watershed management and modeling hydrologic modeling...
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Watershed Management And Modeling
Hydrologic Modeling Overview
Chuck Downer, PhD, PE
Hydrologic Systems BranchCoastal and Hydraulics Laboratory
h d lEngineer Research and Development CenterVicksburg, Mississippi
Watershed Management And Modeling
Discussion Topics
Hydrologic processes Hydrologic modeling Hydrologic modeling Hydrologic modeling approaches
Empirical, lumped parameter modelsp p p Distributed, physics based models Hybrid models
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Hydrologic Cycle
Watershed Management And Modeling
Sources of Stream Flow
Hortonian, infiltration excess, runoff Saturated source areas Saturated source areas Exfiltration Groundwater discharge to streamGroundwater discharge to stream
Watershed Management And Modeling
Infiltration Excess Runoff
Infiltration excess runoff occurs when the rainfall intensity exceeds the infiltration capacity of the soil.
Process described by Horton (1933), often referred to as Hortonian runoff.
Dominant runoff mechanism in arid to semi‐arid regionsDominant runoff mechanism in arid to semi arid regions. Conditions conducive to infiltration excess runoff:
Fine texture soilsHi h i t it i it ti High intensity precipitation
Deep water table
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Saturated Source Areas
When the storage capacity of the soils in the unsaturated zone is filled infiltration no longer occurs, and runoff is equal to the precipitation intensityequal to the precipitation intensity.
Described by Dunne and Black (1970), sometimes referred to as Dunne runoff.
Dominant runoff production mechanism in humid regions.
Conditions conducive to saturation excess runoffConditions conducive to saturation excess runoff Permeable soils Low intensity precipitation High water tableHigh water table High water tableHigh water table
Watershed Management And Modeling
Exfiltration
When the elevation of the surface of the saturated groundwater exceeds the elevation of the land surface groundwater may discharge directly onto the land surface.
Often called a seep or spring. N t t i ll d i t ff h i Not typically a dominant runoff mechanism. Conditions conducive to seeps and springs
High water tableg Breaks in slopes
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Groundwater Discharge to Stream
When the elevation of the saturated groundwater surface exceeds the free water surface elevation in the stream, ,groundwater may discharge directly to the stream.
Often referred to as base flow. Can be a significant portion of water balance in humid areas Can be a significant portion of water balance in humid areas,
especially in larger basins. Conditions conducive to groundwater discharge to the
stream High water table Permeable subsurface materials Extended periods of rainfallExtended periods of rainfall
Watershed Management And Modeling
Mixed Basins
Many basins are mixed basins Runoff is generated from a variety of methodsg y Spikes in runoff are due to Hortonian flow Spikes in runoff may also occur due to saturation excess flow Long tails on hydrographs and base flow due to groundwater
interaction with stream Streams gain and lose depending on location in stream and Streams gain and lose depending on location in stream and
water table Different locations in the watershed may have different y
runoff mechanisms
Watershed Management And Modeling
Special Considerations
Seasonality Soil layering Soil layering
Watershed Management And Modeling
Seasonal Considerations
Snowfall accumulation affects, and can dominate, the timing of runoff and stream flow.g
Frozen soils can greatly inhibit infiltration and produce enhanced runoff.
In temperate zones seasonal plant changes change result in In temperate zones, seasonal plant changes change result in large changes in canopy resistance during the year Inverse of leave area index
C t lli f t i t i ti Controlling factor in evapo‐transpiration
Seasonal plant changes also affect vegetative interception of rainfall
Watershed Management And Modeling
Soil Layering
Soil layer can greatly affect infiltration Infiltration capacity, hydraulic conductivity, tends to be p y, y y,
substantially lower in deeper layers Fragipans – very impermeable layers below the tilled soils,
are common in agricultural areasare common in agricultural areas Impermeable layers in the soil can cause perched water
tables when ET is lowC l i li f h d i ff Can result in a seasonality of the dominate runoff mechanisms Hortonian for summer season Saturation excess for winter/spring season
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Numerical Models
Represent complex natural systems with mathematical and empirical relationships.p p
System complexity is reduced, or processes are solved separately and then reassembledseparately and then reassembled.
Provide a mechanism for analyzing project alternatives and y g p jpredicting the effects of future changes, such as: urban development, land use change, or climate change.
