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Groundwater Hydrology 101
Ken Rainwater, Ph.D., P.E., BCEE, D.WRE,
CFM
Department of Civil, Environmental, and
Construction Engineering
Texas Tech University 1
Subsurface Layer Terms
 Aquifer – geologic layer that holds water
and allows flow to wells
 Unconfined – bounded below only
 Confined – bounded above and below
 Aquitard – layer with low permeability
that allows very little flow
 Aquiclude – layer with no permeability
2
3
Aquifer Parameters
 Hydraulic conductivity – K (L/t)
 Measure of permeability of geologic
material to water
 Porosity – n
 Void volume divided by total volume
 Storage coefficient – S or Sy
 Amount of water released per unit decline
in head (larger for unconfined aquifer)
 Saturated thickness – b (L) 4
Hydraulic Head
 Unconfined – water table
 Aquifer base may be datum
 Saturated thickness changes
 Confined – well water level
 Datum is usually sea level
 Saturated thickness constant
5
elevationheadpressureh +=
http://pubs.usgs.gov/circ/circ1217/html/boxa.html
Head Gradient
6
-0.0057
m350
m2-
dx
dh
==
http://studentweb.usq.edu.au/home/w0028223/webdes/html/gwatere.htm
x
Darcy’s Law
7
alsodirectionszy,incomponentsVelocity
directionxintyconductivihydraulicK
(L)directionhorizontalx
(L/t)poresinvelocityactualv
dx
dh
n
K
v
x
x
x
x
−=
=
=
−=
Well
Drawdown
8
 Pump lowers
head at pumping
well
 3-D head gradient
to pumping well
 “Drawdown cone”
Better Aquifer Definition
 Geologic stratum or layer that
 holds groundwater within saturated thickness, b
 has sufficient hydraulic conductivity, K, for flow
 has enough transmissivity, T = Kb, for useful
production at pumping wells
9
Regional Aquifer Flow
Moderate Pumping
Long-term Depletion
Projections of Aquifer Life
 Some aquifers are being mined
 Withdrawals exceed recharge, lateral flow
 Groundwater owners choose to pump
 Center pivot requirements

400-1200 gpm for quarter-mile

1200-2500 gpm for half-mile
 Municipal supply requirements
 When is aquifer too thin? 30 ft, 50 ft?
13
Estimating Recharge
 Historical regional estimates
 Model calibrations
 Difficult under irrigated lands
 Must know withdrawals
 Irrigation return flow
 Geochemical estimates
14
Long-term Drawdown
15
 Effects of single pumping well
 Initial saturated thickness, ho
to
Q
ho
Long-term Drawdown
16
 Effects of single pumping well
 Initial saturated thickness, ho
 Transient drawdown increases
to
t1
Q
ho
to
t1
t2
Q
ho
ro
Long-term Drawdown
17
 Effects of single pumping well
 Stabilizes within radius of influence, ro
 Can “break suction” if drawdown > ho
Drawdown Calculation
 Equilibrium for unconfined aquifer
 Drawdown, s
 Pumping well radius, rw
 Flow rate, Q
 Hydraulic conductivity, K
 ro, ho
18
( )
21
w
o2
oow
r
r
ln
πK
Q
hhrs 











−−=
Simplifying Assumptions
 Horizontal aquifer base
 Initially horizontal water table
 Homogeneous K, specific yield, Sy
 Constant Q
 No aquifer boundaries, recharge
 Single value of ro
19
Minimum ho for Q, K Values
 Assume ro = 1000 ft, rw = 1 ft
20
0
50
100
150
200
250
0 10 20 30 40 50 60
MinimumSaturatedThickness(ft)
Hydraulic Conductivity (ft/d)
500 gpm
350 gpm
240 gpm
100 gpm
Actual Conditions
 Aquifer base topography
 Water table gradient
 More precise shape with capture zone
analysis
 Heterogeneous K, specific yield, Sy
 Multiple wells
 Overlapping drawdown
 Different times of operation
21
More Complex Situations
 Computer modeling required
 Limited by size of simulated cells and
time steps
 Calibration challenges
22
Actions for Well Owner
 Understand aquifer behavior
 Pump tests for aquifer parameters
 Observe seasonal behavior
 Selection of irrigation rates and timing
 Crop choices, input costs
 How many wells are needed to provide
the demand?
 Costs of new wells, pump replacements
23
Groundwater Issues
 Water quality variations
 Fresh, brackish
 Arsenic, fluoride, perchlorate, others
 Recharge rate determines renewability
 Fast (Edwards)
 Slow (Ogallala)
 Withdrawal > Recharge = Depletion
Nine Major Aquifers
21 Minor Aquifers
GCD Challenges
 Education of Groundwater Owners
 Well interference, depletion, pumping distribution
 Changes in water stored
 Best practices for use and conservation
 Water marketing (agricultural vs. other users)
 GCDs share aquifers
 Concern for future conditions, regional planning
 Recharge, surface water interaction uncertainties
 Some areas not currently included in GCDs
 Groundwater management areas
Conservation District Actions
 Well permit requirements
 Well spacing (production/area)
 Annual limits on saturated thickness
change
 Production monitoring and reporting
30
Opportunities for Groundwater
Scientists and Engineers
 Improve quantitative aquifer descriptions
 Water in storage
 Hydraulic parameters  well capacities
 Regional and local flow models
 Water quality variations
 Inform GCD rule-making process
 Stewardship of shared resources
31

