hydrogeology - energy.gov · 2012-02-08 · hydrogeology 101 the objective is to obtain a better...
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Hydrogeology 101
W. Richard Laton, Ph.D., PG, CPGAssociate Professor of HydrogeologyCalifornia State University, FullertonDepartment of Geological Sciences
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Hydrogeology 101
The objective is to obtain a better understanding of the principles of groundwater, hydrologic cycle and water budgets. The lecture will also cover various types of aquifers and general groundwater quality.
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Objective
To understand Basic definitions Hydrologic Cycle Groundwater Aquifers How water flows Water Budgets Wells Water Quality Contamination Investigation Tools
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Definitions
Water on Earth Hydrologic Cycle Meteorology
weather Hydrology
Surface water Hydrogeology
Groundwater
Unsaturated Zone Vadose Zone
Aquifers Water Table Unconfined Confined
Darcy’s Law Safe Yield Water Chemistry
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Distribution of H2O
on Earth
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Hydrologic Cycle
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Meteorology
Climate Precipitation
Rain Snow
Temperature Other factors
Location Altitude
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Rain Shadow Deserts
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Surface Water
Ocean, Lake, Pond River, Stream Spring, Wetland
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Surface Water Flow
Discharge Baseflow Flood Stage Gaining Stream Losing Stream
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Gaining - Losing
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Groundwater
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Water contained in spaces within soil and bedrock
Less than 1% of all H2O on Earth
40 times more abundant than water found in lakes and streams
Groundwater
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zone of aeration: portion of soil and rock near the surface in which open spaces are filled primarily with air (a.k.avadose zone, unsaturated zone)
saturated zone: zone in which pore spaces are filled with water
water table: boundary between zone of aeration and saturated zone
Groundwater terms
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aquifer: body of rock that is sufficiently water permeable to yield economically significant quantities to wells and springs
Unconfined vs Confined aquitard: body of rock that retards but does not prevent flow of water to or from an adjacent aquifer
aquiclude: body of relatively impermeable rock that is capable of absorbing water slowly but does not transmit it rapidly enough to supply a well or spring
More groundwater terms
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Impacts of Faults on Groundwater Flow
Barriers to Groundwater Flow
Conduits of Flow
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Perched Water Table
Confined Aquifer
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Aquifers
Vadose Zone
Unconfined Aquifer
Aquitard
Confined Aquifer
Water Table
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Isotropy/AnisotropyHomogeneous/Heterogeneous
Isotropy – The condition in which hydraulic properties of the aquifer are equal in all directions.
Anisotropy – The condition under which one or more of the hydraulic properties of an aquifer vary according to the direction of flow.
Homogeneous – A geologic unit that has the same properties at all locations.
Heterogeneous – Hydraulic properties vary spatially.
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porosity: portion of volume of a material that consists of open spaces
permeability: measure of the speed at which fluid can travel through a porous medium
Imagine two vertical pipes, one filled with gravel, one with sand. Out of which one will the water flow faster?
Soils and rocks are not completely solid
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Poorly‐sorted Sandstone
Well‐sorted Sandstone
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Fractured / Unfractured Shale
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Porosity and PermeabilityPrimary and Secondary Porosity
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Hydraulic ConductivityTransmissivity
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Slow to very slow (depending on permeability)
Generally within the range of 10 to 100 cm per day
Rates of groundwater movement
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Q = discharge (m3/sec)A = cross-sectional area (m2)K = coefficient of permeability (m/sec)h1 = beginning height (m)h2 = ending height (m)l = length of flow (m)
Darcy’s Law
Q = AK(h1– h2)l
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Groundwater Movement in Temperate Regions
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Wet Period
Dry Period
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In = Out ± change in storage
Simple in concept Data driven Difficult in practice
Water Budgets
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How and where is the water coming from; Recharge Return flow
How and where is the water going; Pumping Surface water Evapotranspiration
Assumptions – Water Budget
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Variables
Inputs Precipitation Return flow Overland Flow
Streams Springs
Groundwater
Outputs Pumping Evapotranspiration Overland Flow Groundwater
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Example Water Budget
Annual Average(acre-ft) DWR [1967] Goodrich [1978]1 Brose [1987]
Total Input 1,744 1,050 1,750
Total Output 4,640 10,145 7,725
Total Water Budget -2,896 -9,095 -6,475
Annual Average (acre-ft) DWR [1967] Goodrich [1978]2 Brose [1987]
Surface Inflow 1,0501 1,0501 1,0501
Subsurface Inflow - - -
Precipitation 694 - 700
Imported Water - - -
Total 1,744 1,050 1,750
Annual Average (acre-ft) DWR [1967] Goodrich [1978]1 Brose [1987]Stamos and Predmore
[1995]
Surface Outflow - - - -
Subsurface Outflow 100 100 500 300 - 600
Consumptive Use 4,540 10,045 7,725 -
Total 4,640 10,145 8,225 -
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The amount of naturally occurring groundwater that can be economically and legally withdrawn from an aquifer on a sustained basis without impairing the native groundwater quality or creating an undesirable effect such as environmental damage. It cannot exceed the increase in recharge or leakage from adjacent strata plus the reduction in discharge, which is due to the decline in head caused by pumping.
