EcoService Models Library (ESML)
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Variables Details
: (EM-857)
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EM Identity and Description
EM-857 | |
Document Author
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Warren Pinnacle Consulting, Inc. |
Document Year
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2016 |
Variable General Info
Dike location ?Comment:If it is desirable to model the protective effects of dikes, an additional raster layer must be specified that indicates whether each cell is protected by dikes or not. This can be derived from NWI special modifier “h=Diked/Impounded.” As noted above, in the section on Levee and Dike inputs, this raster can also be set up to specify dike locations and elevations, or a combination of the two dike-modeling options may be used. It is possible to input the elevation of the dikes layer to more realistically model water flows as function of sea level. In the traditional model, if a cell is defined as protected by a dike or levee it is not permitted to change. The existence of these dikes can severely affect the ability of wetlands to migrate onto adjacent shorelines. Diked wetlands are assumed to be subject to inundation when relative sea-level change is greater than 2 m, although that assumption can be changed. In SLAMM 6.7 it is also possible to enter the elevation of the levees or dikes on a cell by cell basis or to use a connectivity algorithm along with cell elevations to determine when a dike is overtopped. |
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Variable ID
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20335 |
Not reported | |
Qualitative-Quantitative
variable.detail.continuousCategoricalHelp
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Qualitative (Class, Rating or Ranking) |
Cardinal-Ordinal
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Non-Ordinal |
Not applicable |
Variable Typology
Dike location ?Comment:If it is desirable to model the protective effects of dikes, an additional raster layer must be specified that indicates whether each cell is protected by dikes or not. This can be derived from NWI special modifier “h=Diked/Impounded.” As noted above, in the section on Levee and Dike inputs, this raster can also be set up to specify dike locations and elevations, or a combination of the two dike-modeling options may be used. It is possible to input the elevation of the dikes layer to more realistically model water flows as function of sea level. In the traditional model, if a cell is defined as protected by a dike or levee it is not permitted to change. The existence of these dikes can severely affect the ability of wetlands to migrate onto adjacent shorelines. Diked wetlands are assumed to be subject to inundation when relative sea-level change is greater than 2 m, although that assumption can be changed. In SLAMM 6.7 it is also possible to enter the elevation of the levees or dikes on a cell by cell basis or to use a connectivity algorithm along with cell elevations to determine when a dike is overtopped. |
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Predictor-Intermediate-Response
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Predictor |
Predictor Variable Type
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Time- or Space-varying Variable |
Response Variable Type
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Not applicable |
Data Source/Type
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Not applicable |
Variable Classification Hierarchy
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4. Human-Produced Stressor or Enhancer of Ecosystem Goods and Services Production |
--Nonnatural structures associated with ecosystem access, enhancement, restoration or water storage |
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----Nonnatural structures associated with water storage |
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Variable Spatial Characteristics
Dike location ?Comment:If it is desirable to model the protective effects of dikes, an additional raster layer must be specified that indicates whether each cell is protected by dikes or not. This can be derived from NWI special modifier “h=Diked/Impounded.” As noted above, in the section on Levee and Dike inputs, this raster can also be set up to specify dike locations and elevations, or a combination of the two dike-modeling options may be used. It is possible to input the elevation of the dikes layer to more realistically model water flows as function of sea level. In the traditional model, if a cell is defined as protected by a dike or levee it is not permitted to change. The existence of these dikes can severely affect the ability of wetlands to migrate onto adjacent shorelines. Diked wetlands are assumed to be subject to inundation when relative sea-level change is greater than 2 m, although that assumption can be changed. In SLAMM 6.7 it is also possible to enter the elevation of the levees or dikes on a cell by cell basis or to use a connectivity algorithm along with cell elevations to determine when a dike is overtopped. |
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Spatial Extent Area
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Not applicable |
Spatially Distributed?
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Yes |
Observations Spatially Patterned?
