Groundwater in Clarkdale today and in the future al Consulting cher - - PowerPoint PPT Presentation

groundwater in clarkdale today and in the future
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Groundwater in Clarkdale today and in the future al Consulting cher - - PowerPoint PPT Presentation

Groundwater in Clarkdale today and in the future al Consulting cher Hydrologica La 1 Water Resources Management Program Water Resources Management Program Hydrologic Problem Statement Regional to Clarkdale Specific Model al Consulting


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SLIDE 1

Groundwater in Clarkdale— today and in the future

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SLIDE 2

Water Resources Management Program Water Resources Management Program

Hydrologic Problem Statement Regional to Clarkdale‐Specific Model

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Options for Clarkdale’s Water

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Management Program

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SLIDE 3

How Does Pumping Groundwater Affect the Verde River?

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SLIDE 4

Natural Conditions: RECHARGE = DISCHARGE

Pumping = Aquifer Storage + Capture AQUIFER AQUIFER RECHARGE DISCHARGE

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Capture: I d RECHARGE D d DISCHARGE

Baseflow and Evapotranspiration (ET)

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Increased RECHARGE + Decreased DISCHARGE

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SLIDE 5

Effects of Pumping May Continue for a Long, Long Time... Even After Pumping Stops

Si l t d Ch i St C t f 2005

Simulated Baseflow Capture Due to Pumping in

Even After Pumping Stops

1200 1400 1600 8.00 10.00

Simulated Change in Stream Capture from 2005 Pumping at Fort Huachuca

Simulated Baseflow Capture Due to Pumping in a Distant Well in a Single Year (2005)

600 800 1000 1200 2.00 4.00 6.00 Pumping (AFY) ream Capture (AFY)

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200 400 ‐2.00 0.00 Str

2032

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Year Pumping Stream Capture

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SLIDE 6

GROUNDWATER MODELS

Hydrologic Tools for Understanding Water Systems

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GROUNDWATER MODELS

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SLIDE 7

MODEL: A Description or Analogy Used to Help Visualize Something that Cannot be Directly Observed Something that Cannot be Directly Observed.

‐‐ Merriam‐Webster Dictionary definition no. 11 al Consulting cher Hydrologic La 7

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SLIDE 8

GROUNDWATER MODEL: A Computer Program that Uses Flow Equations to Make Sense of Uses Flow Equations to Make Sense of a Complex Natural System.

Numerical Model

Evaporation

OUTPUT

S

Pumping, Stream Diversions, Groundwater Conditions, Baseflow, E i

INPUT OUTPUT

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Evaporative Demand Evaporative Consumption

Flow Equations

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Flow Equations

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SLIDE 9

Why Use a Groundwater Model? Why Use a Groundwater Model?

  • To test the outcome of actions that can’t

To test the outcome of actions that can t easily be tested in real life:

– future changes in pumping – future changes in pumping – new wells changing climate – changing climate – new recharge projects

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SLIDE 10

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SLIDE 11

What We Know About Our System

Geology Streamflow Evaporative Demand

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Groundwater Levels Pumping Evaporative Demand

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Source: SIR 2013‐5029

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SLIDE 12

Source: SIR 2013‐5029 al Consulting cher Hydrologica Source: SIR 2010‐5180 La Source: SIR 2010 5180 12

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SLIDE 13

MODELING THE CLARKDALE AREA

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MODELING THE CLARKDALE AREA

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SLIDE 14

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1km grid squares

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SLIDE 15

Future Simulation (2006 to 2076) Future Simulation (2006 to 2076)

  • No Change in Pumping from 2006‐2076*

No Change in Pumping from 2006 2076

* Clarkdale pumping updated 2006‐2012, then constant to 2076.

  • Repeat Historic (1910‐1970) Recharge 2016 to

2076

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SLIDE 16

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SLIDE 17

Simulated Recharge Factor

1.6 1.8 2

(Relative to 1940)

repeat 1910‐1970 pattern

0 6 0.8 1 1.2 1.4 1910‐2006 AVG 1910‐2076 AVG

9% Difference al Consulting

0.2 0.4 0.6

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SLIDE 18

Simulated Heads and Flow Paths – 1910 (Predevelopment)

contour interval = 50 ft.

ft amsl

5900 5750 5500 5250 5000

3800

4750 4500 4250 4000 3750 3500 3250 3000

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SLIDE 19

Simulated Heads and Flow Paths – 2006

contour interval = 50 ft.