C.W. Fetter, 1994.
Safe Yield (sustainability)
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Groundwater Hydrographs
Common Typically easy to interpret
Este Hydrologic Sub-basin(05N01E17D01)
1954-2002
50
70
90
110
130
150
1701954 1957 1960 1963 1966 1969 1972 1975 1978 1981 1984 1987 1990 1993 1996 1999 2002
Measure Date
Feet
Bel
ow G
roun
d Su
rfac
e
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Long-term monitoring Frequent monitoring Quality data you can trust
Assumptions - Hydrographs
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0
50
100
150
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4001
6
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51
Dec-49
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Dec-04
Dep
th to
Gro
undw
ater
(Fee
t)
Prec
ipita
tion
(Inch
es)
Este Hydrologic Sub-basinLucerne Valley Sub-Basin
Big Bear Lake Big Bear Dam Lake Arrowhead 06N01W27B001S 06N01W35A001S05N01E06C001S 05N01W01C001S 05N01W01L001S 05N01W01R003S 05N01E08N004S05N01E17D001S 05N01E20F001S 05N01E27H001S 05N01W25G001S 05N01W36F001S
What do the hydrographs say?
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0
50
100
150
200
250
300
350
4001
6
11
16
21
26
31
36
41
46
51
Jan-94M
ay-94Jul-94O
ct-94Jan-95A
pr-95Jul-95O
ct-95Jan-96A
pr-96Jul-96O
ct-96Jan-97A
pr-97Jul-97O
ct-97Jan-98A
pr-98Jul-98O
ct-98Jan-99A
pr-99Jul-99O
ct-99D
ec-99M
ar-00Jun-00S
ep-00D
ec-00M
ar-01Jun-01S
ep-01D
ec-01M
ar-02Jun-02S
ep-02D
ec-02M
ar-03Jun-03S
ep-03D
ec-03M
ar-04Jun-04S
ep-04D
ec-04
Dep
th to
Gro
undw
ater
(Fee
t)
Prec
ipita
tion
(Inch
es)
Este Hydrologic Sub-basinLucerne Valley Sub-Basin
Big Bear Lake Big Bear Dam Lake Arrowhead 06N01W27B001S 06N01W35A001S 05N01E06C001S
05N01W01C001S 05N01W01L001S 05N01W01R003S 05N01E08N004S 05N01E17D001S 05N01E20F001S
05N01E27H001S 05N01W25G001S 05N01W36F001S 04N01E06R001S 04N01E05P002S 04N01E12P001S
04N01W13R001S 04N01E23K001S 04N01E13M001S
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Hydrographs – groundwater levels drive the analysis Decline in water levels Increased water levels No change
Balancing act
Analysis
z1
z2
z3
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Groundwater and Wells
Drawdown Cone of depression Capture zone
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Groundwater Withdrawal
Potable (municipal and private) Irrigation Industrial
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Drawdown Due to Pumping
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Water in aquifers is replenished primarily by infiltration of surface water (groundwater recharge).
Groundwater flows from areas of high pressure (or hydraulic head) to areas of low pressure. In unconfined aquifers, hydraulic head is given by the height of the water table above some reference level.
Left to itself, groundwater flow may intercept a surface water body, and flow into that body (natural groundwater discharge, Q).
Alternatively, it may be removed through wells for human consumption (artificial groundwater discharge).
dischargeto stream
impermeable layer
flow lines
water table
dischargeto well
Q1
Q2
Water flowing underground
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Mans Interaction
Groundwater Withdrawal Pollutants/Contamination
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James W. Borchers/USGS
Fissures, Depressions and Land SubsidenceCaused by Over Pumping
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Water quality can be thought of as a measure of the suitability of water for a particular use based on selected physical, chemical, and biological characteristics. To determine water quality, scientist’s first measure and analyze characteristics of the water such as temperature, dissolved mineral content, and number of bacteria. Selected characteristics are then compared to numeric standards and guidelines to decide if the water is suitable for a particular use.
Some aspects of water quality can be determined right in the stream or at the well. These include temperature, acidity (pH), dissolved oxygen, and electrical conductance (an indirect indicator of dissolved minerals in the water). Analyses of individual chemicals generally are done at a laboratory.
USGS, 2009
Water Quality
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Water Quality and Groundwater Movement
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Sources of Contamination
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Groundwater Contamination
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Investigation tools!
Remote Sensing Geophysics Subsurface Investigations
(monitoring wells, soil and rock borings, etc.)
Aquifer Testing Water level monitoring Water Chemistry Computer Modeling
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Conclusion
Basic definitions Hydrologic Cycle Groundwater Aquifers How water flows Water Budgets Wells Water Quality Contamination
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Thank you
Questions?