Transcript Document

GROUNDWATER RECHARGE
AND FATE OF GROUNDWATER
STORAGE OF
THE WEYBO RIVER
CATCHMENT
WELAYITA-HADIYA ZONES
SOUTHERN ETHIOPIA
BACKGROUND
 Most activities come to rely on
groundwater resources than on surface
water resources mainly due to their
sustainability and quality
 The Potentialities of Groundwater resource
is mainly factored by the Rate of Recharge
 Changes in the Geo-Environment of the
catchment and the entire Omo-Gibe Basin is
manifested by changes in Recharge Rates
OBJECTIVES
 Estimating the Optimum Groundwater
Recharge
Showing the Temporal-Trend of Recharge
w.r.t. the Temporal Changes of the HydroMeteorological Parameters
Assessing the Fate of Groundwater
Storage
To Show the Major Controlling Parameter
of Groundwater Recharge in the Catchment
AREAL EXTENT = 574Km2
PERIMETER = 124Km
60 55’ 42 - 7010’28N
370 31’ 39 - 37046’40E
1000000
950000
900000
850000
800000
750000
DISTANCE FROM ADDIS ABABA AND
ALTERNATIVE ROADS
700000
650000
Legend
Study area
600000
Omo-Gibe Basin
550000
0
500000
100000
150000
200000
250000
50000
300000
100000
350000
Location of the study area in the Omo-Gibe Basin
Along Addis Ababa – Butajira – Hosaina Road = 300Km
Along Addis Ababa – Shashemene – Welaita Road = 410
150000 mAlong Addis Ababa – Durame – Areka = 440Km
400000
PHYSIOGRAPHY
 50% of the area has a slope 2-6%,
 25% has 0-2%,
15% has 6-12%,
 6% has 12-24%
Elevated areas are found in the
boundaries of the area
Topographic relief ranges from 18001900m from the highest peak Damota
to the lowest Weybo valley
GEOLOGY
 The main lithologic units that are outcropped in the
study area and near to its adjacent watersheds are the
teritiary volcanics
 The Nazareth Groups (of Miocene to Pliocene age) and
the flood basalts (Eocene to early Miocene age) are the
dominant units that widely cover the study area
 About 90% of the area is covered by the Nazareth Group,
which comprises of a series of rhyolite-trachyt flows,
ignimbrites, pumice and ash falls
 The Nazareth Group unconformably overlies the early
flood basalts
795000
790000
785000
780000
775000
Legend
770000
Flood basalt
Rhyolite
765000 Trachyte
Ignimbrite
760000
Alluvium
755000
Inferred faults
Known fault
750000 Elevation contours
1800
0
10000
20000
30000
40000 meter
335000 340000 345000 350000 355000 360000 365000 370000 375000 380000 3
HYDROGEOLOGY
HYDROGEOLOGIC UNITS AND AQUIFER SYSTEMS
AQUIFER FORMATION
-Weathered and fractured ignimbrite/welded tuff
-Sediments associated with weathered pumice
-Weathered and fractured rhyolites and Trachytes
TYPES OF AQUIFERS IN THE CATCHMENT
-Dominantly leaky aquifers
HYDROGEOLOGICAL MAP OF THE STUDY AREA
795000
790000
785000
780000
775000
770000
765000
760000
0
10000
20000
30000 meter
795000
HYDRAULIC CHARACTERISTICS
790000
0.8
785000
0.7
0.6
780000
0.5
775000
0.4
0.3
770000
0.2
765000
0.1
335000
340000
Legend
0
345000
350000
10000
355000
360000
20000
365000
30000
370000
375000
380000
40000 meter
Boreholes and their distribution used to map hydraulic conductivity of the area
 Correlation has been made between
Geological structures and hydraulic conductivity values
 A greater extent of the study area possesses
a low permeability zone.
GROUND WATER FLOW SYSTEMS AND
POTENTIOMETRIC CONTOURS
Regional, intermediate and local flow systems
795000
790000
785000
780000
775000
Legend
770000
765000
Regional groundwater flow directions
Local groundwater flow directions
Ground water table
elevation contours
1850
760000
335000
340000
345000
0
10000
350000
355000
20000
360000
30000
365000
40000 meter
370000
375000
RECHARGE AND DISCHARGE ZONES
 Zonation based on topography
790000
785000
2880
780000
2200
775000
770000
e
g
r
a
h
c
Re
765000
e
n
zo
335000 340000 345000 350000 355000 360000 365000 370000 375000
0
10000
20000
30000
40000 meter
1900
800
 Zonation based on peizometric patterns
Flow lines tend to diverge from recharge areas and
converge toward discharge zones
790000
785000
780000
775000
Legend
Zones of converging flows
Catchment boundary
770000
Ground water flow directions
765000 Ground water table contours
340000
345000
0
350000
355000
10000
360000
20000
365000
30000
370000
375000
380000
40000 meter
Fig. Convergence and divergence zones of flow lines showing recharge and discharge zones
 Zonation Based on Hydro chemical Trends
HYDROMETEOROLOGY
PRECIPITATION = 1340 mm
TEMPRATURE = 19.210C
RELATIVE HUMIDITY = 63.5%
MEAN WIND SPEED = 2.45m/s
POTENTIAL EVAPOTRANSPIRATION = 1074.4mm
ACTUAL EVAPOTRANSPIRATION (AET) = 960.3mm
STREAM DISCHARGE OF WEYBO RIVER
(i)
Scaling up the stream flow values
Qmouth = (A2/A1) Qgauged
(ii)
The analogue method
Q = Qan (Pan/P)
3
SUMMARY OF WEYBO RIVER DISCHARGE,m /s, 1992 - 2005
WAT.
