Monitoring of Groundwater and Surfacewater Interactions on the Walla Walla River
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Transcript of Monitoring of Groundwater and Surfacewater Interactions on the Walla Walla River
Monitoring of Groundwater and Surfacewater Interactions on the Walla Walla River
Graduate Student: Starr Silvis
Major Professor: John Selker
Field Coordinator: Bob Bower
outline
Presentation Outline
Location and features of the basinBackgroundGoalsMethods
Chemical SignatureMini-piezometersTemperature Profiling
ResultsDiscussion
background
Location of the Walla Walla River Basin
background
Water Resources for the Basin
Surface waterNorth Fork and South Fork
GroundwaterAlluvial aquiferBasalt aquifers
background
Monthly Mean Flows
0
50
100
150
200
250
300
350
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec
Month
Mon
thly
Mea
n Fl
ow (
cfs)
South Fork
North Fork
22 years of data 1969 - 1991
background
Walla Walla River Returns!
All river water above levied section (~100 c.f.s.) diverted for irrigation since turn of the century from June – September
1998 American Rivers lists Walla Walla River as one of the top 20 most endangered rivers in the U.S.
Bull trout and Steelhead E.S.A. listed in 1998 and 1999
Irrigation districts pledge to leave flow in the mainstem of the Walla Walla River; sign agreement with U.S.F.W. 2000 – 13 c.f.s 2001 – 18 c.f.s. 2002 – 25 c.f.s 2003 - ?
background
Summer 1999
Summer 2002
background
Low Flow Limitations
2000 - all 13 c.f.s. percolated from the surface
Possible causes
In-stream gravel miningNaturally high hydraulic conductivity (Schälchli,
1995,1992)Large hydraulic gradients due to low aquifer levels
background
Aquifer Recharge
Irrigation ditch lossesPrimarily unlined ditches
Stream lossesWinter rechargeNow – summer recharge too
goals
Study Goals
Provide quantitative framework for the surface and groundwater exchanges
Determine influent / effluent nature of levied section
Quantify river losses
Identify seasonal patterns
Estimate alluvial aquifer recharge
SW/GW Overview
Water flows from the stream into the subsurface
Water flows from the subsurface into the stream
methods
Methods
Chemical Signature
Mini-piezometers
Temperature profiling
Ditch loss
methods
Chemical Signature Requirements
Conservative and naturally occurringChloride and Sulphate
GW/SW must have distinctly different concentrations
Ease of analysisIon chromatography
methods
Chemical Signature
Grab Sampling Mainstem Walla Walla River Shallow aquifer wells10% duplicate sampling
Data AnalysisMixing space diagramsLinear RegressionsMass Balance
methods
Chemical Signature; Mass Balance
Qsin
Csin
Qgw Cgw
Qs
Cs
Upstream sampling point
Downstream sampling point
Accumulation = In – OutAccumulation = 0In = Out
methods
Groundwater Sampling Sites
Tumalum Bridge
Nursery Bridge
Milton-Freewater
Hwy 11
Walla Walla River
Red dots are wells
methods
In-Stream Sampling Sites
Nursery Bridge
Tumalum Bridge
Milton-Freewater
methods
Mini-Piezometers
dl
Vertical Hydraulic Gradient = dh/dl
Streambed surface
Mid-point of perforations
Stream surface
dh
outline
Mini-piezometer
Temperature profiling device
methods
Temperature Profiling
methods
Temperature Profiling
Analytical MethodsHYDRUS-2D (Šimůnek et al., 1999)
Computer model using inverse processes to solve for vertical flux
Sine Wave FittingStallman’s (1965) equation for a sine wave fit to
the data
methods
Temperature Profiling
HYDRUS-2D
Sophocleus (1979)
iiw
jij
ix
TqC
x
T
xt
TC
])([)(
Conduction Convection
methods
Temperature Profiling
Sine Wave FittingStallman (1965)
Solution for diurnally heated and cooled boundary condition
t
Tc
z
Tvc
z
Tk oo
2
2
Tz (t) = ΔT e-az sin (2πt/τ – bz) + Taz
methods
Temperature Profiling; No Flux
HYDRUS-2D no flux simulation R2 = 0.95
methods
Ditch Loss StudyInstalled dam
Covered with plastic
Allowed to fill to capacity
Shut off water supply
Measured time and depth of draining for 6 hours
results
Chemical Signature; GW
0.00
5.00
10.00
15.00
20.00
25.00
30.00
0.00 2.00 4.00 6.00 8.00 10.00 12.00 14.00 16.00
Chloride (mg/l)
R2 = 0.89
results
Chemical Signature; SW