Watershed Management And Modeling
Computation Element
Defined region in a model where calculations are performedperformed sub‐watershed grid cell
l l control volume finite element node
Physical conditions, and parameter values, are y , p ,homogeneous throughout the computation element
Any heterogeneity within a computational element is lost, t b i li itl i l d d i th t lor must be implicitly included in the parameter values
Watershed Management And Modeling
Hydrologic Modeling Approaches
Empirically based, lumped parameter modelsEmpirically based, lumped parameter modelsPh i llPh i ll b d di ib d d lb d di ib d d l PhysicallyPhysically‐‐based, distributed parameter modelsbased, distributed parameter modelsHybrids Hybrids –– semisemi‐‐distributed, quasidistributed, quasi‐‐physically basedphysically based
Watershed Management And Modeling
Dual Modeling Theories
Empirically‐based, lumped parameter models – integrated over large enough time and space scales the highly non‐linear over large enough time and space scales, the highly non linear response of watersheds appears linear.
Physically‐based, distributed parameter models – broken down into small enough time and space increments, the physical processes occurring in the watershed may be explicitly simulated, and then integrated to produce the p y , g pwatershed response.
Watershed Management And Modeling
Lumped Parameter Models
The system response, which behaves linearly at sufficient scale is simulated not the underlying physical responses scale, is simulated, not the underlying physical responses, which are highly non‐linear.
Watershed Management And Modeling
Empirically Based, Lumped Models
Computational element is the sub‐watershed. Subdivide watersheds into smaller sub‐watershedsSubdivide watersheds into smaller sub watersheds. A single parameter value represents processes the entire
sub‐watershed.E i i l l i hi l h d l i Empirical relationships relate response to hydrologic inputs. Curve number – fraction of rainfall converted to runoff Similar approaches for other processes erosion
tit t t k /d constituent uptake/decay Sub‐basins are connected with simplified flow
relationships relationships ‐‐ link/nodelink/node
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Lump Model Watershed Representation
Watershed Management And Modeling
Example Models
Rational Method TR 20 TR‐20 HEC‐1 Sacramento ModelSacramento Model HSPF
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Advantages
Conceptually simple Easy to program Easy to program Easy to apply Simulation time is trivialSimulation time is trivial
enhanced calibration – automated methods
Can be applied to enormous basins Generally accepted by regulators Long history of use
Watershed Management And Modeling
Disadvantages
Requires substantial calibration data Not useful outside the range of calibration Not useful outside the range of calibration Do not provide process information Lack of spatial heterogeneity in the modelsLack of spatial heterogeneity in the models Lack of verifiable results
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Lumping of Information Selection of sub‐watersheds (the computational element) is based
primarily on need for output subdivide the watershed where you need informationy
Even at the finest discretization, sub‐watershed are highly variable land use slopeslope soils depth to the water table spatial distribution of featuresspatial distribution of features
Proper element response means the parameters must contain this information – i.e. this information is “lumped” into the sub‐watershed parameterpa a ete
Watershed Management And Modeling
Calibration
Because response, not process, is simulated the parameters must be tuned to the current system.p y
For the model to function over a large range of conditions, the model must be calibrated to these conditions.
Application of the model outside this range is dangerous as changes in process may occur with no way of knowing or nor accounting for the change.g g
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Parameter Values
Parameter values for sub‐watersheds implicitly contain the process information particular to that sub‐watershedprocess information particular to that sub watershed.
Determining parameter values for changing conditions is difficult land use project alternatives
Watershed Management And Modeling
Example
Analysis of riparian restoration of urbanized watershed in Washington D.C., Baltimore District
Restore natural areas within the watershed to reduce runoff and erosion
D l d HEC d l f th i b i Developed HEC‐1 model of the river basin Developed Curve Numbers from highly detailed land use
and soil mapsp Calibrated Curve Numbers to current conditions Adjusted the Curve Numbers for changes in land use for
restoration scenarios Restoration scenarios resulted in increased runoff!
Watershed Management And Modeling Proper Use of Empirical, Lumped Parameter ModelsParameter Models
Empirical lumped parameter models are best used for Empirical lumped parameter models are best used for analysis of current systems.
Can be applied to analyze very large basins Can be used to provide predictions within the range of
calibration Can identify areas of concern Can identify areas of concern
hotspots source areas
Watershed Management And Modeling
Example
National Weather Service uses the Sacramento Model for flood predictionsp
The Sacramental model is a simple volumetric model with compartments representing different hydrologic regions surface water surface water unsaturated zone groundwaterg
Model is automatically recalibrated every evening extend the range of calibration
t f h t th t account for changes to the system. Results would be very difficult to reproduce with other
models and methods .
