EcoService Models Library (ESML)
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Variables Details
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EM-857 | |
Document Author
variable.detail.emDocumentAuthorHelp
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Warren Pinnacle Consulting, Inc. |
Document Year
variable.detail.emDocumentYearHelp
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2016 |
Change in wetland type ?Comment:Map distributions of wetlands are predicted under conditions of accelerated sea level rise, and results are summarized in tabular and graphical form. For each time step the fractional conversion from one class to another is computed on the basis of the relative change in elevation divided by the elevation range of the class in that cell. In addition to mapped output: Available Statistics include: • n cells: The number of cells covered by that land category. Statistics based on small sample sizes should probably be discounted to some degree. • 5th percentile and 95th percentile: The 90% confidence interval for this particular land category in half-tide units. These can be compared with the “Min HTU” and “Max HTU” conceptual model columns. • Mean, St. Dev.: The average elevation value and standard deviation in half tide units. • Min, Max: The minimum and maximum elevation for this cell in half-tide units. These data are usually less useful as horizontal error in a single cell’s classification can produce strange results. • % < Min: The current percentage of cells below the minimum elevation specified. |
Greenhouse gas mass sequestered (CO2) ?Comment:Product of the Carbon Sequestration module. SLAMM estimates Carbon Sequestration as a function of land cover based on the approach developed by Vandebroek and Crooks at ESA PWA (2014). This method accounts for both the amount of Carbon sequestered by wetlands as well as the Carbon emissions through the loss of methane from freshwater habitats. Carbon sequestration calculations will be performed for all time-steps and output steps for all simulations performed and all modeled subsites. |
Infrastructure inundation frequency ?Comment:At the end of a SLAMM the frequency that each infrastructure point will be inundated for <30, 30-60, 60-90 days under normal tides and storm-surge conditions are summarized in the output excel file. |
Probability of having submerged aquatic vegetation ?Comment:Product of the optional Submerged Aquatic Vegetation module. SLAMM uses a regression relationship developed by Melanie Frazier and Patrick Clinton of U.S. EPA to describe the probability of submerged aquatic vegetation being present in a given cell. The default parameters as delivered with SLAMM 6.7 were derived using data from the Yaquina estuary in Oregon and the relationship was then validated at the Tilamook and Alsea estuaries in Oregon. When this model is implemented, probability-of-SAV maps may be produced by the model in each time step. |
Road miles inundated ?Comment:At the end of a SLAMM simulations numerical data of the total length of roads that are inundated <30, 30-60, 60-90 days are summarized in the output excel file. |
Road segment inundation (30, 60, and 90 day frequency) ?Comment:At the end of a SLAMM the frequency that each infrastructure point will be inundated for <30, 30-60, 60-90 days under normal tides and storm-surge conditions are summarized in the output excel file. |
Total area of submerged aquatic vegetation ?Comment:Product of the optional Submerged Aquatic Vegetation module. The expected value of total SAV habitat in square kilometers is output along with other SLAMM tables of output. The default parameters as delivered with SLAMM 6.7 were derived using data from the Yaquina estuary in Oregon and the relationship was then validated at the Tilamook and Alsea estuaries in Oregon. |
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Variable ID
variable.detail.varIdHelp
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20443 | 20440 | 20434 | 20441 | 20433 | 21925 | 20442 |
Not reported |
M sub |
Not reported | PROBSAV | Not reported | Not reported | Not reported | |
Qualitative-Quantitative
variable.detail.continuousCategoricalHelp
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Qualitative (Class, Rating or Ranking) | Quantitative (Cardinal Only) | Quantitative (Cardinal Only) | Quantitative (Cardinal Only) | Quantitative (Cardinal Only) | Quantitative (Cardinal Only) | Quantitative (Cardinal Only) |
Cardinal-Ordinal
variable.detail.cardinalOrdinalHelp
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Non-Ordinal | Cardinal | Cardinal | Cardinal | Cardinal | Cardinal | Cardinal |
Not applicable | metric tons ha^-1 yr^-1 | days | % | mi | days | km^2 |
