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-186 ![]() |
EM-779 ![]() |
EM Short Name
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FORCLIM v2.9, Western OR, USA | Arthropod flower preference, CA, USA |
EM Full Name
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FORCLIM (FORests in a changing CLIMate) v2.9, Western OR, USA | Arthropod flower type preference, California, USA |
EM Source or Collection
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US EPA | None |
EM Source Document ID
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23 ?Comment:Related document ID 22 is a secondary source providing tree species specific parameters in appendix. |
399 |
Document Author
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Busing, R. T., Solomon, A. M., McKane, R. B. and Burdick, C. A. | Lundin, O., Ward, K.L., and N.M. Williams |
Document Year
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2007 | 2018 |
Document Title
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Forest dynamics in Oregon landscapes: evaluation and application of an individual-based model | Indentifying native plants for coordinated hanbitat manegement of arthroppod pollinators, herbivores and natural enemies |
Document Status
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Peer reviewed and published | Peer reviewed and published |
Comments on Status
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Published journal manuscript | Published journal manuscript |
EM ID
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EM-186 ![]() |
EM-779 ![]() |
Not applicable | Not applicable | |
Contact Name
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Richard T. Busing | Ola Lundin |
Contact Address
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U.S. Geological Survey, 200 SW 35th Street, Corvallis, Oregon 97333 USA | Department of Ecology, Swedish Univ. of Agricultural Sciences, Uppsala, Sweden |
Contact Email
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rtbusing@aol.com | ola.lundin@slu.se |
EM ID
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EM-186 ![]() |
EM-779 ![]() |
Summary Description
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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…The simulation of both stand-replacing and partial-stand disturbances across western Oregon improved agreement between simulated and actual data." Western Oregon forested ecoregions (Omernick classification) were Coastal Volcanics (1d), Mid-coastal Sedimentary (1g), Willamette Valley (3), West Cascade Lowlands (4a), West Cascade Montane (4b), Cascade Crest (4c), East Cascade Ponderosa Pine (9d), and East Cascade Pumice Plateau (9e). | ABSTRACT: " Plant species differed in attractiveness for each arthropod functional group. Floral area of the focal plant species positively affected honeybee, predator, and parasitic wasp attractiveness. Later bloom period was associated with lower numbers of parasitic wasps. Flower type (actinomorphic, composite, or zygomorphic) predicted attractiveness for honeybees, which preferred actinomorphic over composite flowers and for parasitic wasps, which preferred composite flowers over actinomorphic flowers. 4. Across plant species, herbivore, predator, and parasitic wasp abundances were positively correlated, and honeybee abundance correlated negatively to herbivore abundance. 5. Synthesis and applications. We use data from our common garden experiment to inform evidence-based selection of plants that support pollinators and natural enemies without enhancing potential pests. We recommend selecting plant species with a high floral area per ground area unit, as this metric predicts the abundances of several groups of beneficial arthropods. Multiple correlations between functionally important arthropod groups across plant species stress the importance of a multifunctional approach to arthropod habitat management. " Changes in arthropod abundance were estimated for flower type (entered as separate runs); Actinomorphic, Composite, Zygomorphic. 43 plant species evaluated included Amsinckia intermedia, Calandrinia menziesii, Nemophila maculata, Nemophila menziesii, Phacelia ciliata, Achillea millefolium, Collinsia heterophylla, Fagopyrum esculentum, Lasthenia fremontii, Lasthenia glabrata, Limnanthes alba, Lupinus microcarpus densiflorus, Lupinus succelentus, Phacelia californica, Phacelia campanularia, Phacelia tanacetifolia, Salvia columbariae, Sphaeralcea ambigua, Trifolium fucatum, Trifolium gracilentum, Antirrhinum conutum, Clarkia purpurea, Clarkia unguiculata, Clarkia williamsonii, Eriophyllum lanatum, Eschscholzia californica, Monardella villosa, Scrophularia californica, Asclepia eriocarpa, Asclepia fascicularis, Camissoniopsis Cheiranthifolia, Eriogonum fasciculatum, Gilia capitata, Grindelia camporum, Helianthus annuus, Lupinus formosus, Malacothrix saxatilis, Oenothera elata, Helianthus bolanderi, Helianthus californicus, Madia elegans, Trichostema lanceolatum, Heterotheca grandiflora." |
Specific Policy or Decision Context Cited
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None Identified | None reported |
Biophysical Context
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Coastal to montane, Pacific Northwest US (Oregon) forests. | Mediteranean climate |
EM Scenario Drivers
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Two scenarios modelled, forests with and without fire | Arthropod groups |
EM ID
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EM-186 ![]() |
EM-779 ![]() |
Method Only, Application of Method or Model Run
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Method + Application (multiple runs exist) View EM Runs ?Comment:Related document ID 22 is a secondary source providing tree species specific parameters in appendix. |
Method + Application (multiple runs exist) View EM Runs |
New or Pre-existing EM?
