groundwater modelingcosumnes.waterforum.org/.../04/...04-04-no-videos.pdf · 11/04/2019 ·...
TRANSCRIPT
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GROUNDWATER MODELING
-- April 4, 2019
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OUTLINE
1. Why Model?
2. Groundwater Flow.
3. Input Data.
4. Adaptability and Maintenance.
5. Available Models and Applications.
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1. WHAT MODELS CAN AND CANNOT DO
Can quantify groundwater conditions:
- Water level changes.
- Direction and rate of flow.
- Storage volume changes.
Can project future changes.
Cannot make decisions.
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1. WHY MODEL IS NEEDED FOR THE GROUNDWATER
SUSTAINABILITY PLAN (GSP)?
Quantify “current” conditions and project changes over the next 50 years:
Water level thresholds and objectives.
- Cones of depression.
- Increased pumping lifts
Water inflows, outflows and volume in the basin (called the ‘water budget’).
- Overdraft (storage depletion)
- Additions and losses associated with interconnected surface water
Help select projects that prevent undesirable results.
Determine data needed to monitor plan effectiveness.
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2. GROUNDWATER FLOWBegin with a hydrogeological
conceptual model (HCM)
of how water enters,
leaves, and moves
through the basin.
Many factors affect the
movement of water across a
basin over time (variable
geology, recharge, pumping,
etc.).
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2. AN AQUIFER IS KIND-OF LIKE A SPONGEWater Storage and Transmitting Properties
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Aquifer’s water storage and
transmitting capability is
determined by its geology –
specifically porosity,
permeability, sediment
compressibility and ability
to release water.
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2. PORE SIZE IS RELATED TO SEDIMENT SIZE (TEXTURE)
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Water is stored in the pore
space between sediment grains.
Water
Sediment
Grain Pore Space
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2.EXAMPLES OF SEDIMENT TEXTURE
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GravelSandSiltClay
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2. SEDIMENT DEPOSITION
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Zone #1 - High energy (e.g., gravel).
Zone #2 - Shallowing of topographic relief (e.g., sands and silt).
Zone #3 - Low energy (e.g., silt and clay).
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2. STREAM CHANNEL MIGRATION AND SEDIMENT
DEPOSITION OVER GEOLOGIC HISTORY
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2. STREAM CHANNEL DEPOSITS
12Source: DWR Bulletin No. 118-3, 1974
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2. FLOW (Q) = VELOCITY (V) x AREA (A)
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HYDRAULIC CONDUCTIVITY OF SOILS
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2. DARCY’S LAW CALCULATES FLOW RATE THROUGH SEDIMENT
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𝑙
H1 H2
Q = Discharge (L3/T)A = Cross Sectional Area (L2)K = Hydraulic Conductivity (L/T)H = Water level elevation or “head” (L)𝑙 = Distance Between Wells (L)
𝑄 = 𝐴(𝐾 ×𝐻2− 𝐻1
𝑙)
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3. INPUT DATA –
Building a model in some ways is analogous to
constructing a house
Construct the frame - mesh/grid, layering, boundaries
Plumb and wire – define aquifer properties
Attach exterior – recharge, pumpage, water deliveries, etc.
Paint and landscape – calibration
Move-in – implementation
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3. “Construct the Frame:” Mesh/Grid
Model domain divided spatially into elements/cells representing areas of
constant properties and stresses
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3. “Construct the Frame:” Mesh/Grid
Rectangles approximating a curve:
Narrower
rectangles
More accurate
approximation
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3. “Construct the Frame:” Mesh/GridCells approximating an area:
Smaller cell
area
More accurate
approximation
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3. “Construct the Frame:” Layering
Basin vertically divided in to
layers based on stratigraphy
Includes thin shallow layers to
improve simulation of
SW/GW interaction
Stratigraphy inferred from cross-section F-F’ in DWR (1974) Evaluation of Ground Water
Resources: Sacramento County. Bulletin No. 118-3. Reprinted April 1980.
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3. “Construct the Frame:” Boundary Conditions
Types of Boundaries
“No flow”
“Specified flow”
“Specified head” or “Constant head”
“Head-dependent flow”
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3.“Construct the Frame:” Boundary Conditions“No flow” = No groundwater crosses boundary.