Change in wetland type ?Comment:Map distributions of wetlands are predicted under conditions of accelerated sea level rise, and results are summarized in tabular and graphical form. For each time step the fractional conversion from one class to another is computed on the basis of the relative change in elevation divided by the elevation range of the class in that cell. In addition to mapped output: Available Statistics include: • n cells: The number of cells covered by that land category. Statistics based on small sample sizes should probably be discounted to some degree. • 5th percentile and 95th percentile: The 90% confidence interval for this particular land category in half-tide units. These can be compared with the “Min HTU” and “Max HTU” conceptual model columns. • Mean, St. Dev.: The average elevation value and standard deviation in half tide units. • Min, Max: The minimum and maximum elevation for this cell in half-tide units. These data are usually less useful as horizontal error in a single cell’s classification can produce strange results. • % < Min: The current percentage of cells below the minimum elevation specified. |
Greenhouse gas mass sequestered (CO2) ?Comment:Product of the Carbon Sequestration module. SLAMM estimates Carbon Sequestration as a function of land cover based on the approach developed by Vandebroek and Crooks at ESA PWA (2014). This method accounts for both the amount of Carbon sequestered by wetlands as well as the Carbon emissions through the loss of methane from freshwater habitats. Carbon sequestration calculations will be performed for all time-steps and output steps for all simulations performed and all modeled subsites. |
Infrastructure inundation frequency ?Comment:At the end of a SLAMM the frequency that each infrastructure point will be inundated for <30, 30-60, 60-90 days under normal tides and storm-surge conditions are summarized in the output excel file. |
Probability of having submerged aquatic vegetation ?Comment:Product of the optional Submerged Aquatic Vegetation module. SLAMM uses a regression relationship developed by Melanie Frazier and Patrick Clinton of U.S. EPA to describe the probability of submerged aquatic vegetation being present in a given cell. The default parameters as delivered with SLAMM 6.7 were derived using data from the Yaquina estuary in Oregon and the relationship was then validated at the Tilamook and Alsea estuaries in Oregon. When this model is implemented, probability-of-SAV maps may be produced by the model in each time step. |
Road miles inundated ?Comment:At the end of a SLAMM simulations numerical data of the total length of roads that are inundated <30, 30-60, 60-90 days are summarized in the output excel file. |
Road segment inundation (30, 60, and 90 day frequency) ?Comment:At the end of a SLAMM the frequency that each infrastructure point will be inundated for <30, 30-60, 60-90 days under normal tides and storm-surge conditions are summarized in the output excel file. |
Total area of submerged aquatic vegetation ?Comment:Product of the optional Submerged Aquatic Vegetation module. The expected value of total SAV habitat in square kilometers is output along with other SLAMM tables of output. The default parameters as delivered with SLAMM 6.7 were derived using data from the Yaquina estuary in Oregon and the relationship was then validated at the Tilamook and Alsea estuaries in Oregon. |
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Predictor-Intermediate-Response
variable.detail.displayVariableTypeHelp
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Response |
Response |
Response |
Response |
Response |
Response |
Response |
Predictor Variable Type
variable.detail.displayPredictorVariableTypeHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Response Variable Type
variable.detail.resClassHelp
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Computed Variable |
Computed Variable |
Computed Variable |
Computed Variable |
Computed Variable |
Computed Variable |
Computed Variable |
Data Source/Type
variable.detail.dataTypeHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Variable Classification Hierarchy
variable.detail.vchLevel1Help
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5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
6. Non-monetary Indicators of Human Demand, Use or Benefit of Ecosystem Goods and Services |
5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
6. Non-monetary Indicators of Human Demand, Use or Benefit of Ecosystem Goods and Services |
6. Non-monetary Indicators of Human Demand, Use or Benefit of Ecosystem Goods and Services |
5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
--Biological characteristics, processes or requirements of living ecosystem components |
--CICES categories: Ecosystem goods and services - or landscape-level indices of suitability to supply EGS |