ft amsl

5900 5750 5500 5250 5000

3800

4750 4500 4250 4000 3750 3500 3250 3000

Haskell Springs/SW Clarkdale Area

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SLIDE 20

Simulated Heads and Flow Paths – 2030

contour interval = 50 ft.

ft amsl

5900 5750 5500 5250 5000

3800

4750 4500 4250 4000 3750 3500 3250 3000

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SLIDE 21

Simulated Heads and Flow Paths – 2076

contour interval = 50 ft. 3800

ft amsl

5900 5750 5500 5250 5000 4750 4500 4250 4000 3750 3500 3250

5620 5640 5660 5680 5700 5720 5740 5760 Feet

Head in Aquifer ‐ Mingus Mountain

3500

Head in Aquifer ‐ Clarkdale Town Hall

3000

5560 5580 5600 5620 Year 3300 3320 3340 3360 3380 3400 3420 3440 3460 3480 3500 Feet

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3300 Year

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SLIDE 22

Simulated Head Change 1910 to 1970

contour interval = 10 ft.

f 150 110 70 30 ‐10 50 feet ‐50 ‐90 ‐120 ‐160 ‐200 ‐240 ‐280 ‐320

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SLIDE 23

Simulated Head Change 1910 to 2006

contour interval = 10 ft.

150 110 70 30 ‐10 feet ‐50 ‐90 ‐120 ‐160 ‐200 ‐240 280 ‐280 ‐320 Jerome Wastewater Treatment Facility

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Simulated Head Change 1910 to 2030

contour interval = 10 ft.

150 110 70 30 ‐10 feet ‐50 ‐90 ‐120 ‐160 ‐200 ‐240 280 ‐280 ‐320

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SLIDE 25

Simulated Head Change 1910 to 2076

contour interval = 10 ft.

150 110 70 30 ‐10 feet ‐50 ‐90 ‐120 ‐160 ‐200 ‐240 280 ‐280 ‐320

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Simulated Change in Baseflow ‐ 1910 to 2006

contour interval = 1 cubic‐foot per second (cfs)

‐9.6 cfs (‐8%) [Q2006=108 cfs]

cfs ‐7 ‐14 ‐21 ‐28 ‐35 ‐42 ‐49 49 ‐56 ‐63 ‐70 ‐77 ‐84

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Simulated Change in Baseflow ‐ 1910 to 2030

contour interval = 1 cubic‐foot per second (cfs)

‐15 cfs (‐13%) [Q2030=103 cfs]

cfs ‐7 ‐14 ‐21 ‐28 ‐35 ‐42 ‐49

1

49 ‐56 ‐63 ‐70 ‐77 ‐84

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SLIDE 28

Simulated Change in Baseflow ‐ 1910 to 2076

contour interval = 1 cubic‐foot per second (cfs)

‐21 cfs (‐18%) [Q2076=97 cfs]

cfs ‐7 ‐14 ‐21 ‐28 ‐35 ‐42 ‐49

1

49 ‐56 ‐63 ‐70 ‐77 ‐84

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SLIDE 29

Simulated Baseflow

250 300 350 400 cfs)

Simulated Baseflow

Clarkdale GS

3 4

50 100 150 200 250 Baseflow (c Clarkdale GS Tuzigoot Bridge 1 Mile Below Tuzigoot Bridge 2 Miles Above Oak Cr Confluence

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1900 1950 2000 2050 2100 Year

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Simulated Recharge Factor (Relative to 1940) and Simulated % Change in Baseflow (Relative to 1910)

0% 5% 1.6 1.8 2 Recharge Factor Repeat Historic ‐15% ‐10% ‐5% 0.8 1 1.2 1.4 Recharge Factor ‐ Repeat Historic Pattern After 2016 1910‐2006 AVG Recharge Factor 1910‐2076 AVGRecharge Factor Recharge Factor Baseflow % Ch

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‐25% ‐20% 15% 0.2 0.4 0.6 1910 2076 AVG Recharge Factor % Change in Baseflow ange

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Years

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SLIDE 31

Take‐Aways Take Aways

  • Baseflows in the middle Verde have declined

Baseflows in the middle Verde have declined by about 8% over the past century and are likely to decline at least 10% more by 2076.

  • Baseflows are sensitive to recharge and

pumping, but pumping impacts will become more significant in the future (even without increased pumping).

  • Haskell Springs/SW Clarkdale area is

hydrologically sensitive.

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SLIDE 32

Thank you! Thank you!

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