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EVALUATION AND DEVELOPMENT OF GROUND WATER RESOURCES OF ADA'A

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Title: EVALUATION AND DEVELOPMENT OF GROUND WATER RESOURCES OF ADA'A


1
EVALUATION AND DEVELOPMENT OF GROUND WATER
RESOURCES OF ADA'ABECHO PLAINS FOR IRRIGATION
PROJECT
  • Engida ZA, Tilahun A, Dr. Seifu K and Dr.
    Yilma

Client Ministry of Water Resources -
Consultant Water Works Design Enterprise (WWDSE)
WATER WORKS DESIGN AND SUPERVISION ENTERPRISE
P.O.BOX 2561 Tel 011- 6614501 Fax 011-6615373
email w.w.d.s.e_at_ethionet.et
2
TABLE OF CONTENT
  • Location
  • Objective and scope of the study
  • Methodology
  • Geology and structures, Hydrology, Geophysics,
    Drilling of mapping wells
  • Isotope and water quality, Water quality
    monitoring, Hydrogeology
  • Main study output of the project
  • Developing conceptual models (Inception phase)
  • Preparing hydrogeological map
  • Preparing groundwater flow system of AB Plains

3
TABLE OF CONTENT
  • Evaluation of groundwater potential of Ada'a and
    Becho plains
  • Interaction of Debre Zeit Lakes with the
    groundwater system
  • Interaction of Awash river with the groundwater
    system

4
1. LOCATION OF THE PROJECT AREA
  • Central Ethiopia, in Oromia Regional State in
    Upper Awash river Basin
  • Adaa plain is found between elevation 1600 and
    1900 masl and approximately between Co-ordinates
    38050E - 39015E and 8030N - 8053N (T
    area-1641 km2 ,223km2M Net area of the plain1418
    km2
  • Becho plain is found between elevation 2040 and
    2120 masl and approximately between coordinates
    38008E - 38036E and 8038N - 9000N (T area
    1414km2 seasonally inundated area117km2 net area
    1297 km2)

Fig1
S6
5
Fig1 LOCATION MAP OF THE PROJECT AREA
6
2. OBJECTIVE AND SCOPE OF THE STUDY
  • Previous studies have indicated that there is a
    possible high groundwater potential, currently
    agriculture consists mainly of rain fed annual
    cropping. Crop yields are generally good in the
    project area, the high population growth has made
    the available land decreasing from year to year.
  • Unless remedial measures are taken, the standard
    of living of the farmers will further decline,
    especially in view of the current rapid
    population growth rate of about 2.9 per year.
    Since the rural population is expected to double
    in about 25 years, it is increasingly important
    to deal with these issues as soon as possible by
    implementing irrigation in the area.

7
2. OBJECTIVE AND SCOPE
  • Determine the hydrogeological condition of the
    Ada'a-Becho plains groundwater system
  • Qualitative and quantitative evaluation of the
    groundwater resources of the plain and select
    potential well fields
  • Carry out analytical and/or numerical model of
    the main aquifer of the area to recommended
    appropriate groundwater management
  • Develop strategy of groundwater resources
    development together with cost estimates

8
3. METHODOLOGY
  • Data collection review of previous works.
  • Geological geomorphologic mapping
  • Hydrological survey and analysis
  • Hydrogeological investigation (water point
    inventory, water quality survey, water quality
    monitoring, mapping well drilling testing)
  • Geophysical investigation (Resistivity and TEM)
  • Isotope hydrogeology
  • Detail qualitative quantitative groundwater
    potential evaluation
  • Prioritization of potential prospective area for
    Pilot well field development
  • Analytical Modelling

SN
9
3. MAIN OUTPUTS OF THE PROJECT
  • A. Developing conceptual models (In. phase) The
    hydrogeological and isotope data from Akaki
    catchment shows the following conditions
  • Most of the deep wells drilled in Addis Ababa and
    adjacent areas are highly confined. Confining
    acidic volcanic and the aquifer basic rocks
    (basalt of different comp. and ages)
  • The upper part of Akaki catchment is steep and
    composed of dominantly acidic volcanic rocks
    (which are practically impervious) it is
    difficult to assume that a recharge that occurred
    at the upper part of the catchment has formed a
    confined aquifer in the basalts at the central,
    eastern and western AA. The upper part of Akaki
    river catchment is merely runoff generator.

