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Integrated
Groundwater/Surface Water Modelling
to Assess Irrigation Demand
and Drought Response
in a Southwestern Ontario Watershed
Dirk Kassenaar, E.J. Wexler
Peter J. Thompson, Michael Takeda
CWRA Montreal
May 25, 2016
Presentation Outline
1. Introduction: Understanding Irrigation Demand
2. Integrated SW/GW Modelling
3. Pilot Watershed: Whitemans Creek Tier 3/ Low Water Response Project
4. GSFLOW Code modifications and conceptual testing
5. Simulation of farm operations in Whitemans Creek
6. Conclusions
Integrated Simulation of Irrigation Demand - Introduction 2
Agricultural Water Use
 Agricultural irrigation is growing in response to:
▪ An increase in climate variability
▪ Contract farming: “supply chain” management and production certainty
▪ Advances in precision agriculture
• “Irrigation is next frontier in precision agriculture” (Farm Press, Oct, 2014)
 Irrigation operations are frequently driven by dynamic soil moisture
▪ Highly adaptive water use
 We need a method to simulate “soil moisture-based irrigation water use”,
including:
▪ Losses of irrigation water to ET or runoff to streams
▪ Return flows – irrigation water that re-infiltrates
▪ Effect of precipitation events on recently irrigated crop land
Integrated Simulation of Irrigation Demand - Modelling Approach 3
Integrated SW/GW Modelling: Advantages
 Better estimate of groundwater recharge and feedback
(rejected recharge)
 Better representation streamflow and head-dependent
leakage
 Better representation of SW/GW storage.
 Better representation of cumulative effects of takings.
 Better calibration: input total precipitation, calibrate to
total flows (no baseflow separation)
 It’s just better...
Integrated Simulation of Irrigation Demand - Modelling Approach 4
California Department of Water Resources
USGS GSFLOW
 USGS integrated GW/SW model
▪ Based on MODFLOW-NWT and PRMS
(Precipitation-Runoff Modelling System)
▪ Fully-distributed: Cell-based representation
▪ Excellent balance of hydrology, hydraulics and GW
▪ Open-source, proven and very well documented
5- Modelling Approach
Irrigation Module for GSFLOW
 Earthfx Inc. has developed a new irrigation module for GSFLOW
 The general technical approach is based on work by the USGS for the
simulation of water use in California’s Central Valley
▪ The MODFLOW-OWHM code includes the “Farm Process” module
▪ OWHM, however, is only a groundwater model, and therefore does not represent the
soil zone, runoff processes and total streamflow routing
▪ GSFLOW is a complete and integrated representation of the hydrologic processes
that drive irrigation demand
 The implementation of this new soil-moisture irrigation demand module is
currently being tested in the Whitemans Creek Watershed with funding support
from the Ontario MNR, MOECC and Grand River Conservation Authority
Integrated Simulation of Irrigation Demand - Modelling Approach 6
PILOT WATERSHED -
WHITEMANS CREEK
Integrated Simulation of Irrigation Demand – Watershed Overview 7
Study Area
 Whitemans Creek watershed is
located southwest of Cambridge,
Ontario
Integrated Simulation of Irrigation Demand - Modelling Approach 8
 Numerous groundwater-fed wetlands.
 Streams are deeply incised in southeast.
 Fluctuations in shallow water table affects
recharge, runoff, ET, and groundwater
discharge to streams.
 Main branch of Whitemans Creek is a
cold-water stream supporting Brown,
Brook, and Rainbow trout.
 Uplands of watershed generally classed as
warm-water reaches.
 Main valley serves as a continuous habitat
corridor from GR Valley into Oxford County.
Wetlands and streams in the Whitemans
Creek subwatershed
Natural Features
Integrated Simulation of Irrigation Demand - Watershed Overview 9
Current Land Use
10Integrated Simulation of Irrigation Demand - Watershed Overview
(SOLRIS v2, 2015)
Agricultural Usage
11
 Corn, sod farms, tobacco, mixed..
 Water usage can vary
considerably by crop type (sod vs.
hay/pasture).
 Includes significant irrigated
water use in Norfolk Sand Plain
Integrated Simulation of Irrigation Demand - Watershed Overview
Integrated Simulation of Irrigation Demand - Geologic & Hydrostratigraphic Model 12
Conceptual Hydrostratigraphic Model
 Wisconsinan glaciation (85,000 to 11,000 years ago)
 Regional Till Sheets (minor tills in report)
▪ Canning Till – very stiff clay till; overlies discontinuous “pre-
Canning” tills and “pre-Canning” sands.
