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Brackish Groundwater:
Perspectives on Potentially Favorable
Development Areas & Deep Brine Injection
Governor’s Water Augmentation Council
Desalination Committee
Leslie T. Katz, P.G.
Montgomery & Associates
www.elmontgomery.com
May 15, 2017
Why Look at Brackish GW in Arizona?
• Largest unallocated water resource
• More than 600 million AF of recoverable brackish
groundwater in storage
• Almost 100 times current total annual AZ water use
• Desalination is proven technology and economical
under certain circumstances
• Brine disposal via deep injection may be feasible
and protective in some hydrogeologic settings
USGS 2017 – US Brackish Groundwater Regions
3
USGS 2017 – AZ Brackish Groundwater
Maximum TDS
in Upper
50 – 500 Feet
of Aquifer
2008 AZ Brackish GW Study Scope
• Identify, quantify, and characterize brackish groundwater reserves
using existing data sets
• Evaluate areas based on established set of criteria
• Select areas for further study based on degree to which criteria are
fulfilled and absence of fatal flaws
 Focus on potential to replace or augment CAP supplies
• Identify data gaps
• Make recommendations for future investigations in favorable areas
2008 Brackish GW Study Ranking Criteria
• Water quality
o 1,000 – 10,000 mg/L TDS (~1,600 – 17,000 uS/cm)
o Lower concentrations of constituents that make RO expensive
o Lack of naturally-occurring or human-caused contaminants not removed with RO
• Sustainability
o Ability to supply up to 10,000 AFY
o Sufficient groundwater in storage above 1,200 feet
• Economic feasibility
o Depth to water not excessive
o Adequate well yields
o Brine injection potential
• Environmental factors
o No anticipated subsidence impacts
o No adverse impacts to existing users
M&A 2008 – Brackish Groundwater in Arizona
4
Electrical
Conductivity
(USGS Data)
Basin Sub-basin or Area
Estimated Desalination
Potential Fatal Flaws
WEST SALT RIVER VALLEY Buckeye Most promising None
GILA BEND BASIN Gila Bend Most promising None
YUMA Yuma Mesa and Yuma Valley Most promising Existing desalting plant
LOWER SANTA CRUZ Picacho-Eloy Most promising None
LITTLE COLORADO RIVER Winslow-Leupp Most promising None
WILLCOX BASIN Willcox Playa Most promising Brackish storage unknown
COL. RVER-HOOVER TO IMPERIAL
DAMS Parker Potentially promising Possibly Indian water rights
LITTLE COLORADO RIVER Concho-Petrified National Forest Potentially promising None
GILA-PAINTED ROCK TO TEXAS HILL Painted Rock Reservoir to Texas Hill Potentially promising Small groundwater storage
GILA-TEXAS HILL TO DOME Wellton-Mohawk Potentially promising Surface water particulates; other uses
HARQUAHALA PLAINS Harquahala Potentially promising Generally low TDS
LITTLE COLORADO RIVER Holbrook-Joseph City Potentially promising None
LITTLE COLORADO RIVER Hopi Reservation Potentially promising Depth to water, excessive salinity
HUALAPAI VALLEY Red Lake Potentially promising Volume of brackish groundwater unknown
LOWER HASSAYAMPA Tonopah Desert/Centennial Wash Potentially promising Low TDS
LOWER SAN PEDRO San Manuel-Winkleman Potentially promising Small well yields and storage
RANEGRAS PLAIN (RAN) Ranegras Plain Potentially promising Low TDS
SAFFORD BASIN Gila Valley Potentially promising None
LITTLE COLORADO RIVER Cameron-Wupatki N.M. Potentially promising None
SAFFORD BASIN San Simon Potentially promising None
LITTLE COLORADO RIVER St. Johns-Springerville Potentially promising None
TUCSON AMA Avra Valley Less promising Mostly low TDS
BIG SANDY VALLEY Big Sandy Less promising Low TDS, small yield
DOUGLAS BASIN Douglas Less promising Low TDS
DUNCAN BASIN Duncan Valley Less promising Low TDS
UPPER SAN PEDRO Sierra Vista Less promising Low TDS, base flow protection
TUCSON AMA Tucson Less promising Low TDS (?)