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Yes |
Spatial Grain Type
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area, for pixel or radial feature |
Spatial Grain Size
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user defined |
Spatial Density
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Not applicable |
EnviroAtlas URL
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Water supply from NID reservoirs (million gallons) |
Variable Temporal Characteristics
Dike location ?Comment:If it is desirable to model the protective effects of dikes, an additional raster layer must be specified that indicates whether each cell is protected by dikes or not. This can be derived from NWI special modifier “h=Diked/Impounded.” As noted above, in the section on Levee and Dike inputs, this raster can also be set up to specify dike locations and elevations, or a combination of the two dike-modeling options may be used. It is possible to input the elevation of the dikes layer to more realistically model water flows as function of sea level. In the traditional model, if a cell is defined as protected by a dike or levee it is not permitted to change. The existence of these dikes can severely affect the ability of wetlands to migrate onto adjacent shorelines. Diked wetlands are assumed to be subject to inundation when relative sea-level change is greater than 2 m, although that assumption can be changed. In SLAMM 6.7 it is also possible to enter the elevation of the levees or dikes on a cell by cell basis or to use a connectivity algorithm along with cell elevations to determine when a dike is overtopped. |
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Temporal Extent
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Not applicable |
Temporally Distributed?
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No |
Regular Temporal Grain?
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Not applicable |
Temporal Grain Size Value
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Not applicable |
Temporal Grain Size Units
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Not applicable |
Temporal Density
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Not applicable |
Variable Values
Dike location ?Comment:If it is desirable to model the protective effects of dikes, an additional raster layer must be specified that indicates whether each cell is protected by dikes or not. This can be derived from NWI special modifier “h=Diked/Impounded.” As noted above, in the section on Levee and Dike inputs, this raster can also be set up to specify dike locations and elevations, or a combination of the two dike-modeling options may be used. It is possible to input the elevation of the dikes layer to more realistically model water flows as function of sea level. In the traditional model, if a cell is defined as protected by a dike or levee it is not permitted to change. The existence of these dikes can severely affect the ability of wetlands to migrate onto adjacent shorelines. Diked wetlands are assumed to be subject to inundation when relative sea-level change is greater than 2 m, although that assumption can be changed. In SLAMM 6.7 it is also possible to enter the elevation of the levees or dikes on a cell by cell basis or to use a connectivity algorithm along with cell elevations to determine when a dike is overtopped. |
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Not applicable | |
Min Value
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Not applicable |
Max Value
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Not applicable |
Other Value Type
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Not applicable |
Other Value
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Not applicable |
Variable Variability and Sensitivity
Dike location ?Comment:If it is desirable to model the protective effects of dikes, an additional raster layer must be specified that indicates whether each cell is protected by dikes or not. This can be derived from NWI special modifier “h=Diked/Impounded.” As noted above, in the section on Levee and Dike inputs, this raster can also be set up to specify dike locations and elevations, or a combination of the two dike-modeling options may be used. It is possible to input the elevation of the dikes layer to more realistically model water flows as function of sea level. In the traditional model, if a cell is defined as protected by a dike or levee it is not permitted to change. The existence of these dikes can severely affect the ability of wetlands to migrate onto adjacent shorelines. Diked wetlands are assumed to be subject to inundation when relative sea-level change is greater than 2 m, although that assumption can be changed. In SLAMM 6.7 it is also possible to enter the elevation of the levees or dikes on a cell by cell basis or to use a connectivity algorithm along with cell elevations to determine when a dike is overtopped. |
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Variability Expression Given?
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Not applicable |
Variability Metric
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None |
Variability Value
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None |
Variability Units
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None |
Resampling Used?
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Not applicable |
Variability Expression Used in Modeling?
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Not applicable |
Variable Operational Validation (Response Variables only)
Variable ID
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Validated?
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Validation Approach (within, between, etc.)
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Validation Quality (Qual/Quant)
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Validation Method (Stat/Deviance)
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Validation Metric
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Validation Value
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Validation Units
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Use of Measured Response Data
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