▪ Catfish Creek Till - stony, over-consolidated, sandy silt to silty
sand till; outcrops at Bright.
▪ Tavistock Till – major unit; outcrops in north and to west of
Whitemans; clayey silt till.
▪ Port Stanley Till - major unit; outcrops in middle of study area;
stiff clayey silt to silt till; sandier to north.
▪ Wentworth Till – Outcrops to east near Bethel Rd; silty sand till;
overrides outwash and Lake Whittlesey deposits.
 Erie Phase Deposits
▪ Waterloo Moraine-age deposits; overlie Catfish Creek and Maryhill
Tills.
 Grand River Outwash
▪ Ice recession during Mackinaw phase.
▪ Difficult to distinguish from overlying Lake Whittlesey sands.
 Lacustrine Deposits
▪ Associated with Glacial Lake Whittlesey
▪ Source of the fine sands of Norfolk sand plain
Integrated Simulation of Irrigation Demand - Geologic & Hydrostratigraphic Model 13
Quaternary Geology
Simulated Streams
Integrated Simulation of Irrigation Demand - GW Model Construction/Calibration 14
 1,767 km of simulated stream channels.
▪ 15,729 Reaches (GW Cell Interactions)
 Properties assigned by Strahler Class
▪ Manning’s Roughness, 8-Point Cross Section, Bed
Conductances
▪ Class 1 represents 842 of 1767 km
Simulation Results: Long Term Average ET (WY1976-WY2010)
Integrated Simulation of Irrigation Demand – PRMS (Hydrologic Submodel) 15
Potential Actual
Simulated Runoff
Integrated Simulation of Irrigation Demand – PRMS (Hydrologic Submodel) 16
Long Term Average Recharge Comparison
Integrated Simulation of Irrigation Demand – PRMS (Hydrologic Submodel) 17
PRMS
(248 mm/year)
GAWSER
(243 mm/year)
18
Actual ET
Integrated Simulation of Irrigation Demand – Preliminary GSFLOW Model Calibration
 Animation shows daily Actual ET from the
PRMS submodel for WY2007, a relatively
dry year
 AET response is sinusoidal but varies
spatially depending on available soil
moisture
 AET is reduced in the dry years because
of basin-wide limitations in available soil
moisture
Animation Link
19
Water Levels
Integrated Simulation of Irrigation Demand – Preliminary GSFLOW Model Calibration
 Animation shows transient water levels
from the MODFLOW submodel in Layer 3
for WY2007
 Groundwater response appears muted
because of contour interval places but
change is in range of 1-2 metres
Animation Link
20
Streamflow
Integrated Simulation of Irrigation Demand – Preliminary GSFLOW Model Calibration
 Animation shows transient streamflow for
WY2007
 Results show:
▪ Streamflow response to dry year
▪ Where streamflow is intermittent
▪ Location of reaches which might be more
sensitive to drought
 Simulated flows at locations of active and
historic gauges can be compared to
observed.
 Animation Link
21
Streamflow
Integrated Simulation of Irrigation Demand – Preliminary GSFLOW Model Calibration
 Animation shows transient streamflow
for WY2007
 Results highlight an area of the
watershed with relatively low
permeability surface materials.
Animation Link
WATER USE
Whitemans Creek Tier 3
Integrated Simulation of Irrigation Demand - Water Use 22
 Significant agricultural water takings:
▪ Over 95% of reported takings
▪ Takings vary by crop, season, and
antecedent rainfall/ET
 Need historic consumptive use for model calibration.
 Need to predict future usage for drought analysis.
Integrated Simulation of Irrigation Demand - Water Use 23
Water Use - Overview
 Permits to take Water:
▪ Permit ID can be assigned to multiple sources (e.g., 2 different wells).
▪ Sources have generic names (e.g., “Well 1”, “Pond”).
▪ Locations linked to Permit ID, no link to WWIS Well ID.
▪ Sometimes source locations plot close enough to existing wells to assign.
▪ Maximum Permitted Taking often well in excess of actual.
 Water Taking Reporting System
▪ Self reporting compliance poor in 2009; improves in subsequent years.
