable | both |
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EM Time Continuity
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discrete | Not applicable | discrete |
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EM Temporal Grain Size Value
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1 | Not applicable | 1 |
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EM Temporal Grain Size Unit
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Year | Not applicable | Month |
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EM ID
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EM-374 | EM-449 |
EM-618 |
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Bounding Type
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Not applicable | Physiographic or ecological | Watershed/Catchment/HUC |
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Spatial Extent Name
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Not applicable | Coastal zone surrounding St. Croix | Santa Basin |
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Spatial Extent Area (Magnitude)
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Not applicable | 100-1000 km^2 | 10,000-100,000 km^2 |
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EM ID
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EM-374 | EM-449 |
EM-618 |
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EM Spatial Distribution
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spatially distributed (in at least some cases) | spatially distributed (in at least some cases) | spatially distributed (in at least some cases) |
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Spatial Grain Type
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area, for pixel or radial feature | area, for pixel or radial feature | area, for pixel or radial feature |
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Spatial Grain Size
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application specific | 10 m x 10 m | 1 km2 |
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EM ID
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EM-374 | EM-449 |
EM-618 |
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EM Computational Approach
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Analytic | Analytic | Numeric |
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EM Determinism
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deterministic | deterministic | deterministic |
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Statistical Estimation of EM
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EM ID
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EM-374 | EM-449 |
EM-618 |
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Model Calibration Reported?
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Not applicable | Yes | No |
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Model Goodness of Fit Reported?
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Not applicable | No | No |
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Goodness of Fit (metric| value | unit)
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None | None | None |
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Model Operational Validation Reported?
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Not applicable | Yes | Yes |
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Model Uncertainty Analysis Reported?
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Not applicable | No | No |
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Model Sensitivity Analysis Reported?
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Not applicable | No | No |
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Model Sensitivity Analysis Include Interactions?
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Not applicable | Not applicable | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
| EM-374 | EM-449 |
EM-618 |
| None | None |
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Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
| EM-374 | EM-449 |
EM-618 |
| None |
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None |
Centroid Lat/Long (Decimal Degree)
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EM ID
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EM-374 | EM-449 |
EM-618 |
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Centroid Latitude
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-9999 | 17.73 | -9.05 |
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Centroid Longitude
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-9999 | -64.77 | -77.81 |
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Centroid Datum
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Not applicable | WGS84 | WGS84 |
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Centroid Coordinates Status
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Not applicable | Estimated | Estimated |
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EM ID
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EM-374 | EM-449 |
EM-618 |
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EM Environmental Sub-Class
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Not applicable | Near Coastal Marine and Estuarine | Rivers and Streams | Terrestrial Environment (sub-classes not fully specified) |
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Specific Environment Type
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Terrestrial environments, but not specified for methods | Coral reefs | tropical, coastal to montane |
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EM Ecological Scale
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Not applicable | Ecological scale is finer than that of the Environmental Sub-class |
Other or unclear (comment) ?Comment:Variable data was derived from multiple climate data stations distrubuted across the study area. The location and distribution of the data stations was not provided. |
Scale of differentiation of organisms modeled
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EM ID
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EM-374 | EM-449 |
EM-618 |
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EM Organismal Scale
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Not applicable | Not applicable | Not applicable |
Taxonomic level and name of organisms or groups identified
| EM-374 | EM-449 |
EM-618 |
| None Available | None Available | None Available |
EnviroAtlas URL
| EM-374 | EM-449 |
EM-618 |
| GAP Ecological Systems, Carbon Storage by Tree Biomass, Hectares of cotton crops | National Hydrography Dataset Plus (NHD PlusV2) | Average Annual Precipitation |
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-374 | EM-449 |
EM-618 |
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<a target="_blank" rel="noopener noreferrer" href="https://www.epa.gov/eco-research/national-ecosystem-services-classification-system-nescs-plus">National Ecosystem Services Classification System (NESCS) Plus</a>
(Environmental Subclass > Ecological End-Product (EEP) > EEP Subclass > EEP Modifier)
| EM-374 | EM-449 |
EM-618 |
| None |
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