MIDDLE VERDE RIVER Camp Verde Less promising Small well yields and storage
VIRGIN RIVER Littlefield Less promising Small storage
WATERMAN WASH Rainbow Valley Less promising Low TDS, small storage
WESTERN MEXICAN DRAIN Ajo Less promising Low TDS, small well yields and storage
Brackish Groundwater Area Ranking
Basin
Sub-basin or
Area
Estimated
Desalination
Potential
Estimated
Available
Groundwater
Storage (AF)
TDS Range
(mg/L)
Well Yields
(gpm)
Depth to
Water (feet,
bls)
Potential for
Local Brine
Disposal
Salinity
Source Subsidence CAP Interest
WEST SALT RIVER
VALLEY Buckeye
Most
promising 20,000,000 Low High 500-2,500 <20 Evaporation
Irrigation
and
effluent None
Replace CAP
use
GILA BEND BASIN Gila Bend
Most
promising 25,000,000 1,000 5,000 300-4,000 75-200 Evaporation
Irrigation
and
evaporites
Little or
none
Solar power,
replace CAP
use
YUMA
Yuma Mesa and
Yuma Valley
Most
promising 49,000,000 900 5,000 2,000-5,000 20-70 Evaporation
Mostly
irrigation None
Augment
Colorado
River supply
LOWER SANTA
CRUZ Picacho-Eloy
Most
promising 24,000,000 <1,000 4,000 1,000-3,000 300 500
Evaporation
or injection
Bedded
halite and
anhydrite Existing
Near CAP
canal
LITTLE COLORADO
RIVER Winslow-Leupp
Most
promising
16,000,000
(brackish) 1,500 5,000 300-1,000 50-400
Nearby
injection
Bedded
halite --
Navajo water
rights,
municipal,
power
WILLCOX BASIN Willcox Playa
Most
promising
20,000,000
(brackish) 1,500 >10,000 1,000-2,000 40-300 Evaporation
Evaporites
near playa
and
irrigation Existing
Sierra Vista
supply,
power
RANEGRAS PLAIN Ranegras Plain
Potentially
promising 20,000,000 1,000 >50,000 100-3,000 30-300 Evaporation Natural (?) Potential
Near CAP
canal
SAFFORD BASIN Gila Valley
Potentially
promising 35,000,000 400 4,000 500-2,000 100-500
Nearby
injection (?)
Evaporites
and
irrigation -- None
LITTLE COLORADO
RIVER
Cameron-
Wupatki N.M.
Potentially
promising 6-10 million 400 64,000 500-1,000 200-800
Possible
injection
Bedded
halite None Little or none
SAFFORD BASIN San Simon
Potentially
promising 30,000,000 300 9,000 500-2,000 30-150 Evaporation Irrigation Existing None
LITTLE COLORADO
RIVER
St. Johns-
Springerville
Potentially
promising 20,000,000 (?) 1,500 25,000 500-2,000 50-150 Evaporation
Evaporites
(?) None Little or none
Most Promising & Potentially Promising
Brackish Groundwater Areas
Areas for Further Study
• Buckeye Area
• Gila Bend Basin
• Yuma Mesa and Yuma Valley
• Picacho Basin
• Winslow-Leupp Area (Little Colorado River Basin)
• Willcox Playa Area (Willcox Basin)
Areas for Further Investigation
• Buckeye Area
• Gila Bend Basin
• Yuma Mesa / Yuma Valley
• Picacho Basin
• Winslow-Leupp Area
• Willcox Playa Area
EC in Buckeye Area
Buckeye Area Pros / Cons
Pros
• Large area of groundwater in optimal TDS range
• Coincides with water logged area
• Current and anticipate demand for fresh water supplies
• Multiple sources of TDS
Cons
• Future land use changes may affect brackish supply
• Groundwater chemistry (Ca, Mg) may pose challenges for
desal
• Potential presence of pesticides and pharmaceuticals
• Brine disposal may be problematic
TDS in Gila Bend Area
5
Gila Bend Area Pros / Cons
Pros
• Large volume of groundwater in storage with TDS
concentrations in optimal range
• Water quality very consistent laterally/vertically
• Low Ca concentrations
• Recharge from runoff events and wastewater flows
• Irrigation demand and potential demand for solar power plant
Cons
• Potential presence of pesticides and pharmaceuticals
• Brine disposal may be problematic
EC in Yuma Mesa / Yuma Valley
Yuma Valley /Mesa Area Pros / Cons
Pros
• Long-term, sustainable supply of brackish groundwater
• Pumping could partially mitigate water logging
• Anticipated long-term demand for agricultural supplies
Cons
• Administration of Colorado River accounting surface during
drought could be problematic
• Recent water quality data is lacking and can’t rule-out issues
for desal
• Brine disposal may be problematic
EC in Picacho Basin
Picacho Basin Pros / Cons
Pros
• Long-term, sustainable supply of brackish groundwater
• Anticipated long-term demand for agricultural supplies,
particularly during CAP shortages
• Deep injection may be feasible
Cons