▪ WTRS data linked to Permit ID/Source; no locations or names.
▪ Queries to match PTTW to WTRS partly successful; varies by year.
• 65% matched in study area; 62% in Whitemans in 2012
• Does (38%) non-reporting equal no usage ?
▪ Taking not always separated by source; is taking amalgamated?
WTRS Sources matching PTTW Sources
Integrated Simulation of Irrigation Demand - Water Use 24
Reconciling Provincial Data
Simulated SW Use
Integrated Simulation of Irrigation Demand - GW Model Construction/Calibration 25
 A total of 70 surface water permits
with 92 sources simulated in the
model
 Surface water permits processed to
assign location of source streams:
▪ Represented using MODFLOW-SFR package
▪ Script used to assign takings (diversions) to
closest simulated stream segment
▪ All ponds assumed to be online with no
mitigative storage effects
Groundwater Permits –
by Primary Purpose
Agricultural Groundwater Permits –
by Sub-Purpose
Integrated Simulation of Irrigation Demand - Water Use 26
Annual Takings for Groundwater Permits –
2012
Annual Takings for Agricultural GW Permits
– 2012
Integrated Simulation of Irrigation Demand - Water Use 27
Analysis of
WTRS data
provides
Insights
Daily Takings
for Agriculture
by Crop Type
(2012)
Integrated Simulation of Irrigation Demand - Water Use 28
Variation in Water Use by Crop
Daily Takings for
Wet vs. Dry Year
(2011-2012)
at a Sod Farm
Integrated Simulation of Irrigation Demand - Water Use 29
Variation in Water Use by Year
Daily Takings for
Agriculture
Sod Farm 1 vs.
Sod Farm 2
(2012)
Integrated Simulation of Irrigation Demand - Water Use 30
Variation in Water Use by Location
 Model calibration runs for GSFLOW Model
based on daily taking data from
PTTW/WTRS.
 470 GW takings
 Well locations and aquifers determined by
matching PTTW to WWIS data.
Integrated Simulation of Irrigation Demand - Water Use 31
Use of PTTW/WTRS Data
Water Use - Conclusions
 Data compiled from multiple sources.
 WTRS data provides good snapshot of recent takings.
 Daily data used in model calibration phase.
 WTRS provides targets for development/calibration of irrigation
submodel.
Integrated Simulation of Irrigation Demand - Water Use 32
SOIL MOISTURE DEMAND-
BASED IRRIGATION MODULE
Earthfx GSFLOW Code Extension
Integrated Simulation of Irrigation Demand - Streamflow Data 33
Irrigation Demand Submodel - Methodology
 Need to predict water use under drought or future development conditions
▪ Simply using maximum permitted rate does not help us understand real crop needs
under future drought conditions.
 Proposed method to estimate water use requires daily takings:
▪ GSFLOW/PRMS daily estimate of soil moisture used to “trigger” irrigation.
▪ Irrigation starts when available soil moisture falls below trigger
▪ Trigger can be defined based on soil and crop type
▪ Irrigation water can be lost to ET, runoff or returned to the GW system
 Predictive irrigation submodel can be calibrated with actual WTRS data.
▪ PTTW/WTRS data used estimating historic use for model calibration.
Integrated Simulation of Irrigation Demand - Water Use 34
Irrigation Demand Submodel – Code Features
 Each farm represented by multiple PRMS cells (fully distributed)
▪ Each farm can have multiple crop types and unique moisture content triggers
▪ Each well is linked to a Farm ID with max pumping rate
▪ Farm SW diversions can take a defined percentage of current daily streamflow
 Soil moisture calculated on a daily basis in PRMS and used to trigger GW
pumping or SW diversion
 Total GW well pumping or SW diversion per farm passed back to PRMS
▪ PRMS adds pumped volume to precipitation (for spray irrigation) or to net
precipitation after interception (for drip irrigation) over farm cells.
▪ PRMS calculates runoff and infiltration in usual manner
Integrated Simulation of Irrigation Demand - Water Use 35
Integration of Irrigation Module
 Low moisture levels in soil
zone reservoir can trigger
spray irrigation from either GW
pumping wells or SW
diversions.
