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Equus Beds ASR Program – Wichita’s Future Water Supply September 6, 2012.

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Presentation on theme: "Equus Beds ASR Program – Wichita’s Future Water Supply September 6, 2012."— Presentation transcript:

1 Equus Beds ASR Program – Wichita’s Future Water Supply September 6, 2012

2 Wichita Public Works & Utilities  186 mi 2 Service Area  425,000+ Served  128,905 Residential Customers  13,291 Commercial Customers  160 MGD Lime Softening Plant  Average Day Demand 60 MGD  186 mi 2 Service Area  425,000+ Served  128,905 Residential Customers  13,291 Commercial Customers  160 MGD Lime Softening Plant  Average Day Demand 60 MGD

3 Wichita Water Utilities Sources of Water Wichita Well Field Little Arkansas River Arkansas River Cheney Reservoir Burrton Bentley Reserve Well Field Wichita Local Well Field Cheney Reservoir – 1965 80MGD Equus Beds Well Field – 1940s+ 55 Wells – 78 MGD Bentley Well Field 6 Wells – 10 MGD Local Well Field 19 Wells – 34 MGD

4 Equus Beds Aquifer  1,400 square miles  4 Counties  2,000 Non-Domestic Water Wells  157,000 acre-feet Withdrawn Annually  1,400 square miles  4 Counties  2,000 Non-Domestic Water Wells  157,000 acre-feet Withdrawn Annually

5 Projected Water Supply Demands Average Day Demand Projections Peak Day Demand Projections Average Day Capacity Max Day Capacity 20002005201020152020202520302035204020452050 YEAR 0 50 100 150 200 250 Million Gallons per Day Demand19922050 Average Day60 MGD112 MGD Max Day125 MGD225 MGD

6 Integrated Local Water Supply Plan (ILWS Plan)  Approved 1993  Meet 2050 Water Demands  Principle Component 100 MGD ASR Program  Approved 1993  Meet 2050 Water Demands  Principle Component 100 MGD ASR Program

7 Equus Beds – Water Level Decline  Since 1940 agricultural and municipal pumping created a depression  65 billion gallons available for storage (to return to 1940 water levels) More than 30 feet of water-level decline since 1940

8 Equus Beds – Chloride Migration  Studies demonstrate chloride will migrate into the well field by 2050  Chlorides will exceed 250 ppm

9 Decline in Storage Volume

10 ASR A Win-Win Project  Reliable & Sustainable Water Supply Source through 2050  Water Quality Protected from Salt Water Contamination  No Requirements to Curtail Irrigation  Irrigators Have Lower Pumping Costs  Improves Low Flows in Little Ark. River  Less Land Required  Reliable & Sustainable Water Supply Source through 2050  Water Quality Protected from Salt Water Contamination  No Requirements to Curtail Irrigation  Irrigators Have Lower Pumping Costs  Improves Low Flows in Little Ark. River  Less Land Required

11 Challenges to ASR Project  1 st ASR Project in Kansas  No Regulations in Place to Administer  No Proof that Water can be Diverted from River by Wells  No Regulations in Place to Administer Bank Storage Wells  No Documentation that ASR would not Contaminate Shared Aquifer  Poor Image of City in Project Area  1 st ASR Project in Kansas  No Regulations in Place to Administer  No Proof that Water can be Diverted from River by Wells  No Regulations in Place to Administer Bank Storage Wells  No Documentation that ASR would not Contaminate Shared Aquifer  Poor Image of City in Project Area

12 Scale of ASR Program  Ultimate Capacity to Recharge & Recover 100 MGD  80 mi 2 area  Recharge Facilities at Build-out  97 ASR Wells  2 Recharge Basins  ASR Wells  Average Depth ~ 200 ft  Average Injection Rate ~ 1 MGD  134 Monitoring Wells  Ultimate Capacity to Recharge & Recover 100 MGD  80 mi 2 area  Recharge Facilities at Build-out  97 ASR Wells  2 Recharge Basins  ASR Wells  Average Depth ~ 200 ft  Average Injection Rate ~ 1 MGD  134 Monitoring Wells

13 Source of Recharge Water  Little Arkansas River  High Turbidity  Varies from 8 - 2000 NTUs  High Atrazine Concentration  Varies from >1 – 50  g/L  Little Arkansas River  High Turbidity  Varies from 8 - 2000 NTUs  High Atrazine Concentration  Varies from >1 – 50  g/L  Surface Water can only be diverted at Above Base Flow Conditions  Expect to Recharge 120 days/year  Spring & Early Fall  Surface Water can only be diverted at Above Base Flow Conditions  Expect to Recharge 120 days/year  Spring & Early Fall

14 Typical Storm Event Minimum Flowrate for Diversion

15 ASR Program Schematic

16 Recharge Basin  Area  4.5 acres  Recharge Rate  ~ 1.5 in/day

17 Typical ASR Recharge Well Recharge Tubes (3-4 per well)

18

19 ASR Phase I  Location selected to prevent migration of chlorides into the Equus Beds  Constructed to establish a hydraulic barrier  Location selected to prevent migration of chlorides into the Equus Beds  Constructed to establish a hydraulic barrier Phase I City Wells Phase I City Wells