• Recharge of imported CAP water could decrease TDS over
time
• Documented subsidence and fissures
• Issues with permitting of deep brine injection
TDS in Winslow – Leupp Area
5
Winslow-Leupp Area Pros / Cons
Pros
• Significant supply of brackish groundwater
• Good data in some areas from recent testing
• Potential demand from Flagstaff and tribes
• Deep brine disposal potentially feasible
Cons
• Hydrogeologic and water quality conditions are variable
• Water quality may deteriorate and/or change over time
• Issues with permitting of deep brine disposal
Deep Brine Injection Opportunities/Challenges
• All subsurface water currently regulated as a drinking
water aquifer in AZ
• APP process already encompasses injection wells
• Current structure provides potential pathways
o Aquifer declassification
o Application of existing regulatory structure
o Use of narrative standards
o Non-degradation demonstration
o Protection of existing and foreseeable uses
Permitting and Implementation of Deep
Brine Injection Will Require…
• Robust site conceptual model
o Site characterization to update and augment existing data regarding vertical and lateral
lithologic and water quality conditions
o Develop geologic model representing presence and continuity of brackish groundwater aquifer,
confining units/barriers to vertical communication, and deeper high-TDS horizons potentially
favorable for injection (adjacent to evaporite deposits?)
• Reliable groundwater flow (and possibly transport) model
o Simulate conditions within and interactions between brackish groundwater extraction and brine
injection zones
o Project changes over time under current and potential future conditions
• Coordinated efforts between stakeholders
o Benefits for funding, data sharing, and permitting
• Demonstration of technical and economic feasibility
o Recommend smaller scale pilot injection project using brackish rather than saline water
o Select basin that is better characterized and inject into known high-TDS horizon

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AZ Brackish Groundwater_May2017

  • 1. Brackish Groundwater: Perspectives on Potentially Favorable Development Areas & Deep Brine Injection Governor’s Water Augmentation Council Desalination Committee Leslie T. Katz, P.G. Montgomery & Associates www.elmontgomery.com May 15, 2017
  • 2. Why Look at Brackish GW in Arizona? • Largest unallocated water resource • More than 600 million AF of recoverable brackish groundwater in storage • Almost 100 times current total annual AZ water use • Desalination is proven technology and economical under certain circumstances • Brine disposal via deep injection may be feasible and protective in some hydrogeologic settings
  • 3. USGS 2017 – US Brackish Groundwater Regions 3
  • 4. USGS 2017 – AZ Brackish Groundwater Maximum TDS in Upper 50 – 500 Feet of Aquifer
  • 5. 2008 AZ Brackish GW Study Scope • Identify, quantify, and characterize brackish groundwater reserves using existing data sets • Evaluate areas based on established set of criteria • Select areas for further study based on degree to which criteria are fulfilled and absence of fatal flaws  Focus on potential to replace or augment CAP supplies • Identify data gaps • Make recommendations for future investigations in favorable areas
  • 6. 2008 Brackish GW Study Ranking Criteria • Water quality o 1,000 – 10,000 mg/L TDS (~1,600 – 17,000 uS/cm) o Lower concentrations of constituents that make RO expensive o Lack of naturally-occurring or human-caused contaminants not removed with RO • Sustainability o Ability to supply up to 10,000 AFY o Sufficient groundwater in storage above 1,200 feet • Economic feasibility o Depth to water not excessive o Adequate well yields o Brine injection potential • Environmental factors o No anticipated subsidence impacts o No adverse impacts to existing users
  • 7. M&A 2008 – Brackish Groundwater in Arizona 4 Electrical Conductivity (USGS Data)
