groundwater profiling for selective extraction: steve walden and debra cerda

29
Selective Extraction Case Study: Lee County WSC Presented by Debra Cerda and Steve Walden

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TAGD October 2013 Quarterly Meeting

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Page 1: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Selective Extraction Case Study:

Lee County WSC

Presented byDebra Cerda and

Steve Walden

Page 2: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Questions

• What have I been missing in my well?– Variable flow– Variable quality

• What is selective extraction?• How can it be applied to

solve water quality issues?

Page 3: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

• Visual• Depth-dependent flow• Depth-dependent quality• Ambient mixing

Miniaturized Down-hole Diagnostics

Page 4: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

• Represents normal working conditions

• Use the good water, leave the bad in the ground

Miniaturized Down-hole Diagnostics

Page 5: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Straddle Packer / Pump Assemblies for Zone Isolation Testing

Dynamic Flow and Chemistry Profiling

Flow

Chemistry

Packer

Pump

Vs.

Comparisons of Technology for Groundwater Profiling

Page 6: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

As & NO3 ?

As & NO3?

As & NO3 ?

As & NO3 ?

Production Well XYZZone Test #1

Zone Test #2

Zone Test #3

Packer

Pump

1,000 GPMAs = 9 - 12 PPB

NO3 = 49 – 53 PPM Zone Test #4

Disadvantages of Packer Testing

• Time – can take weeks

• Effort and impact

• Cost-prohibitive

• Data quality – suction on a well zone not indicative of normal operation conditions

Page 7: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

High Tech, Low Cost Technology

• U.S. Geological Survey Developed Tracer-Pulse Profiling Method

• BESST Inc. holds exclusive U.S. license

Tracer system deployed down hole with existing pump in place

Page 8: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

What data can be collected?

Dynamic profiling breaks down flow and quality into slices along the length of production zones

Page 9: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Miniaturized Tools

• Apply easily attainable z-axis data for

three-dimensional view

• Minimally invasive downhole diagnostics

• To date, BESST has profiled over 400

wells for cost savings of ~$300 M

– Reduced or avoided treatment

5 PPB As 10 PPB As 50 PPB As

100 GPM ZOI300 GPM ZOI

700 GPM ZOI

Page 10: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Dynamic Flow and Water Quality Profiling

• Fairly easy to implement– Existing pump or test equivalent

close to normal operations– In-line flowmeter– Sample tap– Water discharge and disposal

option– Access pipe if limited annular

space

Page 11: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Access Pipes

Page 12: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda
Page 13: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Dye Injection Scheme

Page 14: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Q1

Q2

Q3

Q4

Q5

T1

T2

T3

T4

?

?

?

?

Incremental Flow Contribution

Incremental Flow Contribution

Incremental Flow Contribution

Cumulative Flow Contribution

Cumulative Flow Contribution

Cumulative Flow Contribution

Cumulative Flow Contribution

Cumulative Flow Contribution

Profiling is a visual, volumetric and chemical mass accounting system

Page 15: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Dynamic Flow Profile Under Steady State

Draw-Down

Fluorometer

Flow From Well To Fluorometer

Flow From Fluorometer To Waste

1,900 GPM

406080

100120140160180200220240260280300320340360380400

Dye Injection Shot Points

Ft. Below Ground Surface

Water Sampling Spool

Dye Injection Spool

Explanation of Dye Injection Process For Dynamic Flow Profiling In Production Wells

Cumulative Flow Slices (CFS)

Page 16: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Flow Equation

The basic equation used for calculating flow between two points is:

Q = vA where v = (d2-d1)/(t2-t1)

Q: flowA: cross sectional area of well

A = π(r12-r2

2) if above intake

A = πr12 if below intake

v: velocity

d2: injection depth #2d1: injection depth #1t2: return time of d2

t1: return time of d1

r1: inner radius of well casingr2: outer radius of pump column

Page 17: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Recent Gulf Coast Aquifer Brackish Well Flow Profile