 With drip irrigation, water is
added to the recharge zone
Integrated Simulation of Irrigation Demand - Climate Data 36
Groundwater Model
MODFLOW NWT
PRMS
GWPumping
SWPumping
 Simple problem with streams lakes and multiple irrigated
and non-irrigated farms
 Farm wells and SW diversion used for irrigation
 Different triggers used for each well
 Different irrigation types (drip/spray)
 Animation shows soil moisture in farm vicinity, farm well
pumping, and streamflow
Animation Link
Simple Submodel Testing
Integrated Simulation of Irrigation Demand - Water Use 37
Sub-model Testing
 Example shows one Water Year (Oct 1-Sept 30)
▪ Soil moisture on irrigated farm fields
▪ Groundwater levels as blue contours
▪ Pumping wells shown as small circles
 Fall-winter: Water levels stable – no pumping
▪ Irrigation starts in late May
 Soil moisture represented as color – pumping
adjusted to maintain moisture levels
 GW drawdown cones grow over the summer and
recover in the fall after irrigation stops
Animation Link
Integrated Simulation of Irrigation Demand - Water Use 38
Whitemans Test Simulation
 Testing of GSFLOW Farm Process module
in the Whitemans Creek model
Integrated Simulation of Irrigation Demand - Water Use 39
Whitemans Simulation
 Farm wells linked
to classified crop
areas.
Integrated Simulation of Irrigation Demand - Water Use 40
Soil Moisture Animation link
 Example shows
Integrated Simulation of Irrigation Demand - Water Use 41
Whitemans Simulation: Soil Moisture vs Pumping
 Example compares soil
moisture in an irrigated
field vs a field outside
of the farm.
 Pump comes on when
moisture levels drop –
Irrigated field never
dries out
Integrated Simulation of Irrigation Demand - Water Use 42
43
Conclusions
Integrated Simulation of Irrigation Demand - Conclusions & Next Steps
 Predicting and simulating cumulative water use under future drought conditions
requires an understanding of farm irrigation processes and triggers
 The new GSFLOW irrigation module developed by Earthfx integrates farm
water management practices into a comprehensive and fully integrated SW/GW
model
 Historic climate and WTRS data can be used to develop farm-specific water use
practices and triggers.
▪ Alternatively, standard or best management practices could be represented in the
model to simulate and evaluate improved water use and informed permit renewal

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Integrated Groundwater/Surface Water Modelling to Assess Irrigation Demand and Drought Response in a Southwestern Ontario Watershed

  • 1. Integrated Groundwater/Surface Water Modelling to Assess Irrigation Demand and Drought Response in a Southwestern Ontario Watershed Dirk Kassenaar, E.J. Wexler Peter J. Thompson, Michael Takeda CWRA Montreal May 25, 2016
  • 2. Presentation Outline 1. Introduction: Understanding Irrigation Demand 2. Integrated SW/GW Modelling 3. Pilot Watershed: Whitemans Creek Tier 3/ Low Water Response Project 4. GSFLOW Code modifications and conceptual testing 5. Simulation of farm operations in Whitemans Creek 6. Conclusions Integrated Simulation of Irrigation Demand - Introduction 2
  • 3. Agricultural Water Use  Agricultural irrigation is growing in response to: ▪ An increase in climate variability ▪ Contract farming: “supply chain” management and production certainty ▪ Advances in precision agriculture • “Irrigation is next frontier in precision agriculture” (Farm Press, Oct, 2014)  Irrigation operations are frequently driven by dynamic soil moisture ▪ Highly adaptive water use  We need a method to simulate “soil moisture-based irrigation water use”, including: ▪ Losses of irrigation water to ET or runoff to streams ▪ Return flows – irrigation water that re-infiltrates ▪ Effect of precipitation events on recently irrigated crop land Integrated Simulation of Irrigation Demand - Modelling Approach 3
  • 4. Integrated SW/GW Modelling: Advantages  Better estimate of groundwater recharge and feedback (rejected recharge)  Better representation streamflow and head-dependent leakage  Better representation of SW/GW storage.  Better representation of cumulative effects of takings.  Better calibration: input total precipitation, calibrate to total flows (no baseflow separation)  It’s just better... Integrated Simulation of Irrigation Demand - Modelling Approach 4 California Department of Water Resources