  • 8. Basin Sub-basin or Area Estimated Desalination Potential Fatal Flaws WEST SALT RIVER VALLEY Buckeye Most promising None GILA BEND BASIN Gila Bend Most promising None YUMA Yuma Mesa and Yuma Valley Most promising Existing desalting plant LOWER SANTA CRUZ Picacho-Eloy Most promising None LITTLE COLORADO RIVER Winslow-Leupp Most promising None WILLCOX BASIN Willcox Playa Most promising Brackish storage unknown COL. RVER-HOOVER TO IMPERIAL DAMS Parker Potentially promising Possibly Indian water rights LITTLE COLORADO RIVER Concho-Petrified National Forest Potentially promising None GILA-PAINTED ROCK TO TEXAS HILL Painted Rock Reservoir to Texas Hill Potentially promising Small groundwater storage GILA-TEXAS HILL TO DOME Wellton-Mohawk Potentially promising Surface water particulates; other uses HARQUAHALA PLAINS Harquahala Potentially promising Generally low TDS LITTLE COLORADO RIVER Holbrook-Joseph City Potentially promising None LITTLE COLORADO RIVER Hopi Reservation Potentially promising Depth to water, excessive salinity HUALAPAI VALLEY Red Lake Potentially promising Volume of brackish groundwater unknown LOWER HASSAYAMPA Tonopah Desert/Centennial Wash Potentially promising Low TDS LOWER SAN PEDRO San Manuel-Winkleman Potentially promising Small well yields and storage RANEGRAS PLAIN (RAN) Ranegras Plain Potentially promising Low TDS SAFFORD BASIN Gila Valley Potentially promising None LITTLE COLORADO RIVER Cameron-Wupatki N.M. Potentially promising None SAFFORD BASIN San Simon Potentially promising None LITTLE COLORADO RIVER St. Johns-Springerville Potentially promising None TUCSON AMA Avra Valley Less promising Mostly low TDS BIG SANDY VALLEY Big Sandy Less promising Low TDS, small yield DOUGLAS BASIN Douglas Less promising Low TDS DUNCAN BASIN Duncan Valley Less promising Low TDS UPPER SAN PEDRO Sierra Vista Less promising Low TDS, base flow protection TUCSON AMA Tucson Less promising Low TDS (?) MIDDLE VERDE RIVER Camp Verde Less promising Small well yields and storage VIRGIN RIVER Littlefield Less promising Small storage WATERMAN WASH Rainbow Valley Less promising Low TDS, small storage WESTERN MEXICAN DRAIN Ajo Less promising Low TDS, small well yields and storage Brackish Groundwater Area Ranking
  • 9. Basin Sub-basin or Area Estimated Desalination Potential Estimated Available Groundwater Storage (AF) TDS Range (mg/L) Well Yields (gpm) Depth to Water (feet, bls) Potential for Local Brine Disposal Salinity Source Subsidence CAP Interest WEST SALT RIVER VALLEY Buckeye Most promising 20,000,000 Low High 500-2,500 <20 Evaporation Irrigation and effluent None Replace CAP use GILA BEND BASIN Gila Bend Most promising 25,000,000 1,000 5,000 300-4,000 75-200 Evaporation Irrigation and evaporites Little or none Solar power, replace CAP use YUMA Yuma Mesa and Yuma Valley Most promising 49,000,000 900 5,000 2,000-5,000 20-70 Evaporation Mostly irrigation None Augment Colorado River supply LOWER SANTA CRUZ Picacho-Eloy Most promising 24,000,000 <1,000 4,000 1,000-3,000 300 500 Evaporation or injection Bedded halite and anhydrite Existing Near CAP canal LITTLE COLORADO RIVER Winslow-Leupp Most promising 16,000,000 (brackish) 1,500 5,000 300-1,000 50-400 Nearby injection Bedded halite -- Navajo water rights, municipal, power WILLCOX BASIN Willcox Playa Most promising 20,000,000 (brackish) 1,500 >10,000 1,000-2,000 40-300 Evaporation Evaporites near playa and irrigation Existing Sierra Vista supply, power RANEGRAS PLAIN Ranegras Plain Potentially promising 20,000,000 1,000 >50,000 100-3,000 30-300 Evaporation Natural (?) Potential Near CAP canal SAFFORD BASIN Gila Valley Potentially promising 35,000,000 400 4,000 500-2,000 100-500 Nearby injection (?) Evaporites and irrigation -- None LITTLE COLORADO RIVER Cameron- Wupatki N.M. Potentially promising 6-10 million 400 64,000 500-1,000 200-800 Possible injection Bedded halite None Little or none SAFFORD BASIN San Simon Potentially promising 30,000,000 300 9,000 500-2,000 30-150 Evaporation Irrigation Existing None LITTLE COLORADO RIVER St. Johns- Springerville Potentially promising 20,000,000 (?) 1,500 25,000 500-2,000 50-150 Evaporation Evaporites (?) None Little or none Most Promising & Potentially Promising Brackish Groundwater Areas
  • 10. Areas for Further Study • Buckeye Area • Gila Bend Basin • Yuma Mesa and Yuma Valley • Picacho Basin • Winslow-Leupp Area (Little Colorado River Basin) • Willcox Playa Area (Willcox Basin)