Page 18: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda
Page 19: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Dynamic Groundwater Sampling Under Steady

State Draw-Down

406080

100120140160180200220240260280300320340360380400

Groundwater Sampling Points

Ft. Below Ground Surface

Ca1

Ca2

Ca3

Ca4

Ca5

Ca6

Ca7

Ca8

Ca9

Ca10

Ca11

Ca12

Ca13

Ca14

Ca15

Ca16

Ca17

Cumulative

Concentration

Explanation of Basic Mass Balance Calculations

Slices of Water Quality

Page 20: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Contaminant Concentration Calculation

Average Cumulative Contaminant Concentration Calculation can be defined as:

Ca1= (Q1C1 – Q2C2)/Q1- Q2

Incremental Average Contaminant Concentration between two imaginary flow planes within the well can be expressed as:

Ca1- Ca2

Page 21: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Case Study: Groundwater in Lee County, Texas

Lee County Water Supply Corporation (LCWSC): • Serves 3536 connections and over

10K customers• Recipient of numerous industry

awards, including TCEQ Superior rating

• Experienced water quality issues from Country Corners well site, primarily: color, turbidity, and iron

• In 2012, contracted BESST Inc. to locate zones of poor water quality

Page 22: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

8” Liner

1452’Top of Liner

1554’

1734’

1840’

1646’

1664’

1672’

1636’

1723’

Color

Lithology

Hard Shale & Rocks

Broken Rocks & Fine SandShale & Rocks

Coarse Light Gray Sand & Rocks

Hard Shale

Hard Sand & Shale Streaks

Hard Shale & Rocks

1400-1500

1554-1600

1600-1636

1646-1664

1672-1723

1734-1755

1755-1820

below 1820

0 20 40 60 80 100 120

0

110

0

NC

26

60

20

100

Dynamic Chemical Mass Balance Profile

Color Units

Sam

plin

g In

terv

al (ft

. bgs

)

High Color correlates with Shale formations

High Color correlates with Shale formations

Lower Color section correlates with Coarse Light Gray Sand & Rocks

~20% of flow

~60% of flow

~80% combined

Page 23: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

23

Change Pumping Rate

Change Pump Intake Location and/or Diameter

Packers, Sleeves and Engineered Suctions

Lower or Raise Pump (Intake)

Attach Suction Pipe To Bottom of Pump

Higher Pumping Rate Vertically Shifts Flow Contribution Downward Inside Well – Away From Pump IntakeLower Pumping Rate Vertically Shifts Flow Contribution Upward Inside Well – Towards Pump Intake

Change Well Diameter and/or Length DiameterInstall Liner

Backfill Bottom of Well

How Do We Hydraulically Manipulate Groundwater Production Wells?

Well RehabilitationRemove mineral encrustations and biofilm on Well Screen

Well Reconstruction / Re-Engineering

Page 24: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Selective Extraction at Work: Block off zones of poor water quality

8” Pump Column

1452’Top of Liner

1554’

1734’

460’

1840’

1646’

1664’

1672’

1636’

13.25” Inner Casing

Pump

Intake

8” Liner

1723’

Grout deepest screen

Sleeve off shallow screen

Potential Solutions:

Page 25: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Before modification (avg) After modification0

0.1

0.2

0.3

0.4

0.5

0.6

0.501

0.05

Total Iron (mg/L)

Total Iron (mg/L)

Less than detect = 100% reduction

<

Page 26: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda
Page 27: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda
Page 28: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Feedback from LCWSC

“Sometimes you have to look at the whole picture, and take a chance on new science or methods. Sticking our head in the dirt and never trying anything new will not benefit us as a water provider” -- Wade Dane, LCWSC Assistant General Manager

Page 29: Groundwater Profiling for Selective Extraction: Steve Walden and Debra Cerda

Questions?

Debra Cerda-BESST Inc. Director of Technical Sales and Licensing, Texas

[email protected] cell

---------------------------Steven Walden

[email protected]