EcoService Models Library (ESML)
loading
Compare EMs
Which comparison is best for me?EM Variables by Variable Role
One quick way to compare ecological models (EMs) is by comparing their variables. Predictor variables show what kinds of influences a model is able to account for, and what kinds of data it requires. Response variables show what information a model is capable of estimating.
This first comparison shows the names (and units) of each EM’s variables, side-by-side, sorted by variable role. Variable roles in ESML are as follows:
- Predictor Variables
- Time- or Space-Varying Variables
- Constants and Parameters
- Intermediate (Computed) Variables
- Response Variables
- Computed Response Variables
- Measured Response Variables
EM Variables by Category
A second way to use variables to compare EMs is by focusing on the kind of information each variable represents. The top-level categories in the ESML Variable Classification Hierarchy are as follows:
- Policy Regarding Use or Management of Ecosystem Resources
- Land Surface (or Water Body Bed) Cover, Use or Substrate
- Human Demographic Data
- Human-Produced Stressor or Enhancer of Ecosystem Goods and Services Production
- Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services
- Non-monetary Indicators of Human Demand, Use or Benefit of Ecosystem Goods and Services
- Monetary Values
Besides understanding model similarities, sorting the variables for each EM by these 7 categories makes it easier to see if the compared models can be linked using similar variables. For example, if one model estimates an ecosystem attribute (in Category 5), such as water clarity, as a response variable, and a second model uses a similar attribute (also in Category 5) as a predictor of recreational use, the two models can potentially be used in tandem. This comparison makes it easier to spot potential model linkages.
All EM Descriptors
This selection allows a more detailed comparison of EMs by model characteristics other than their variables. The 50-or-so EM descriptors for each model are presented, side-by-side, in the following categories:
- EM Identity and Description
- EM Modeling Approach
- EM Locations, Environments, Ecology
- EM Ecosystem Goods and Services (EGS) potentially modeled, by classification system
EM Descriptors by Modeling Concepts
This feature guides the user through the use of the following seven concepts for comparing and selecting EMs:
- Conceptual Model
- Modeling Objective
- Modeling Context
- Potential for Model Linkage
- Feasibility of Model Use
- Model Certainty
- Model Structural Information
Though presented separately, these concepts are interdependent, and information presented under one concept may have relevance to other concepts as well.
EM Identity and Description
EM ID
em.detail.idHelp
?
|
EM-376 | EM-938 | EM-993 |
EM Short Name
em.detail.shortNameHelp
?
|
MIMES: For Massachusetts Ocean (v1.0) | OpenNSPECT v. 1.2 | Velma- 6PPD-Q concentrations, Seattle, WA |
EM Full Name
em.detail.fullNameHelp
?
|
Multi-scale Integrated Model of Ecosystem Services (MIMES) for the Massachusetts Ocean (v1.0) | OpenNSPECT v. 1.2 | VELMA: 6PPD-Quinone stormwater concentrations , Seattle, Washington |
EM Source or Collection
em.detail.emSourceOrCollectionHelp
?
|
US EPA | None | US EPA |
EM Source Document ID
|
316 | 431 | 465 |
Document Author
em.detail.documentAuthorHelp
?
|
Altman, I., R.Boumans, J. Roman, L. Kaufman | Eslinger, David L., H. Jamieson Carter, Matt Pendleton, Shan Burkhalter, Margaret Allen | Halama JJ, McKane RB, Barnhart BL, Pettus PP, Brookes AF, Adams AK, Gockel CK, Djang KS, Phan V, Chokshi SM, Graham JJ, Tian Z, Peter KT and Kolodziej,EP |
Document Year
em.detail.documentYearHelp
?
|
2012 | 2012 | 2024 |
Document Title
em.detail.sourceIdHelp
?
|
Multi-scale Integrated Model of Ecosystem Services (MIMES) for the Massachusetts Ocean (v1.0) | “OpenNSPECT: The Open-source Nonpoint Source Pollution and Erosion Comparison Tool.” NOAA Office for Coastal Management, Charleston, South Carolina. Accessed (11/2022) at https://coast.noaa.gov/digitalcoast/tools/opennspect.html | Watershed analysis of urban stormwater contaminant 6PPD-Quinone hotspots and stream concentrations using a process-based ecohydrological model |
Document Status
em.detail.statusCategoryHelp
?
|
Documented, not peer reviewed | Peer reviewed and published | Peer reviewed and published |
Comments on Status
em.detail.commentsOnStatusHelp
?
|
Published report | Webpage | Published journal manuscript |
EM ID
em.detail.idHelp
?
|
EM-376 | EM-938 | EM-993 |
http://www.afordablefutures.com/orientation-to-what-we-do | https://coast.noaa.gov/digitalcoast/tools/opennspect.html | Not reported | |
Contact Name
em.detail.contactNameHelp
?