  • 11. Areas for Further Investigation • Buckeye Area • Gila Bend Basin • Yuma Mesa / Yuma Valley • Picacho Basin • Winslow-Leupp Area • Willcox Playa Area
  • 13. Buckeye Area Pros / Cons Pros • Large area of groundwater in optimal TDS range • Coincides with water logged area • Current and anticipate demand for fresh water supplies • Multiple sources of TDS Cons • Future land use changes may affect brackish supply • Groundwater chemistry (Ca, Mg) may pose challenges for desal • Potential presence of pesticides and pharmaceuticals • Brine disposal may be problematic
  • 14. TDS in Gila Bend Area 5
  • 15. Gila Bend Area Pros / Cons Pros • Large volume of groundwater in storage with TDS concentrations in optimal range • Water quality very consistent laterally/vertically • Low Ca concentrations • Recharge from runoff events and wastewater flows • Irrigation demand and potential demand for solar power plant Cons • Potential presence of pesticides and pharmaceuticals • Brine disposal may be problematic
  • 16. EC in Yuma Mesa / Yuma Valley
  • 17. Yuma Valley /Mesa Area Pros / Cons Pros • Long-term, sustainable supply of brackish groundwater • Pumping could partially mitigate water logging • Anticipated long-term demand for agricultural supplies Cons • Administration of Colorado River accounting surface during drought could be problematic • Recent water quality data is lacking and can’t rule-out issues for desal • Brine disposal may be problematic
  • 18. EC in Picacho Basin
  • 19. Picacho Basin Pros / Cons Pros • Long-term, sustainable supply of brackish groundwater • Anticipated long-term demand for agricultural supplies, particularly during CAP shortages • Deep injection may be feasible Cons • Recharge of imported CAP water could decrease TDS over time • Documented subsidence and fissures • Issues with permitting of deep brine injection
  • 20. TDS in Winslow – Leupp Area 5
  • 21. Winslow-Leupp Area Pros / Cons Pros • Significant supply of brackish groundwater • Good data in some areas from recent testing • Potential demand from Flagstaff and tribes • Deep brine disposal potentially feasible Cons • Hydrogeologic and water quality conditions are variable • Water quality may deteriorate and/or change over time • Issues with permitting of deep brine disposal
  • 22. Deep Brine Injection Opportunities/Challenges • All subsurface water currently regulated as a drinking water aquifer in AZ • APP process already encompasses injection wells • Current structure provides potential pathways o Aquifer declassification o Application of existing regulatory structure o Use of narrative standards o Non-degradation demonstration o Protection of existing and foreseeable uses
  • 23. Permitting and Implementation of Deep Brine Injection Will Require… • Robust site conceptual model o Site characterization to update and augment existing data regarding vertical and lateral lithologic and water quality conditions o Develop geologic model representing presence and continuity of brackish groundwater aquifer, confining units/barriers to vertical communication, and deeper high-TDS horizons potentially favorable for injection (adjacent to evaporite deposits?) • Reliable groundwater flow (and possibly transport) model o Simulate conditions within and interactions between brackish groundwater extraction and brine injection zones o Project changes over time under current and potential future conditions • Coordinated efforts between stakeholders o Benefits for funding, data sharing, and permitting • Demonstration of technical and economic feasibility o Recommend smaller scale pilot injection project using brackish rather than saline water o Select basin that is better characterized and inject into known high-TDS horizon

Editor's Notes

  1. https://water.usgs.gov/ogw/gwrp/brackishgw/ Modified from Feth and others, 1965 Talk will be focusing on our work in Arizona and Texas https://water.usgs.gov/ogw/gwrp/brackishgw/approach.html
  2. https://water.usgs.gov/ogw/gwrp/brackishgw/use.html
  3. https://water.usgs.gov/ogw/gwrp/brackishgw/use.html
  4. https://water.usgs.gov/ogw/gwrp/brackishgw/use.html