YEAR
JAN
FEB
MAR
APR
MAY
JUN
JUL
AUG
SEP
OCT
NOV
DEC
TOTAL
1992
0.873
0.742
1.116
2.475
5.521
3.785
5.754 27.050 35.044 34.221 26.519 10.400
1993
1.235
1.942
0.787
1.907
8.330
7.991
8.415 17.491 11.366
4.984
1.654
0.781
1994
0.622
0.548
1.014
1.751
3.505
3.776 17.453 27.442 12.739
4.436
1.430
0.713
1995
0.548
0.557
0.534
3.310
2.833
2.426 11.675 14.278 21.995 11.761
1.996
0.669
1996
0.569
0.348
1.618
3.855
6.759 30.334 22.546 21.688 28.892
1.878
0.666
1997
0.424
0.345
0.528
3.113
3.575
2.152
3.001 11.454 18.458
7.985
1998
2.662
1.598
1.509
2.043
5.394
6.252 14.847 26.248 14.988 16.848
6.432
2.054
1999
1.318
0.928
1.223
2.302
2.553
2.856
9.367 11.557 10.602 19.428
5.146
1.483
2000
0.525
0.427
0.545
1.760
4.710
1.509
2.564
8.012 12.695
6.160
1.556
2001
0.704
0.542
0.545
1.350
5.071
6.535 13.131 26.761 19.498 12.598
3.060
0.848
2002
0.878
0.793
1.940
1.350
0.943
0.973
1.512
2.673
2.187
0.843
0.366
0.610
2003
0.539
0.454
1.630
2.635
0.914
2.043
6.841 20.403
5.671
0.843
0.365
0.628
2004
0.873
0.742
1.116
2.453
4.051
1.229
3.260
5.208
4.572
5.777
1.129
0.510
2005
0.448
0.422
1.515
4.032
2.554
1.231
3.259
5.207
4.571
5.778
1.128
0.510
0.873
0.742
1.116
2.453
4.051
5.221
8.915 15.623 13.081 10.636
5.408
2.101 70.219
MEAN
4.180
5.406
7.310
7.230
GROUNDWATER RECHARGE (GWR)
 CONVENTIONAL WATER BALANCE APPROACH
GWR = 88.19mm/annum
 STREAM HYDROGRAPHS ANALYSES
Mean long-term minimum flow = 62.5mm/year
Seasonal recession method = 74.5mm/year
 CHLORIDE MASS BALANCE = 123.5mm/year
THE OPTIMUM GROUND WATER RECHARGE
ESTIMATION BASED ON GROUNDWATER BUDGET
ESTIMATED GROUNDWATER OUTFLOW = 78.56
GW INFLOW ESTIMATED FROM WATER BALANCE
AND SEASONAL RECESSION METHOD = 81.5mm
THE OPTIMUM GROUND WATER RECHARGE = 81.5
TREND OF GROUNDWATER RECHARGE
FATE OF GROUNDWATER STORAGE
Equating the linear equation: y = -587x + 93.07
Groundwater storage will be heavily affected
and appreciable change in storage will be
seen after 30 years now on
RECHARGE TREND W.R.T. CONTROLLING
HYDRO-METEOROLOGICAL PARAMETERS
MEAN PPT,mm
TREND OF PRECIPITATION IN THE STUDY AREA
1500
1400
1300
1200
1100
1985-1989
1990-1994
1995-1999
2000-2004
Mean precipitation is slightly decreasing,
however, its rate of declination is not
comparable
mean temperature shows an increasing trend
16
0
Minimum T(
C)
15
14
13
12
11
10
1988
1989
1990
1991
1995
1996
1997
1998
1999
2000
2001
2002
2003
9
8
7
6
5
4
3
2
1
0
19
88
19
89
19
90
19
91
19
92
19
93
19
94
19
95
19
96
19
97
19
98
19
99
20
00
20
01
20
02
20
03
20
04
20
05
Mean Wind
Speed(m/s)
I n c r e a s i n g T r e n d o f M e a n W i n d Sp e e d
mean wind speed shows an increasing trend
2004
TREND OF PET, 1988-2005
potential evapotranspiration is slightly increasing
1200
1150
PET, mm
1100
1050
1000
950
900
850
1988 1989 1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005
CONCLUSION
-Groundwater recharge is computed using 4 different Methods
and four different values are obtained. The optimum=81.5mm
-The decline in groundwater recharge is highly attributed to
changes in the environment
-Measurable changes in groundwater storage will be seen in
a 30 years period of time if environmental changes are
keeping on the same rate
-The groundwater recharge estimated from measurements of
chloride yields an over estimated result.