  • 5. USGS GSFLOW  USGS integrated GW/SW model ▪ Based on MODFLOW-NWT and PRMS (Precipitation-Runoff Modelling System) ▪ Fully-distributed: Cell-based representation ▪ Excellent balance of hydrology, hydraulics and GW ▪ Open-source, proven and very well documented 5- Modelling Approach
  • 6. Irrigation Module for GSFLOW  Earthfx Inc. has developed a new irrigation module for GSFLOW  The general technical approach is based on work by the USGS for the simulation of water use in California’s Central Valley ▪ The MODFLOW-OWHM code includes the “Farm Process” module ▪ OWHM, however, is only a groundwater model, and therefore does not represent the soil zone, runoff processes and total streamflow routing ▪ GSFLOW is a complete and integrated representation of the hydrologic processes that drive irrigation demand  The implementation of this new soil-moisture irrigation demand module is currently being tested in the Whitemans Creek Watershed with funding support from the Ontario MNR, MOECC and Grand River Conservation Authority Integrated Simulation of Irrigation Demand - Modelling Approach 6
  • 7. PILOT WATERSHED - WHITEMANS CREEK Integrated Simulation of Irrigation Demand – Watershed Overview 7
  • 8. Study Area  Whitemans Creek watershed is located southwest of Cambridge, Ontario Integrated Simulation of Irrigation Demand - Modelling Approach 8
  • 9.  Numerous groundwater-fed wetlands.  Streams are deeply incised in southeast.  Fluctuations in shallow water table affects recharge, runoff, ET, and groundwater discharge to streams.  Main branch of Whitemans Creek is a cold-water stream supporting Brown, Brook, and Rainbow trout.  Uplands of watershed generally classed as warm-water reaches.  Main valley serves as a continuous habitat corridor from GR Valley into Oxford County. Wetlands and streams in the Whitemans Creek subwatershed Natural Features Integrated Simulation of Irrigation Demand - Watershed Overview 9
  • 10. Current Land Use 10Integrated Simulation of Irrigation Demand - Watershed Overview (SOLRIS v2, 2015)
  • 11. Agricultural Usage 11  Corn, sod farms, tobacco, mixed..  Water usage can vary considerably by crop type (sod vs. hay/pasture).  Includes significant irrigated water use in Norfolk Sand Plain Integrated Simulation of Irrigation Demand - Watershed Overview
  • 12. Integrated Simulation of Irrigation Demand - Geologic & Hydrostratigraphic Model 12 Conceptual Hydrostratigraphic Model
  • 13.  Wisconsinan glaciation (85,000 to 11,000 years ago)  Regional Till Sheets (minor tills in report) ▪ Canning Till – very stiff clay till; overlies discontinuous “pre- Canning” tills and “pre-Canning” sands. ▪ Catfish Creek Till - stony, over-consolidated, sandy silt to silty sand till; outcrops at Bright. ▪ Tavistock Till – major unit; outcrops in north and to west of Whitemans; clayey silt till. ▪ Port Stanley Till - major unit; outcrops in middle of study area; stiff clayey silt to silt till; sandier to north. ▪ Wentworth Till – Outcrops to east near Bethel Rd; silty sand till; overrides outwash and Lake Whittlesey deposits.  Erie Phase Deposits ▪ Waterloo Moraine-age deposits; overlie Catfish Creek and Maryhill Tills.  Grand River Outwash ▪ Ice recession during Mackinaw phase. ▪ Difficult to distinguish from overlying Lake Whittlesey sands.  Lacustrine Deposits ▪ Associated with Glacial Lake Whittlesey ▪ Source of the fine sands of Norfolk sand plain Integrated Simulation of Irrigation Demand - Geologic & Hydrostratigraphic Model 13 Quaternary Geology
  • 14. Simulated Streams Integrated Simulation of Irrigation Demand - GW Model Construction/Calibration 14  1,767 km of simulated stream channels. ▪ 15,729 Reaches (GW Cell Interactions)  Properties assigned by Strahler Class ▪ Manning’s Roughness, 8-Point Cross Section, Bed Conductances ▪ Class 1 represents 842 of 1767 km
  • 15. Simulation Results: Long Term Average ET (WY1976-WY2010) Integrated Simulation of Irrigation Demand – PRMS (Hydrologic Submodel) 15 Potential Actual
  • 16. Simulated Runoff Integrated Simulation of Irrigation Demand – PRMS (Hydrologic Submodel) 16
  • 17. Long Term Average Recharge Comparison Integrated Simulation of Irrigation Demand – PRMS (Hydrologic Submodel) 17 PRMS (248 mm/year) GAWSER (243 mm/year)