|
Irit Altman | Not reported | Jonathan Halama |
Contact Address
|
Boston University, Portland, Maine | NOAA Coastal Services Center, 2234 South Hobson Avenue Charleston, South Carolina 29405-2413 | U.S. Environmental Protection Agency, Corvallis, OR |
Contact Email
|
iritaltman@bu.edu | Not reported | Halama.Jonathan@epa.gov |
EM ID
em.detail.idHelp
?
|
EM-376 | EM-938 | EM-993 |
Summary Description
em.detail.summaryDescriptionHelp
?
|
AUTHORS DESCRIPTION: "MIMES uses a systems approach to model ecosystem dynamics across a spatially explicit environment. The modeling platform used by this work is a commercially available, object-based modeling and simulation software. This model, referred to as Massachusetts Ocean MIMES, was applied to a selected area of Massachusetts’ coastal waters and nearshore waters. The model explores the implications of management decisions on select marine resources and economic production related to a suite of marine based economic sectors. | "This open-source version of the Nonpoint Source Pollution and Erosion Comparison Tool is used to investigate potential water quality impacts from climate change and development to other land uses. The downloadable tool is designed to be broadly applicable for coastal and noncoastal areas alike. Tool functions simulate erosion, pollution, and the accumulation from overland flow. OpenNSPECT uses spatial elevation data to calculate flow direction and flow accumulation throughout a watershed. To do this, land cover, precipitation, and soils data are processed to estimate runoff volume at both the local and watershed levels. Coefficients representing the contribution of each land cover class to the expected pollutant load are also applied to land cover data to approximate total pollutant loads. These coefficients are taken from published sources or can be derived from local water quality studies. The output layers display estimates of runoff volume, pollutant loads, pollutant concentration, and total sediment yield. Requires MapWindow GIS v.4.8.8 (open source software)" | ABSTRACT: "Coho salmon (Oncorhynchus kisutch) are highly sensitive to 6PPD-Quinone (6PPD-Q). Details of the hydrological and biogeochemical processes controlling spatial and temporal dynamics of 6PPD-Q fate and transport from points of deposition to receiving waters (e.g., streams, estuaries) are poorly understood. To understand the fate and transport of 6PPD and mechanisms leading to salmon mortality Visualizing Ecosystem Land Management Assessments (VELMA), an ecohydrological model developed by US Environmental Protection Agency (EPA), was enhanced to better understand and inform stormwater management planning by municipal, state, and federal partners seeking to reduce stormwater contaminant loads in urban streams draining to the Puget Sound National Estuary. This work focuses on the 5.5 km2 Longfellow Creek upper watershed (Seattle, Washington, United States), which has long exhibited high rates of acute urban runoff mortality syndrome in coho salmon. We present VELMA model results to elucidate these processes for the Longfellow Creek watershed across multiple scales–from 5-m grid cells to the entire watershed. Our results highlight hydrological and biogeochemical controls on 6PPD-Q flow paths, and hotspots within the watershed and its stormwater infrastructure, that ultimately impact contaminant transport to Longfellow Creek and Puget Sound. Simulated daily average 6PPD-Q and available observed 6PPD-Q peak in-stream grab sample concentrations (ng/L) corresponds within plus or minus 10 ng/L. Most importantly, VELMA’s high-resolution spatial and temporal analysis of 6PPD-Q hotspots provides a tool for prioritizing the locations, amounts, and types of green infrastructure that can most effectively reduce 6PPD-Q stream concentrations to levels protective of coho salmon and other aquatic species. " |
Specific Policy or Decision Context Cited
em.detail.policyDecisionContextHelp
?
|
None identified | None identified | Not reported |
Biophysical Context
|
No additional description provided | No additional description provided | 6PPD deposition from vehicle tire wear particles. |
EM Scenario Drivers
em.detail.scenarioDriverHelp
?
|
No scenarios presented | No scenarios presented | N/A |
EM ID
em.detail.idHelp
?
|
EM-376 | EM-938 | EM-993 |
Method Only, Application of Method or Model Run
em.detail.methodOrAppHelp
?
|
Method + Application | Method Only | Method + Application |
New or Pre-existing EM?
em.detail.newOrExistHelp
?
|
New or revised model | New or revised model | Application of existing model |
Related EMs (for example, other versions or derivations of this EM) described in ESML
EM ID
em.detail.idHelp
?
|
EM-376 | EM-938 | EM-993 |
Document ID for related EM
em.detail.relatedEmDocumentIdHelp
?
|
None | None | Doc-366 | Doc-423 | Doc-430 |
EM ID for related EM
em.detail.relatedEmEmIdHelp
?
|
None | EM-940 | None |
EM Modeling Approach
EM ID
em.detail.idHelp
?
|
EM-376 | EM-938 | EM-993 |
EM Temporal Extent
em.detail.tempExtentHelp
?
|
Not applicable | Not applicable | 9/2020-6/2021 |
EM Time Dependence
em.detail.timeDependencyHelp
?
|
time-dependent | time-stationary | time-dependent |
EM Time Reference (Future/Past)
em.detail.futurePastHelp
?