Basin
“A”
Basin
“B”
Groundwater conditions in Basin “A” are independent of Basin “B.”
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3.“Construct the Frame:” Boundary Conditions?No flow
No cross boundary flow
along “aquifer” and
“bedrock” contact.
Bedrock
No FlowNo-flow
Boundary
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3.“Construct the Frame:” Boundary Conditions“Constant Head” = Cross boundary flow calculated to
keep water level constant along boundary
Basin
“A”
Basin
”B”
GW Flow
Groundwater conditions in Basin “A” and Basin “B” influenced by
specified water level.
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3.“Construct the Frame:” Boundary ConditionsConstant Head
Basin
”B”
GW Flow
Flow in or out of lake in
response to changes in
groundwater system
and/or lake levels.
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3.“Construct the Frame:” Boundary Conditions“Specified Flow” = Cross boundary flow specified by user
Basin
“A”
Basin
”B”
GW Flow
Groundwater conditions in Basin “A” and Basin “B” influenced by
quantity and direction of specified flow.
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3.“Construct the Frame:” Boundary ConditionsSpecified Flow – darcy’s law
Basin
”B”
GW Flow
𝑙
H1 H2
𝑄 = 𝐴(𝐾 ×𝐻2− 𝐻1
𝑙)
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3.“Construct the Frame:” Boundary Conditions“Head-Dependent Flow” = Cross boundary flow proportional to
water level differences
Basin
“A”
Basin
”B”
GW Flow
Groundwater conditions in Basin “A” and Basin “B” determined by
relative water level changes within basins.
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3.“Construct the Frame:” Boundary ConditionsHead-Dependent Flow
Basin
”B”
GW Flow
Monitoring well location.
Flow calculated based on
difference between adjacent
external water level and basin
model-water calculated water
level.
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3.“Construct the Frame:” Boundary ConditionsHead-Dependent Flow
River/Stream is a special case
of head-dependent flux
boundary.
Source: Harbaugh, 2005, USGS Techniques and Methods 6-A16
Low permeability
streambed material
Low permeability
streambed material
Head at the node
in the cell
Head at the node
in the cell
Head at the bottom of the riverbed is equal to
the head at the node in the cell
Head at the bottom of the riverbed is equal to
elevation of bottom of riverbed
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3.“Construct the Frame:” Boundary Conditions
Uncertain boundary
conditions can be located
large distances from basin to
correspond with physical
boundaries or reduce
influence on basin model
results.
Model Boundary
Basin Boundary
Eastern San Joaquin Water Resources Model
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3. “Construct the Frame:” Boundary ConditionsLinked/nested models
Uncertain boundary conditions can be determined by output from other (e.g., Linked/Nested Models).
Specified water level or flux
along/across Local Model
boundaries linked to simulated
values from Regional Model.
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3.“Construct the Frame:” Boundary ConditionsLinked/nested models
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EXAMPLE: regional
model-calculated water
levels used by local
model.
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3.“Construct the Frame:” Boundary ConditionsEvaluating cross boundary flows
Flow directions should be the same
Outflow from one basin should be an inflow to the
adjacent basin
The magnitude of flow to/from adjacent basins
need not be exact but should agree within
reason
Differences should not materially change conclusions
based on model output
The inferred source/sink for the water should be
the same
The water should be entering/leaving the same primary
aquifer, surface water feature, etc.
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3.“Plumb and Wire:”
Aquifer Properties
Water storage and transmitting
properties
-Aquifer tests
-Published values
-Inferred from geology and lithology
Laudon and Belitz, 1989, Texture and depositional
history of near-surface alluvial deposits in the central
part of the western San Joaquin Valley, California, USGS
Open-File Report 89-235
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3.“Attach exterior:” Inflows and outflows
Recharge
R = P + D – RO – CU + ΔS
R = recharge
P = precipitation
D = deliveries (surface water supply)
RO = runoff
CU = consumptive use (ET, urban use)
ΔS = change in storage
Precipitation
(P)
Evapotranspiration
(CU)
Runoff (RO)
Groundwater
Recharge
(R)
Surface Water
Deliveries
(D)
UNSATURATED
SOIL
WATER TABLE
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3.“Attach exterior:” Inflows and outflows
Pumping
Urban, Agricultural and Residential Pumping
- Metered
- Estimated
Land use
Typical use
Precipi-
tation
(P)
Total
Crop
Demand
(D)
Surface Water
Deliveries (D)
Groundwater
Basin
Pumpage (P)
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3.“Paint and Landscape:” Calibration
An acceptable model calibration:
Employs reasonable aquifer properties (e.g. hydraulic
conductivity).