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
0.4 0.6 0.8 1.0 1.2 1.4 1.6
Chloride (mg/L)
R2 = 0.96
results
Chemical Signature; Mass Balance
0.0
0.2
0.4
0.6
0.8
1.0
1.2
1.4
5 10 15 20 25
Site Number (SW-)
0.00
0.20
0.40
0.60
0.80
1.00
1.20
1.40
1.60
1.80
12-J ul
31-J ul
14-Aug
12-J ul
31-J ul
14-Aug
Tumalum Bridge
Filled symbols correspond to left axis, open symbols correspond to the right axis
GW dominates
SW dominates
Qsin
Qgw
results
Mini-piezometers Average Vertical Hydraulic Gradient
-1.80
-1.60
-1.40
-1.20
-1.00
-0.80
-0.60
-0.40
-0.20
0.00
0.20
Piezometer site ID
Vert
ical
Hyd
raul
ic G
radi
ent
(cm
/cm
)Nursery Bridge Tumalum Bridge
duplicatesduplicates
results
Temperature Profile
10
12
14
16
18
20
22
8/17/0212:00
AM
8/17/024:48 AM
8/17/029:36 AM
8/17/022:24 PM
8/17/027:12 PM
8/18/0212:00
AM
8/18/024:48 AM
8/18/029:36 AM
8/18/022:24 PM
8/18/027:12 PM
8/19/0212:00
AM
time
degr
ees
(C)
5
4
3
2
1
results
Temperature Profiling; Sine Wave
12
13
14
15
16
17
18
19
20
21
22
8/11
/02
7:01
8/11
/02
12:0
1
8/11
/02
17:0
1
8/11
/02
22:0
1
8/12
/02
3:01
8/12
/02
8:01
8/12
/02
13:0
1
8/12
/02
18:0
1
8/12
/02
23:0
1
8/13
/02
4:01
Date
Te
mp
(C
)logger 3 data
logger 3 f it
logger 2 data
logger 2 f it
logger 1 data
logger 1 f it
M 5.5 August 14
results
Temperature Profiling; HYDRUS-2D
12
14
16
18
20
22
0.0 0.5 1.0 1.5 2.0 2.5
Time [days]
M-5.5 (August 14th)
results
Temperature Profiling; Sine Wave vs. HYDRUS-2D
y = 3.29x0.73
R2 = 0.55
y = 1.98x0.71
R2 = 0.78
1
10
100
1000
1 10 100 1000
HYDRUS-2D estimation of q (cm/d)
Sta
llman
's s
ine
est
imat
ion
of q
(cm
/d)
Pink are results using loggers 3 to 2 (15 cm)
Blue are results using loggers 3 to 1 (30 cm)
results
Mini-piezometers
-140
-120
-100
-80
-60
-40
-20
0
20
40
06/08/01 07/28/01 09/16/01 11/05/01 12/25/01 02/13/02 04/04/02
date
mea
n he
ad d
iffer
ence
(cm
)
results
Seasonal Patterns; Mini-Piezometers
0.00E+00
2.00E-03
4.00E-03
6.00E-03
8.00E-03
1.00E-02
1.20E-02
1.40E-02
1.60E-02
1.80E-02
2.00E-02
M4-M5a M5b-M6 M6-M7 M7-M8
Site IDs
K (
cm/d
ay)
july
aug
oct
K = -Q / (A dh/dl)
results
Seasonal Patterns; Temperature
0
50
100
150
200
250
300
350
6/13/2002 7/3/2002 7/23/2002 8/12/2002 9/1/2002 9/21/2002 10/11/2002
Date
Q (
cm/d
ay)
HYDRUS-2D
Sine
HYDRUS-2D average
results
Ditch Loss
Infiltration estimate 204 cm/d
discussion
Conclusions
Effluent river on section studiedEstimated flow loss
0.3-0.76 m3/s using temperature estimates0.43-0.63 m3/s using in-stream flow
measurements
Seasonally hydraulic conductivity decreased factor of 2-4 using temperature profiling estimatesfactor of 2-100 using mini-piezometer estimates
discussion
Implications for GW recharge of the shallow aquifer
Assuming only 50 km of ditches with an average infiltration rate of 204 cm/d 2 * 107 m3 / yrOn an area of 538 km2 and a porosity of 0.27
equivalent to 23 cm of water
Assuming 5 months at max infiltration rate of 310 cm/day using temperature profiling estimates 1.8 * 108 m3 / yr On an area of 538 km2 equivalent to 1.2 meters of
water
discussion
Future Work
Determine seasonal patterns in aquifer levelsContinual static level measurements
Installed pressure transducers in 12 wellsChemical signature
Spatial mapping of anion concentrationsDitch loss studies
Inflow out flow measurementsTemperature profiling of ditch bedEvapotransporation
Area of influence of infiltration from the river Instrument a transect across the entire levyLeave devices in place for the entire season
Thanks to;
WWBWC and OWEB for caring enough about the watershed to fund this project
Bob Bower for EVERYTHING!
Community in the Walla Walla Watershed
John Selker for tireless enthusiasm and myriad of good ideas
Emilie Baer for her hard work in the field and in data analysis
My committee; Julia Jones, Jeff McDonnell, Roy Haggerty, and Mike Gamroth
OSU Bioengineering Department; June Rice, Elena Maus, David Rupp, Kristy Warren, Ruth Boitz, Linda
Hoyser
Friends and Family for continual support
Especially thanks to Jeff Silvis for still becoming my husband even after the trials and tribulations of moving across the country and graduate school.