--Demand for or use of regulation & maintenance services-Mediation of flows |
--Biological characteristics, processes or requirements of living ecosystem components |
--Demand for or use of regulation & maintenance services-Mediation of flows |
--Demand for or use of regulation & maintenance services-Mediation of flows |
--Biological characteristics, processes or requirements of living ecosystem components |
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----Biological characteristics, processes or requirements of ecological communities |
----Suitability to supply regulation & maintenance services-Mediation of wastes |
----Flood and storm protection |
----Biological characteristics, processes or requirements of ecological communities |
----Flood and storm protection |
----Flood and storm protection |
----Biological characteristics, processes or requirements of ecological communities |
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------Near coastal marine, estuarine, and coral communities |
------Filtration/sequestration/storage/accumulation by ecosystems |
------Near coastal marine, estuarine, and coral communities |
------Near coastal marine, estuarine, and coral communities |
Change in wetland type ?Comment:Map distributions of wetlands are predicted under conditions of accelerated sea level rise, and results are summarized in tabular and graphical form. For each time step the fractional conversion from one class to another is computed on the basis of the relative change in elevation divided by the elevation range of the class in that cell. In addition to mapped output: Available Statistics include: • n cells: The number of cells covered by that land category. Statistics based on small sample sizes should probably be discounted to some degree. • 5th percentile and 95th percentile: The 90% confidence interval for this particular land category in half-tide units. These can be compared with the “Min HTU” and “Max HTU” conceptual model columns. • Mean, St. Dev.: The average elevation value and standard deviation in half tide units. • Min, Max: The minimum and maximum elevation for this cell in half-tide units. These data are usually less useful as horizontal error in a single cell’s classification can produce strange results. • % < Min: The current percentage of cells below the minimum elevation specified. |
Greenhouse gas mass sequestered (CO2) ?Comment:Product of the Carbon Sequestration module. SLAMM estimates Carbon Sequestration as a function of land cover based on the approach developed by Vandebroek and Crooks at ESA PWA (2014). This method accounts for both the amount of Carbon sequestered by wetlands as well as the Carbon emissions through the loss of methane from freshwater habitats. Carbon sequestration calculations will be performed for all time-steps and output steps for all simulations performed and all modeled subsites. |
Infrastructure inundation frequency ?Comment:At the end of a SLAMM the frequency that each infrastructure point will be inundated for <30, 30-60, 60-90 days under normal tides and storm-surge conditions are summarized in the output excel file. |
Probability of having submerged aquatic vegetation ?Comment:Product of the optional Submerged Aquatic Vegetation module. SLAMM uses a regression relationship developed by Melanie Frazier and Patrick Clinton of U.S. EPA to describe the probability of submerged aquatic vegetation being present in a given cell. The default parameters as delivered with SLAMM 6.7 were derived using data from the Yaquina estuary in Oregon and the relationship was then validated at the Tilamook and Alsea estuaries in Oregon. When this model is implemented, probability-of-SAV maps may be produced by the model in each time step. |
Road miles inundated ?Comment:At the end of a SLAMM simulations numerical data of the total length of roads that are inundated <30, 30-60, 60-90 days are summarized in the output excel file. |
Road segment inundation (30, 60, and 90 day frequency) ?Comment:At the end of a SLAMM the frequency that each infrastructure point will be inundated for <30, 30-60, 60-90 days under normal tides and storm-surge conditions are summarized in the output excel file. |
Total area of submerged aquatic vegetation ?Comment:Product of the optional Submerged Aquatic Vegetation module. The expected value of total SAV habitat in square kilometers is output along with other SLAMM tables of output. The default parameters as delivered with SLAMM 6.7 were derived using data from the Yaquina estuary in Oregon and the relationship was then validated at the Tilamook and Alsea estuaries in Oregon. |
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Spatial Extent Area
variable.detail.spExtentHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Spatially Distributed?