Model-calculated water levels and flows are reasonable.
- Water levels in wells generally agree.
- Seasonal and multi-year changes generally agree.
- Flow directions consistent with observed conditions.
- Volumetric water budget is consistent with independent estimates.
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3.“Paint and Landscape:” Calibration
“History matching” compares model-calculated water levels with corresponding measured values.
Adjust model input within reasonable ranges to improve match.
Ideally the differences are small and random at different locations and times.
Source: GRA WSB model presentation
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3.“Move in:” implementation
Extract water budget and estimate sustainable yield.*
Develop scenarios to represent land use changes, climate
changes, and proposed projects.*
Identifying management areas.*
Identify impacts of projects and management actions.*
Identify data gaps and monitoring networks improvements.*
* GSP Regs §354.18, §354.18(d), §354.20, §354.38, and §354.44
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4. MODEL ADAPTABILITY AND MAINTENANCE
Don’t have to be replaced
or redone
Can be updated and
improved as more and
better data becomes
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4. MODEL ADAPTABILITY AND MAINTENANCE
The level of effort for updates depend on the quality of existing input
data and the questions model is designed to answer, which usually evolve
with time.
Model maintenance is most economic and efficient when:
- There is consensus among stakeholders
- The number of owners is maximized
Model reliance is maximized.
Number of investors is maximized
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Physical Models Mathematical Models
Analytical
Numerical
5. AVAILABLE MODELS – WHICH MODEL TO USE?
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𝐾 ×∆𝐻
𝑙
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5. AVAILABLE MODELS -The model platform is the numerical solver for the mathematical
model
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5. AVAILABLE MODELS -The application employs the platform to represent a specific site/basin
Example applications relevant to the Cosumnes Subbasin - the Subbasin is contained entirely within the geographic extent of the model
Central Valley Groundwater-Surface Water Simulation Model (C2VSim-FG)
Central Valley Hydrologic Model (CVHM)
Eastern San Joaquin Water Resources Model (ESJWRM)
Sacramento Area Integrated Water Resources Model) (SacIWRM)
- Updated version Cosumnes South American North American Model (CoSANA)
Sacramento Valley Groundwater-Surface Water Simulation Model (SVSim)
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EXAMPLE ApplicationCentral Valley Groundwater-Surface Water
Simulation Model (C2VSIM-FG)
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EXAMPLE ApplicationCentral Valley Hydrologic Model (CVHM)
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EXAMPLE ApplicationsSacramento Area Integrated Water Resources Model
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5. SGMA STANDARDS - PLATFORM AND APPLICATION
California Department of Water Resources Sustainable Groundwater Management Program, “Best Management Practices for the Sustainable Management of Groundwater Modeling BMP,” December 2016.
California Department of Water Resources Sustainable Groundwater Management Program, “Best Management Practices for the Sustainable Management of Groundwater Hydrogeologic Conceptual Model
BMP,” December 2016.
DWR Sustainable Groundwater Management Program, “Groundwater Sustainability Plan (GSP) Emergency Regulations Guide,” 2016.
Standard Notes
Publicly available documentation IWFM or MODFLOW
Peer reviewed mathematical foundation
and model code IWFM or MODFLOW
Public domain open-source software IWFM or MODFLOW
Covers entire basin (at a minimum) Model Grid/Mesh Specifications
Boundary conditions consistent between
adjacent basin models South American and Eastern San Joaquin Valley
Based on detailed HCM In Progress
Sensitivity tests and uncertainty analysis Model Development
Model adaptability (e.g., accommodate
additional data and/or refined HCM) IWFM or MODFLOW
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TAKE AWAY
Models support decision makers – they don’t make decisions.
Expectations - No model is perfect.
Model’s can be updated and improved over time.
- Quantity and quality of existing input data.
- Questions model is intended to answer evolve.
Maintenance and improvement is most efficient when ownership is maximized:
- There is consensus among stakeholders.
- Distributes costs.