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2018 Leadership Training_Groundwater Hydrology 101

  • 1. Groundwater Hydrology 101 Ken Rainwater, Ph.D., P.E., BCEE, D.WRE, CFM Department of Civil, Environmental, and Construction Engineering Texas Tech University 1
  • 2. Subsurface Layer Terms  Aquifer – geologic layer that holds water and allows flow to wells  Unconfined – bounded below only  Confined – bounded above and below  Aquitard – layer with low permeability that allows very little flow  Aquiclude – layer with no permeability 2
  • 3. 3
  • 4. Aquifer Parameters  Hydraulic conductivity – K (L/t)  Measure of permeability of geologic material to water  Porosity – n  Void volume divided by total volume  Storage coefficient – S or Sy  Amount of water released per unit decline in head (larger for unconfined aquifer)  Saturated thickness – b (L) 4
  • 5. Hydraulic Head  Unconfined – water table  Aquifer base may be datum  Saturated thickness changes  Confined – well water level  Datum is usually sea level  Saturated thickness constant 5 elevationheadpressureh += http://pubs.usgs.gov/circ/circ1217/html/boxa.html
  • 8. Well Drawdown 8  Pump lowers head at pumping well  3-D head gradient to pumping well  “Drawdown cone”
  • 9. Better Aquifer Definition  Geologic stratum or layer that  holds groundwater within saturated thickness, b  has sufficient hydraulic conductivity, K, for flow  has enough transmissivity, T = Kb, for useful production at pumping wells 9
  • 13. Projections of Aquifer Life  Some aquifers are being mined  Withdrawals exceed recharge, lateral flow  Groundwater owners choose to pump  Center pivot requirements  400-1200 gpm for quarter-mile  1200-2500 gpm for half-mile  Municipal supply requirements  When is aquifer too thin? 30 ft, 50 ft? 13
  • 14. Estimating Recharge  Historical regional estimates  Model calibrations  Difficult under irrigated lands  Must know withdrawals  Irrigation return flow  Geochemical estimates 14
  • 15. Long-term Drawdown 15  Effects of single pumping well  Initial saturated thickness, ho to Q ho
  • 16. Long-term Drawdown 16  Effects of single pumping well  Initial saturated thickness, ho  Transient drawdown increases to t1 Q ho
  • 17. to t1 t2 Q ho ro Long-term Drawdown 17  Effects of single pumping well  Stabilizes within radius of influence, ro  Can “break suction” if drawdown > ho
  • 18. Drawdown Calculation  Equilibrium for unconfined aquifer  Drawdown, s  Pumping well radius, rw  Flow rate, Q  Hydraulic conductivity, K  ro, ho 18 ( ) 21 w o2 oow r r ln πK Q hhrs             −−=
  • 19. Simplifying Assumptions  Horizontal aquifer base  Initially horizontal water table  Homogeneous K, specific yield, Sy  Constant Q  No aquifer boundaries, recharge  Single value of ro 19
  • 20. Minimum ho for Q, K Values  Assume ro = 1000 ft, rw = 1 ft 20 0 50 100 150 200 250 0 10 20 30 40 50 60 MinimumSaturatedThickness(ft) Hydraulic Conductivity (ft/d) 500 gpm 350 gpm 240 gpm 100 gpm
  • 21. Actual Conditions  Aquifer base topography  Water table gradient  More precise shape with capture zone analysis  Heterogeneous K, specific yield, Sy  Multiple wells  Overlapping drawdown  Different times of operation 21
  • 22. More Complex Situations  Computer modeling required  Limited by size of simulated cells and time steps  Calibration challenges 22
  • 23. Actions for Well Owner  Understand aquifer behavior  Pump tests for aquifer parameters  Observe seasonal behavior  Selection of irrigation rates and timing  Crop choices, input costs  How many wells are needed to provide the demand?  Costs of new wells, pump replacements 23
  • 24. Groundwater Issues  Water quality variations  Fresh, brackish  Arsenic, fluoride, perchlorate, others  Recharge rate determines renewability  Fast (Edwards)  Slow (Ogallala)  Withdrawal > Recharge = Depletion
  • 27.
  • 28. GCD Challenges  Education of Groundwater Owners  Well interference, depletion, pumping distribution  Changes in water stored  Best practices for use and conservation  Water marketing (agricultural vs. other users)  GCDs share aquifers  Concern for future conditions, regional planning  Recharge, surface water interaction uncertainties  Some areas not currently included in GCDs  Groundwater management areas
  • 29.
  • 30. Conservation District Actions  Well permit requirements  Well spacing (production/area)  Annual limits on saturated thickness change  Production monitoring and reporting 30
  • 31. Opportunities for Groundwater Scientists and Engineers  Improve quantitative aquifer descriptions  Water in storage  Hydraulic parameters  well capacities  Regional and local flow models  Water quality variations  Inform GCD rule-making process  Stewardship of shared resources 31

Editor's Notes

  1. First GW District established in 1951 Today 89 confirmed or provisional (5) GW Districts Manage appx. 80-90% of GW produced in Texas