Fig 2
10
3. MAIN OUTPUTS OF THE PROJECT
  • A. Developing conceptual models (In. phase) The
    hydrogeological and isotope data from Akaki
    catchment shows the following conditions
  • The tritium value from different sources Yves M.
    Travi, Kebede S. (2000) shows Except few wells
    (probably shallow wells) the other wells both
    cold and thermal wells are depleted in tritium
    value in general
  • Reconnaissance surveys at Muger and Abbay rivers
    gorges showed that the Mesozoic sedimentary
    formation is most likely dipping in SSE
    direction, which highly favors the Abay plateau
    groundwater flow to SSE direction into Awash
    River basin
  • These observations led to conceptualize that the
    groundwater of Addis Ababa and in general Becho
    and Ada'a plains groundwater is recharged mainly
    from outside their surface catchments. The basalt
    plateau of Abay river basin that is found
    adjacent to Akaki and Awash rivers catchments
    could be the main recharge zone of Ada'a plain
    (as shown the figs 3and 4 below)

11
Fig 2 CONCEPTUAL MODEL DEV.
FIG 3
FIG 4
Main output
12
FIG 3 CONCEPTUAL X-SECTION AP-AA-ADAA
13
FIG 4 CONCEPTUAL X-SECTION AP-BECHO-ADAA
14
3. MAIN OUTPUTS OF THE PROJECT
  • B. Preparation of Hydrogeological map and
    cross-section Phase I Inv. and analysis
  • Hydrogeological conditions of the area is a
    function of geomorphology and tectonics, on the
    Plateau older Tertiary volcanic outcrops to the
    south the younger geological formation over lies
    the older volcanic unit
  • The recharge condition, groundwater flow and
    aquifer parameters in the Adaa-Becho plains is
    highly governed by the general bedding of the
    sedimentary formation underlying the volcanic
    unit, the tectonic condition and the hydraulic
    properties of the different volcanic units that
    outcrops in the basin
  • There are two basaltic aquifers in the Becho
    plain and along west-east direction from
    Becho-Legedadi section which are separated by
    ignimbrites and welded tuffs

HG-Map
BECHO
15
3. MAIN OUTPUTS OF THE PROJECT
  • B. Preparation of Hydrogeological map and
    cross-section Phase I Inv. and analysis
  • Upper Basalt Aquifer
  • composed of Quaternary of Weliso-Ambo basalts,
    Akaki basalts scoria and spatter cones, and
    Tertiary-Neogenes basalt of Addis Ababa basalts
    and Tulu ries basalts.
  • one aquifer system in Adaa plain (south of
    Dukem)
  • distributed in Upper Awash, where it outcrops at
    Central Addis Ababa, Weliso and Akaki and it also
    overlain by ignimbrites and tuffs at Becho
    plaains, Legedadi area, in general where the
    ignimbrites and tuff outcrops
  • Varies from more than 200 to 50 m thickness TDS
    400-700 mg/l
  • by water balance method and chloride balance
    method the recharge of this aquifer is estimated
    to be 390 Mm3/year

16
3. MAIN OUTPUTS OF THE PROJECT
  • B. Preparation of Hydrogeological map and
    cross-section Phase I Inv. and analysis
  • Lower Basalt Aquifer
  • composed of tertiary Tarmaber basalt composed of
    dominantly scoraceous basalt and Amba Aiba
    basalt. These tertiary basalt formations occupy
    more than 75 of Abay plateau about 7,000 km2. .
  • mapping wells drilling at Becho Plain, Holota,
    Melka Kunture, Legedadi areas penetrated at
    different depth this aquifer. The total confining
    head more than 220 meters
  • The yield of the well was progressively
    increasing when the depth of penetration is
    increased in this aquifer. Water level varies
    from artesian condition to a depth of 67.5 meters
  • The total annually recharge of the lower aquifer
    is estimated by different method is about
    700Mm3/year.

Sn 24
17
Fig 5 Hydrogeological Map of ADAA-BECHO PLAINS
Fig 10
Fig 7
Fig 9
Fig 8
Fig 6
Fig11
18
Fig 6 HYDROGEOLOGICAL X-SECTION ALONG BECHO
PLAIN
19
Fig 7 Hydrogeological x-section along Kachise
Becho-Adaa line
20
Fig 8 Muger-Holota-Becho
21
Fig 9 SEGNO GEBYA-LEGEDADI
Well log
22
Fig 10 Hydrogeological x-section along Plateau
-Legedadi - Akaki section line
23
Fig 11 Hydrogeological x-section in Adaa Plain
(Southwest Northeast direction)
24
3. MAIN OUTPUTS OF THE PROJECT
  • B. Preparation of Groundwater flow system of AB
    Plains Phase I Inv. and analysis
  • Groundwater level elevation contour map was
    constructed for the regional basalt aquifer
    (lower aquifer) applying the data generated from
    drilling of mapping wells and existing bore holes
    identified to be representing the regional
    aquifer water level
  • On the groundwater elevation contour map the
    following understanding is obtained
  • Entoto and Wechecha furi and Bedegebaba ridges
    acts as local barrier
  • The recharge at Abay plateau flows to Upper
    Awash through two main direction i.e. through
    Becho plain and along Legedadi areas
  • Almost 100 of Abay plateau is the recharge
    area of the lower basalt aquifer in Upper Awash
    basin
  • Bore holes drilled along flow paths have yield
    and artesian if drilled at lower places