  • 18. 18 Actual ET Integrated Simulation of Irrigation Demand – Preliminary GSFLOW Model Calibration  Animation shows daily Actual ET from the PRMS submodel for WY2007, a relatively dry year  AET response is sinusoidal but varies spatially depending on available soil moisture  AET is reduced in the dry years because of basin-wide limitations in available soil moisture Animation Link
  • 19. 19 Water Levels Integrated Simulation of Irrigation Demand – Preliminary GSFLOW Model Calibration  Animation shows transient water levels from the MODFLOW submodel in Layer 3 for WY2007  Groundwater response appears muted because of contour interval places but change is in range of 1-2 metres Animation Link
  • 20. 20 Streamflow Integrated Simulation of Irrigation Demand – Preliminary GSFLOW Model Calibration  Animation shows transient streamflow for WY2007  Results show: ▪ Streamflow response to dry year ▪ Where streamflow is intermittent ▪ Location of reaches which might be more sensitive to drought  Simulated flows at locations of active and historic gauges can be compared to observed.  Animation Link
  • 21. 21 Streamflow Integrated Simulation of Irrigation Demand – Preliminary GSFLOW Model Calibration  Animation shows transient streamflow for WY2007  Results highlight an area of the watershed with relatively low permeability surface materials. Animation Link
  • 22. WATER USE Whitemans Creek Tier 3 Integrated Simulation of Irrigation Demand - Water Use 22
  • 23.  Significant agricultural water takings: ▪ Over 95% of reported takings ▪ Takings vary by crop, season, and antecedent rainfall/ET  Need historic consumptive use for model calibration.  Need to predict future usage for drought analysis. Integrated Simulation of Irrigation Demand - Water Use 23 Water Use - Overview
  • 24.  Permits to take Water: ▪ Permit ID can be assigned to multiple sources (e.g., 2 different wells). ▪ Sources have generic names (e.g., “Well 1”, “Pond”). ▪ Locations linked to Permit ID, no link to WWIS Well ID. ▪ Sometimes source locations plot close enough to existing wells to assign. ▪ Maximum Permitted Taking often well in excess of actual.  Water Taking Reporting System ▪ Self reporting compliance poor in 2009; improves in subsequent years. ▪ WTRS data linked to Permit ID/Source; no locations or names. ▪ Queries to match PTTW to WTRS partly successful; varies by year. • 65% matched in study area; 62% in Whitemans in 2012 • Does (38%) non-reporting equal no usage ? ▪ Taking not always separated by source; is taking amalgamated? WTRS Sources matching PTTW Sources Integrated Simulation of Irrigation Demand - Water Use 24 Reconciling Provincial Data
  • 25. Simulated SW Use Integrated Simulation of Irrigation Demand - GW Model Construction/Calibration 25  A total of 70 surface water permits with 92 sources simulated in the model  Surface water permits processed to assign location of source streams: ▪ Represented using MODFLOW-SFR package ▪ Script used to assign takings (diversions) to closest simulated stream segment ▪ All ponds assumed to be online with no mitigative storage effects
  • 26. Groundwater Permits – by Primary Purpose Agricultural Groundwater Permits – by Sub-Purpose Integrated Simulation of Irrigation Demand - Water Use 26
  • 27. Annual Takings for Groundwater Permits – 2012 Annual Takings for Agricultural GW Permits – 2012 Integrated Simulation of Irrigation Demand - Water Use 27
  • 28. Analysis of WTRS data provides Insights Daily Takings for Agriculture by Crop Type (2012) Integrated Simulation of Irrigation Demand - Water Use 28 Variation in Water Use by Crop
  • 29. Daily Takings for Wet vs. Dry Year (2011-2012) at a Sod Farm Integrated Simulation of Irrigation Demand - Water Use 29 Variation in Water Use by Year
  • 30. Daily Takings for Agriculture Sod Farm 1 vs. Sod Farm 2 (2012) Integrated Simulation of Irrigation Demand - Water Use 30 Variation in Water Use by Location
  • 31.  Model calibration runs for GSFLOW Model based on daily taking data from PTTW/WTRS.  470 GW takings  Well locations and aquifers determined by matching PTTW to WWIS data. Integrated Simulation of Irrigation Demand - Water Use 31 Use of PTTW/WTRS Data
  • 32. Water Use - Conclusions  Data compiled from multiple sources.  WTRS data provides good snapshot of recent takings.  Daily data used in model calibration phase.  WTRS provides targets for development/calibration of irrigation submodel. Integrated Simulation of Irrigation Demand - Water Use 32