variable.detail.spDistributedHelp
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Yes | Yes | Yes | Yes | Yes | Yes | No |
Observations Spatially Patterned?
variable.detail.regularSpGrainHelp
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Yes | Yes | Yes | Yes | Yes | Yes | Not applicable |
Spatial Grain Type
variable.detail.spGrainTypeHelp
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area, for pixel or radial feature | area, for pixel or radial feature | area, for pixel or radial feature | area, for pixel or radial feature | area, for pixel or radial feature | area, for pixel or radial feature | Not applicable |
Spatial Grain Size
variable.detail.spGrainSizeHelp
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user defined | user defined | user defined | user defined | user defined | user defined | Not applicable |
Spatial Density
variable.detail.spDensityHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
EnviroAtlas URL
variable.detail.enviroAtlasURLHelp
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Change in wetland type ?Comment:Map distributions of wetlands are predicted under conditions of accelerated sea level rise, and results are summarized in tabular and graphical form. For each time step the fractional conversion from one class to another is computed on the basis of the relative change in elevation divided by the elevation range of the class in that cell. In addition to mapped output: Available Statistics include: • n cells: The number of cells covered by that land category. Statistics based on small sample sizes should probably be discounted to some degree. • 5th percentile and 95th percentile: The 90% confidence interval for this particular land category in half-tide units. These can be compared with the “Min HTU” and “Max HTU” conceptual model columns. • Mean, St. Dev.: The average elevation value and standard deviation in half tide units. • Min, Max: The minimum and maximum elevation for this cell in half-tide units. These data are usually less useful as horizontal error in a single cell’s classification can produce strange results. • % < Min: The current percentage of cells below the minimum elevation specified. |
Greenhouse gas mass sequestered (CO2) ?Comment:Product of the Carbon Sequestration module. SLAMM estimates Carbon Sequestration as a function of land cover based on the approach developed by Vandebroek and Crooks at ESA PWA (2014). This method accounts for both the amount of Carbon sequestered by wetlands as well as the Carbon emissions through the loss of methane from freshwater habitats. Carbon sequestration calculations will be performed for all time-steps and output steps for all simulations performed and all modeled subsites. |
Infrastructure inundation frequency ?Comment:At the end of a SLAMM the frequency that each infrastructure point will be inundated for <30, 30-60, 60-90 days under normal tides and storm-surge conditions are summarized in the output excel file. |
Probability of having submerged aquatic vegetation ?Comment:Product of the optional Submerged Aquatic Vegetation module. SLAMM uses a regression relationship developed by Melanie Frazier and Patrick Clinton of U.S. EPA to describe the probability of submerged aquatic vegetation being present in a given cell. The default parameters as delivered with SLAMM 6.7 were derived using data from the Yaquina estuary in Oregon and the relationship was then validated at the Tilamook and Alsea estuaries in Oregon. When this model is implemented, probability-of-SAV maps may be produced by the model in each time step. |
Road miles inundated ?Comment:At the end of a SLAMM simulations numerical data of the total length of roads that are inundated <30, 30-60, 60-90 days are summarized in the output excel file. |
Road segment inundation (30, 60, and 90 day frequency) ?Comment:At the end of a SLAMM the frequency that each infrastructure point will be inundated for <30, 30-60, 60-90 days under normal tides and storm-surge conditions are summarized in the output excel file. |
Total area of submerged aquatic vegetation ?Comment:Product of the optional Submerged Aquatic Vegetation module. The expected value of total SAV habitat in square kilometers is output along with other SLAMM tables of output. The default parameters as delivered with SLAMM 6.7 were derived using data from the Yaquina estuary in Oregon and the relationship was then validated at the Tilamook and Alsea estuaries in Oregon. |
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Temporal Extent
variable.detail.tempExtentHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Temporally Distributed?
variable.detail.tempDistributedHelp
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Yes | Yes | Yes | Yes | Yes | Yes | Yes |
Regular Temporal Grain?