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Application of existing model | New or revised model |
Related EMs (for example, other versions or derivations of this EM) described in ESML
EM ID
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EM-186 ![]() |
EM-779 ![]() |
Document ID for related EM
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Doc-22 | Doc-23 ?Comment:Related document ID 22 provides tree species specific parameters in appendix. |
None |
EM ID for related EM
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EM-146 | EM-208 | EM-224 | None |
EM Modeling Approach
EM ID
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EM-186 ![]() |
EM-779 ![]() |
EM Temporal Extent
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>650 yrs | 2015-2016 |
EM Time Dependence
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time-dependent | time-stationary |
EM Time Reference (Future/Past)
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past time | Not applicable |
EM Time Continuity
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discrete | Not applicable |
EM Temporal Grain Size Value
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1 | Not applicable |
EM Temporal Grain Size Unit
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Year | Not applicable |
EM ID
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EM-186 ![]() |
EM-779 ![]() |
Bounding Type
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Physiographic or ecological | Point or points |
Spatial Extent Name
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Western Oregon, north of 43.00 N to Washington border | Harry Laidlaw Jr. Honey Bee Research facility |
Spatial Extent Area (Magnitude)
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10,000-100,000 km^2 | <1 ha |
EM ID
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EM-186 ![]() |
EM-779 ![]() |
EM Spatial Distribution
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spatially distributed (in at least some cases) | spatially lumped (in all cases) |
Spatial Grain Type
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area, for pixel or radial feature | Not applicable |
Spatial Grain Size
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0.08 ha | Not applicable |
EM ID
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EM-186 ![]() |
EM-779 ![]() |
EM Computational Approach
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Numeric | Numeric |
EM Determinism
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deterministic | deterministic |
Statistical Estimation of EM
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EM ID
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EM-186 ![]() |
EM-779 ![]() |
Model Calibration Reported?
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No | Not applicable |
Model Goodness of Fit Reported?
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No | Not applicable |
Goodness of Fit (metric| value | unit)
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None | None |
Model Operational Validation Reported?
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Yes | Not applicable |
Model Uncertainty Analysis Reported?
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No | No |
Model Sensitivity Analysis Reported?
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No | No |
Model Sensitivity Analysis Include Interactions?
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Not applicable | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
EM-186 ![]() |
EM-779 ![]() |
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Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
EM-186 ![]() |
EM-779 ![]() |
None | None |
Centroid Lat/Long (Decimal Degree)
EM ID
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EM-186 ![]() |
EM-779 ![]() |
Centroid Latitude
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44.66 | 38.54 |
Centroid Longitude
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-122.56 | -121.79 |
Centroid Datum
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WGS84 | WGS84 |
Centroid Coordinates Status
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Estimated | Provided |
EM ID
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EM-186 ![]() |
EM-779 ![]() |
EM Environmental Sub-Class
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Forests | Agroecosystems |
Specific Environment Type
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Primarily conifer forest | Agricultural fields |
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 |
Scale of differentiation of organisms modeled
EM ID
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EM-186 ![]() |
EM-779 ![]() |
EM Organismal Scale
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Species | Guild or Assemblage |
Taxonomic level and name of organisms or groups identified
EM-186 ![]() |
EM-779 ![]() |
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EnviroAtlas URL
EM-186 ![]() |
EM-779 ![]() |
GAP Ecological Systems, Average Annual Precipitation, U.S. EPA (Omernik) ecoregions | GAP Ecological Systems |
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-186 ![]() |
EM-779 ![]() |
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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-186 ![]() |
EM-779 ![]() |
None |
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