Watershed Management And Modeling
Physically‐based, Distributed Models
Fine scale physical processes are simulated at the elemental level. Plant interception InfiltrationInfiltration Runoff Evapo‐transpiration
Th l l i d d i h The elemental responses are integrated to determine the system response.
Watershed Management And Modeling Distributed,Two‐dimensional Representation of WatershedRepresentation of Watershed
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Advantages
Simulates physical processes Explicitly includes spatial heterogeneity Explicitly includes spatial heterogeneity Provides information at the sub‐watershed level Requires less calibration dataRequires less calibration data Extendible beyond calibration range Can be used to analyze changing conditions
land use changes project alternatives climate changeclimate change
Watershed Management And Modeling
Disadvantages
Numerical modeling concepts can be difficult to grasp Code develop is difficult Application is difficult compared to lumped parameter
modelsmodels Data intensive Computational penalty
Simulation times can be long Simulation times increase with increasing complexity and
resolutionH lib i Hampers calibration
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Applicability
Watersheds with minimal calibration data Analyze land use or climate change project alternatives or Analyze land use or climate change, project alternatives, or
any conditions outside the range of calibrated values. Inherently distributed processes ‐ sediment erosion and y p
deposition, non‐point source pollution, surface water/groundwater interaction
Watershed Management And Modeling
Examples
GSSHA MIKE SHE MIKE‐SHE MODHMS WASH123DWASH123D ADH
Watershed Management And Modeling
Discretization
Watershed is discretized based on resolution required to simulate dominate features and processes.p
Parameters are prescribed to each computational element based on the physical properties of the element land use land use soils
Watershed Management And Modeling
GSSHA Representation of Land Use
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Example – Goodwin Creek Erosion
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Calibration
Initial values are assigned based on literature and field Initial values are assigned based on literature and field values
Parameters must be calibrated values are uncertain model formulation introduces errors discretization introduces errorsdiscretization introduces errors
Watershed Management And Modeling
Parameter Values
Calibrated values are based on physical conditions in the computational elementcomputational element
The tie to physical conditions provides a means to logically alter parameters based on changing conditions.
Watershed Management And Modeling Model Which Processes?And How?And How?
Extend capability include more processesinclude more processes general treatment
Added complexity increases the number of parameters increases difficulty in using model increases difficulty in using model increases computation time
Watershed Management And Modeling
Hybrid Models
Contain elements of lumped parameter and fully distributed, physics based modelsphysics based models
Approach varies amongst models Typically include greater spatial heterogeneity than simple yp y g p g y p
lumped parameter models May include more physically meaningful representation of
processesprocesses Mixture of empirical and physics based approaches within the
model
Watershed Management And Modeling
Examples
HEC‐HMS TOPMODEL TOPMODEL SWAT
Watershed Management And Modeling
Advantages/Disadvantages
Semi‐distributed models share many of the same advantages/disadvantages as simple lumped parameter g g p p pmodels
The advantage over simple lumped parameter models are increased spatial resolution increased spatial resolution better process descriptions
Semi‐distributed models maintain the computational advantage over fully distributed physics based modelsadvantage over fully distributed, physics based models
Watershed Management And Modeling
Example with HMS
Problem Simulate existing system Evaluate alternatives for reducing flood damageEvaluate alternatives for reducing flood damage
Modeling Approach Subdivide domain based on data availability. Estimate parameters for infiltration model, i.e. Green Ampt. Runoff
Use quasi‐distributed approach if there is a good source of gridded precipitation. Use Unit hydrograph if there is regional calibration data available.
Apply physical channel routing methods pp y p y g kinematic Muskingum‐Cunge
Analysis Apply frequency events to get appropriate runoff Apply frequency events to get appropriate runoff. Compute frequency curve for each alternative and compare.
Watershed Management And Modeling
Modeling Philosophy
Model representation of the physical system should be as simple as possiblesystem should be as simple as possible, but no simpler
Model should account for dominant physical processes Model must include important physical features (both
t l d ti l)temporal and spatial) Model should not contain undue complexity Different approaches for different problems Different approaches for different problems
Watershed Management And Modeling Conclusions
The hydrologic cycle is complex Hydrologic modeling aids in understanding and analyzing hydrologic
tsystems Hydrologic modeling falls into two large classes
empirical, lumped parameter models distributed physics based models distributed, physics based models
Hybrid models contain elements of both Different types are useful for different purposes Lumped models are best for analysis Lumped models are best for analysis Physics based models are best suited for design Hybrid models
fi l i refine analysis screen design
Physics based models range greatly in complexity The appropriate model depends on the application The appropriate model depends on the application