variable.detail.regularTempGrainHelp
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Yes | Yes | Yes | Yes | Yes | Yes | Yes |
Temporal Grain Size Value
variable.detail.tempGrainSizeValHelp
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user defined | user defined | user defined | user defined | user defined | user defined | user defined |
Temporal Grain Size Units
variable.detail.tempGrainSizeUnitHelp
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Year | Year | Year | Year | Year | Year | Year |
Temporal Density
variable.detail.tempDensityHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Change in wetland type ?Comment:Map distributions of wetlands are predicted under conditions of accelerated sea level rise, and results are summarized in tabular and graphical form. For each time step the fractional conversion from one class to another is computed on the basis of the relative change in elevation divided by the elevation range of the class in that cell. In addition to mapped output: Available Statistics include: • n cells: The number of cells covered by that land category. Statistics based on small sample sizes should probably be discounted to some degree. • 5th percentile and 95th percentile: The 90% confidence interval for this particular land category in half-tide units. These can be compared with the “Min HTU” and “Max HTU” conceptual model columns. • Mean, St. Dev.: The average elevation value and standard deviation in half tide units. • Min, Max: The minimum and maximum elevation for this cell in half-tide units. These data are usually less useful as horizontal error in a single cell’s classification can produce strange results. • % < Min: The current percentage of cells below the minimum elevation specified. |
Greenhouse gas mass sequestered (CO2) ?Comment:Product of the Carbon Sequestration module. SLAMM estimates Carbon Sequestration as a function of land cover based on the approach developed by Vandebroek and Crooks at ESA PWA (2014). This method accounts for both the amount of Carbon sequestered by wetlands as well as the Carbon emissions through the loss of methane from freshwater habitats. Carbon sequestration calculations will be performed for all time-steps and output steps for all simulations performed and all modeled subsites. |
Infrastructure inundation frequency ?Comment:At the end of a SLAMM the frequency that each infrastructure point will be inundated for <30, 30-60, 60-90 days under normal tides and storm-surge conditions are summarized in the output excel file. |
Probability of having submerged aquatic vegetation ?Comment:Product of the optional Submerged Aquatic Vegetation module. SLAMM uses a regression relationship developed by Melanie Frazier and Patrick Clinton of U.S. EPA to describe the probability of submerged aquatic vegetation being present in a given cell. The default parameters as delivered with SLAMM 6.7 were derived using data from the Yaquina estuary in Oregon and the relationship was then validated at the Tilamook and Alsea estuaries in Oregon. When this model is implemented, probability-of-SAV maps may be produced by the model in each time step. |
Road miles inundated ?Comment:At the end of a SLAMM simulations numerical data of the total length of roads that are inundated <30, 30-60, 60-90 days are summarized in the output excel file. |
Road segment inundation (30, 60, and 90 day frequency) ?Comment:At the end of a SLAMM the frequency that each infrastructure point will be inundated for <30, 30-60, 60-90 days under normal tides and storm-surge conditions are summarized in the output excel file. |
Total area of submerged aquatic vegetation ?Comment:Product of the optional Submerged Aquatic Vegetation module. The expected value of total SAV habitat in square kilometers is output along with other SLAMM tables of output. The default parameters as delivered with SLAMM 6.7 were derived using data from the Yaquina estuary in Oregon and the relationship was then validated at the Tilamook and Alsea estuaries in Oregon. |
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | |
Min Value
variable.detail.minEstHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Max Value
variable.detail.estHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Other Value Type
variable.detail.natureOtherEstHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Other Value
variable.detail.otherEstHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Change in wetland type ?Comment:Map distributions of wetlands are predicted under conditions of accelerated sea level rise, and results are summarized in tabular and graphical form. For each time step the fractional conversion from one class to another is computed on the basis of the relative change in elevation divided by the elevation range of the class in that cell. In addition to mapped output: Available Statistics include: • n cells: The number of cells covered by that land category. Statistics based on small sample sizes should probably be discounted to some degree. • 5th percentile and 95th percentile: The 90% confidence interval for this particular land category in half-tide units. These can be compared with the “Min HTU” and “Max HTU” conceptual model columns. • Mean, St. Dev.: The average elevation value and standard deviation in half tide units. • Min, Max: The minimum and maximum elevation for this cell in half-tide units. These data are usually less useful as horizontal error in a single cell’s classification can produce strange results. • % < Min: The current percentage of cells below the minimum elevation specified. |