|
future time | Not applicable | past time |
EM Time Continuity
em.detail.continueDiscreteHelp
?
|
discrete | Not applicable | discrete |
EM Temporal Grain Size Value
em.detail.tempGrainSizeHelp
?
|
1 | Not applicable | 1 |
EM Temporal Grain Size Unit
em.detail.tempGrainSizeUnitHelp
?
|
Year | Not applicable | Day |
EM ID
em.detail.idHelp
?
|
EM-376 | EM-938 | EM-993 |
Bounding Type
em.detail.boundingTypeHelp
?
|
Physiographic or ecological | Not applicable | Watershed/Catchment/HUC |
Spatial Extent Name
em.detail.extentNameHelp
?
|
Massachusetts Ocean | Not applicable | Longfellow creek |
Spatial Extent Area (Magnitude)
em.detail.extentAreaHelp
?
|
1000-10,000 km^2. | Not applicable | 1-10 km^2 |
EM ID
em.detail.idHelp
?
|
EM-376 | EM-938 | EM-993 |
EM Spatial Distribution
em.detail.distributeLumpHelp
?
|
spatially distributed (in at least some cases) | spatially distributed (in at least some cases) | spatially lumped (in all cases) |
Spatial Grain Type
em.detail.spGrainTypeHelp
?
|
area, for pixel or radial feature | area, for pixel or radial feature | Not applicable |
Spatial Grain Size
em.detail.spGrainSizeHelp
?
|
1 km x1 km | 30 m | Not applicable |
EM ID
em.detail.idHelp
?
|
EM-376 | EM-938 | EM-993 |
EM Computational Approach
em.detail.emComputationalApproachHelp
?
|
Numeric | Analytic | Analytic |
EM Determinism
em.detail.deterStochHelp
?
|
deterministic | deterministic | deterministic |
Statistical Estimation of EM
em.detail.statisticalEstimationHelp
?
|
|
|
|
EM ID
em.detail.idHelp
?
|
EM-376 | EM-938 | EM-993 |
Model Calibration Reported?
em.detail.calibrationHelp
?
|
No | Not applicable | Yes |
Model Goodness of Fit Reported?
em.detail.goodnessFitHelp
?
|
No | Not applicable | No |
Goodness of Fit (metric| value | unit)
em.detail.goodnessFitValuesHelp
?
|
None | None | None |
Model Operational Validation Reported?
em.detail.validationHelp
?
|
No | Not applicable | Yes |
Model Uncertainty Analysis Reported?
em.detail.uncertaintyAnalysisHelp
?
|
No | Not applicable | Unclear |
Model Sensitivity Analysis Reported?
em.detail.sensAnalysisHelp
?
|
No | Not applicable | Unclear |
Model Sensitivity Analysis Include Interactions?
em.detail.interactionConsiderHelp
?
|
Not applicable | Not applicable | Not applicable |
EM Locations, Environments, Ecology
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
EM-376 | EM-938 | EM-993 |
None | None |
|
Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
EM-376 | EM-938 | EM-993 |
|
None | None |
Centroid Lat/Long (Decimal Degree)
EM ID
em.detail.idHelp
?
|
EM-376 | EM-938 | EM-993 |
Centroid Latitude
em.detail.ddLatHelp
?
|
41.72 | Not applicable | 47.55 |
Centroid Longitude
em.detail.ddLongHelp
?
|
-69.87 | Not applicable | 122.37 |
Centroid Datum
em.detail.datumHelp
?
|
WGS84 | Not applicable | None provided |
Centroid Coordinates Status
em.detail.coordinateStatusHelp
?
|
Estimated | Not applicable | Provided |
EM ID
em.detail.idHelp
?
|
EM-376 | EM-938 | EM-993 |
EM Environmental Sub-Class
em.detail.emEnvironmentalSubclassHelp
?
|
Near Coastal Marine and Estuarine | Aquatic Environment (sub-classes not fully specified) | Near Coastal Marine and Estuarine | Terrestrial Environment (sub-classes not fully specified) | Rivers and Streams |
Specific Environment Type
em.detail.specificEnvTypeHelp
?
|
None identified | Coastal and non-coastal | small stream |
EM Ecological Scale
em.detail.ecoScaleHelp
?
|
Ecological scale is finer than that of the Environmental Sub-class | Ecological scale is finer than that of the Environmental Sub-class | Ecological scale is finer than that of the Environmental Sub-class |
Scale of differentiation of organisms modeled
EM ID
em.detail.idHelp
?
|
EM-376 | EM-938 | EM-993 |
EM Organismal Scale
em.detail.orgScaleHelp
?
|
Species | Not applicable | Species |
Taxonomic level and name of organisms or groups identified
EM-376 | EM-938 | EM-993 |
|
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-376 | EM-938 | EM-993 |
|
|
|
<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-376 | EM-938 | EM-993 |
|
None |
Comment:Model identifies toxicant concentrations relative to the known LC50 for coho juveniles which is 95ng/L (Spromber and Scholz, 2011; |