  • 33. SOIL MOISTURE DEMAND- BASED IRRIGATION MODULE Earthfx GSFLOW Code Extension Integrated Simulation of Irrigation Demand - Streamflow Data 33
  • 34. Irrigation Demand Submodel - Methodology  Need to predict water use under drought or future development conditions ▪ Simply using maximum permitted rate does not help us understand real crop needs under future drought conditions.  Proposed method to estimate water use requires daily takings: ▪ GSFLOW/PRMS daily estimate of soil moisture used to “trigger” irrigation. ▪ Irrigation starts when available soil moisture falls below trigger ▪ Trigger can be defined based on soil and crop type ▪ Irrigation water can be lost to ET, runoff or returned to the GW system  Predictive irrigation submodel can be calibrated with actual WTRS data. ▪ PTTW/WTRS data used estimating historic use for model calibration. Integrated Simulation of Irrigation Demand - Water Use 34
  • 35. Irrigation Demand Submodel – Code Features  Each farm represented by multiple PRMS cells (fully distributed) ▪ Each farm can have multiple crop types and unique moisture content triggers ▪ Each well is linked to a Farm ID with max pumping rate ▪ Farm SW diversions can take a defined percentage of current daily streamflow  Soil moisture calculated on a daily basis in PRMS and used to trigger GW pumping or SW diversion  Total GW well pumping or SW diversion per farm passed back to PRMS ▪ PRMS adds pumped volume to precipitation (for spray irrigation) or to net precipitation after interception (for drip irrigation) over farm cells. ▪ PRMS calculates runoff and infiltration in usual manner Integrated Simulation of Irrigation Demand - Water Use 35
  • 36. Integration of Irrigation Module  Low moisture levels in soil zone reservoir can trigger spray irrigation from either GW pumping wells or SW diversions.  With drip irrigation, water is added to the recharge zone Integrated Simulation of Irrigation Demand - Climate Data 36 Groundwater Model MODFLOW NWT PRMS GWPumping SWPumping
  • 37.  Simple problem with streams lakes and multiple irrigated and non-irrigated farms  Farm wells and SW diversion used for irrigation  Different triggers used for each well  Different irrigation types (drip/spray)  Animation shows soil moisture in farm vicinity, farm well pumping, and streamflow Animation Link Simple Submodel Testing Integrated Simulation of Irrigation Demand - Water Use 37
  • 38. Sub-model Testing  Example shows one Water Year (Oct 1-Sept 30) ▪ Soil moisture on irrigated farm fields ▪ Groundwater levels as blue contours ▪ Pumping wells shown as small circles  Fall-winter: Water levels stable – no pumping ▪ Irrigation starts in late May  Soil moisture represented as color – pumping adjusted to maintain moisture levels  GW drawdown cones grow over the summer and recover in the fall after irrigation stops Animation Link Integrated Simulation of Irrigation Demand - Water Use 38
  • 39. Whitemans Test Simulation  Testing of GSFLOW Farm Process module in the Whitemans Creek model Integrated Simulation of Irrigation Demand - Water Use 39
  • 40. Whitemans Simulation  Farm wells linked to classified crop areas. Integrated Simulation of Irrigation Demand - Water Use 40
  • 41. Soil Moisture Animation link  Example shows Integrated Simulation of Irrigation Demand - Water Use 41
  • 42. Whitemans Simulation: Soil Moisture vs Pumping  Example compares soil moisture in an irrigated field vs a field outside of the farm.  Pump comes on when moisture levels drop – Irrigated field never dries out Integrated Simulation of Irrigation Demand - Water Use 42
  • 43. 43 Conclusions Integrated Simulation of Irrigation Demand - Conclusions & Next Steps  Predicting and simulating cumulative water use under future drought conditions requires an understanding of farm irrigation processes and triggers  The new GSFLOW irrigation module developed by Earthfx integrates farm water management practices into a comprehensive and fully integrated SW/GW model  Historic climate and WTRS data can be used to develop farm-specific water use practices and triggers. ▪ Alternatively, standard or best management practices could be represented in the model to simulate and evaluate improved water use and informed permit renewal