Greenhouse gas mass sequestered (CO2) ?Comment:Product of the Carbon Sequestration module. SLAMM estimates Carbon Sequestration as a function of land cover based on the approach developed by Vandebroek and Crooks at ESA PWA (2014). This method accounts for both the amount of Carbon sequestered by wetlands as well as the Carbon emissions through the loss of methane from freshwater habitats. Carbon sequestration calculations will be performed for all time-steps and output steps for all simulations performed and all modeled subsites. |
Infrastructure inundation frequency ?Comment:At the end of a SLAMM the frequency that each infrastructure point will be inundated for <30, 30-60, 60-90 days under normal tides and storm-surge conditions are summarized in the output excel file. |
Probability of having submerged aquatic vegetation ?Comment:Product of the optional Submerged Aquatic Vegetation module. SLAMM uses a regression relationship developed by Melanie Frazier and Patrick Clinton of U.S. EPA to describe the probability of submerged aquatic vegetation being present in a given cell. The default parameters as delivered with SLAMM 6.7 were derived using data from the Yaquina estuary in Oregon and the relationship was then validated at the Tilamook and Alsea estuaries in Oregon. When this model is implemented, probability-of-SAV maps may be produced by the model in each time step. |
Road miles inundated ?Comment:At the end of a SLAMM simulations numerical data of the total length of roads that are inundated <30, 30-60, 60-90 days are summarized in the output excel file. |
Road segment inundation (30, 60, and 90 day frequency) ?Comment:At the end of a SLAMM the frequency that each infrastructure point will be inundated for <30, 30-60, 60-90 days under normal tides and storm-surge conditions are summarized in the output excel file. |
Total area of submerged aquatic vegetation ?Comment:Product of the optional Submerged Aquatic Vegetation module. The expected value of total SAV habitat in square kilometers is output along with other SLAMM tables of output. The default parameters as delivered with SLAMM 6.7 were derived using data from the Yaquina estuary in Oregon and the relationship was then validated at the Tilamook and Alsea estuaries in Oregon. |
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Variability Expression Given?
variable.detail.variabilityExpHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Variability Metric
variable.detail.variabilityMetricHelp
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None | None | None | None | None | None | None |
Variability Value
variable.detail.variabilityValueHelp
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None | None | None | None | None | None | None |
Variability Units
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None | None | None | None | None | None | None |
Resampling Used?
variable.detail.bootstrappingHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Variability Expression Used in Modeling?
variable.detail.variabilityUsedHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Change in wetland type | Greenhouse gas mass sequestered (CO2) | Infrastructure inundation frequency | Probability of having submerged aquatic vegetation | Road miles inundated | Road segment inundation (30, 60, and 90 day frequency) | Total area of submerged aquatic vegetation | |
Variable ID
variable.detail.varIdHelp
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20443 | 20440 | 20434 | 20441 | 20433 | 21925 | 20442 |
Validated?
variable.detail.resValidatedHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Validation Approach (within, between, etc.)
variable.detail.validationApproachHelp
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None | None | None | None | None | None | None |
Validation Quality (Qual/Quant)
variable.detail.validationQualityHelp
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None | None | None | None | None | None | None |
Validation Method (Stat/Deviance)
variable.detail.validationMethodHelp
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None | None | None | None | None | None | None |
Validation Metric
variable.detail.validationMetricHelp
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None | None | None | None | None | None | None |
Validation Value
variable.detail.validationValHelp
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None | None | None | None | None | None | None |
Validation Units
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None | None | None | None | None | None | None |
Use of Measured Response Data
variable.detail.measuredResponseDataHelp
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None | None | None | None | None | None | None |