20 ASR Phase I  Recharge & Recovery Capacity of 10 MGD  ASR Facilities  7 MGD River Intake  SWTP (7 MGD)  15 miles of pipeline  3 Diversion Wells  4 ASR Wells  2 Recharge Basins  Recharge & Recovery Capacity of 10 MGD  ASR Facilities  7 MGD River Intake  SWTP (7 MGD)  15 miles of pipeline  3 Diversion Wells  4 ASR Wells  2 Recharge Basins

21 ASR Phase I  Award Winning Project  Has established the hydraulic barrier  Award Winning Project  Has established the hydraulic barrier

22 ASR Phase II  Recharge & Recovery Capacity of 30 MGD  ASR Facilities  River Intake (60 MGD, Equipped for 30 MGD)  SWTP (30 MGD)  31 ASR Wells  Recharge Basin (~ 7 MGD)  31 miles of Pipelines  Vital Statistics  950 Sheets of Design  43 Permits Obtained  51 Easements Acquired  Recharge & Recovery Capacity of 30 MGD  ASR Facilities  River Intake (60 MGD, Equipped for 30 MGD)  SWTP (30 MGD)  31 ASR Wells  Recharge Basin (~ 7 MGD)  31 miles of Pipelines  Vital Statistics  950 Sheets of Design  43 Permits Obtained  51 Easements Acquired

23 ASR Phase II  ASR Phase II SWTP Treatment Process  Pre-Sedimentation & Ultrafiltration Membranes to remove suspended solids  Advanced Oxidation Processes (AOP) for Virus Inactivation & Destruction of Atrazine (and other pesticides)  ASR Phase II SWTP Treatment Process  Pre-Sedimentation & Ultrafiltration Membranes to remove suspended solids  Advanced Oxidation Processes (AOP) for Virus Inactivation & Destruction of Atrazine (and other pesticides)

24 Intake Site

25 Intake Structure Model 1:5 Scale

26 ASR Phase II SWTP

27 Regulatory Controls  First ASR project in Kansas – NO regulations existed to administer  Project includes restrictions on flow conditions in the river.  Class V permit from KDHE controls water quality to wells and basins.  Establishment of index well network.  Installation of numerous monitoring wells near diversion wells and recharge sites.  First ASR project in Kansas – NO regulations existed to administer  Project includes restrictions on flow conditions in the river.  Class V permit from KDHE controls water quality to wells and basins.  Establishment of index well network.  Installation of numerous monitoring wells near diversion wells and recharge sites.

28 Diversion Wells  Appropriations require at least 56 cfs in the river during irrigation season  Drawdown less than 10 feet 660 feet from well  Recovery to regional water level in less than 7 days  No impairment to other groundwater users  Appropriations require at least 56 cfs in the river during irrigation season  Drawdown less than 10 feet 660 feet from well  Recovery to regional water level in less than 7 days  No impairment to other groundwater users

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30 ASR Phase II – Geochemical Evaluation  Evaluate Mixing of Surface Water, Groundwater and Equus Beds Aquifer Matrix  Preliminary Predictions:  Pyrite (if present) within the aquifer matrix, may oxidize releasing arsenic  Iron will also precipitate and form a rust coating on matrix  Arsenic is absorbed onto rust  Evaluate Mixing of Surface Water, Groundwater and Equus Beds Aquifer Matrix  Preliminary Predictions:  Pyrite (if present) within the aquifer matrix, may oxidize releasing arsenic  Iron will also precipitate and form a rust coating on matrix  Arsenic is absorbed onto rust

31 ASR Phase II – Geochemical Evaluation: Pilot Study Filters

32 Recharge Quantity  2006 – No recharge because of low flows in river.  2007- 369 million gallons recharged.  2008 – 319 million gallons recharged  2009 – 170 million gallons recharged  2010 – 89 million gallons recharged  2011 – No recharge – low flow and construction issues  2012 – 33 million recharged to date To date – 978 million gallons (over 3,000 AF) has been recharged.  2006 – No recharge because of low flows in river.  2007- 369 million gallons recharged.  2008 – 319 million gallons recharged  2009 – 170 million gallons recharged  2010 – 89 million gallons recharged  2011 – No recharge – low flow and construction issues  2012 – 33 million recharged to date To date – 978 million gallons (over 3,000 AF) has been recharged.

33 ASR Phases III & IV  Recharge & Recovery Capacity of 60 MGD  ASR Facilities  To Be Determined  Likely to consist of Diversion Wells and/or additional diversion capacity at Phase II River Intake  Possible expansion of Phase II SWTP  Recharge & Recovery Capacity of 60 MGD  ASR Facilities  To Be Determined  Likely to consist of Diversion Wells and/or additional diversion capacity at Phase II River Intake  Possible expansion of Phase II SWTP

34 Questions?


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