Fig12
Fig 12
sn30
25
Fig 12 SIMPLIFIED GROUNDWATER FLOW PATHS IN AB
26
Fig 13 Drilling at Holeta area
27
Fig 14 DRILLING AT ASGORI
28
Fig 15 Melka Kunture Pumping test Q36 l/s
29
Fig 16 Artesian flow well drilled south of
legedadi
30
3. MAIN OUTPUTS OF THE PROJECT
  • C. Evaluation of groundwater potential of Adaa
    plains (ECGPAP)
  • AQUIFER CHARACTERISTICS
  • aquifer composed of scoria, scoraceous Basalt and
    fractured basalt unconfined extensive with high
    transmissivity
  • groundwater recharge to Adaa plain groundwater
    system is from three direction i.e.i) between
    Mountains Yerer and Guji, ii) between Bede Gebaba
    and Ziquala (Qgz) and from Mojo, Wedecha and
    Belebela catchment (Qmw).

31
ADAA PLAIN
32
Fig 11 Hydrogeological x-section in Adaa Plain
(Southwest Northeast direction)
33
3. MAIN OUTPUTS OF THE PROJECT C. ECGPAP
ESTIMATED RECHARGE AP
Recharge Direction Weighted transmissivity (Tav), m2/day Width of flow (L), m Average flow gradient (I) Recharge estimated in MCM/year Remark
Yerer Guji Zone 1200 10,800 0.02 94.6
Bede Gebaba Ziqual 10,200 13,460 0.01 532.0
ModjoWedecha Belebela 153.0 Vol. II chap 7.3
Total Total 779.6 MCM/Year
34
3. MAIN OUTPUTS OF THE PROJECT ESTIMATED
EXPLOITABLE GWR OF AP Analytical method
  • Excluding the recharge from Becho plain due to
    the maximum exploitation of the groundwater
    resource in the plain the net available
    exploitable ground water potential is estimated
    about 1,046MCM/year or 2.9MCM/day or 33 500 l/s

35
3. MAIN OUTPUTS OF THE PROJECT PRIORITIZING
GROUNDWATER PROSPECTING SITES IN AP
Prospective site Prioritizing Criteria Prioritizing Criteria Prioritizing Criteria Prioritizing Criteria Ranking
Prospective site Area, ha GWD range, m T,Range, m2/day EC,range, µS/cm Ranking
A 23,425 Dominantly from 60-120 5,000-10,000 in some part gt10,000 Dominantly 500-750 2
B 19,760 lt 30 5,000-10,000 Dominantly 500-750 1
C 5,540 60-120 5,000-10,000 500-750 3
D 3,316 30-90 200-1,000 500-750 4
Fig 17
36
3. MAIN OUTPUTS OF THE PROJECT C. ECGPAP Fig
17 Prospective groundwater potential sites
Table
37
3. MAIN OUTPUTS OF THE PROJECT C. ECGPAP
Parameters considered
  • The groundwater system as extensive unconfined
    aquifer.
  • Average transmissivity of the confined aquifer
    Tavg 5000m2/day
  • The specific yield of the aquifer is estimated to
    be about 0.25.
  • Thickness of Aquifer 300 m
  • 100 wells 1km apart in grid

38
C. ECGPAP Fig 18 Proposed PW in prioritized sites
39
C. ECGPAP Calculated Max DD in the WF for
different scenario of Abstraction rate and
duration of pumping
Scenario Well discharge Well discharge No. wells Total discharge Total discharge Calculated maximum drawdown at the center of the well field for different period of exploitation Calculated maximum drawdown at the center of the well field for different period of exploitation Calculated maximum drawdown at the center of the well field for different period of exploitation Calculated maximum drawdown at the center of the well field for different period of exploitation Calculated maximum drawdown at the center of the well field for different period of exploitation Calculated maximum drawdown at the center of the well field for different period of exploitation
Scenario l/s m3/ day No. wells l/s m3/day 500 days 1000 days 2000 days 5000 days 8000 days 10000 days
  l/s m3/ day No. wells l/s m3/day 1.4 2.7 5.5 13.7 21.9 27.4
1 20 1728 120 2400 207360 2.3 4.6 6.9 9.9 11.4 12.2
2 40 3456 120 4800 414720 4.6 9.1 13.7 19.8 22.9 24.4
3 50 4320 120 6000 518400 5.7 11.4 17.2 24.7 28.6 30.4
4 70 6048 120 8400 725760 8 16 24 34.6 40 42.6
5 100 8640 120 12000 1036800 11.4 22.9 34.3 49.4 57.2 60.9
40
C. ECGPAP Estimated EGWP of prioritized area
  • The estimated exploitable groundwater resource
    (safe yield) is about 378MCM /Year or 1,036,800
    m3/day or 8, 640 l/s by 100 wells each
    discharging 100 l/s.

41
C. ECGPAP IMPACT ON THE LAKES
Lake Name Distance from the well field, m Discharge of the wells in m3/day and drawdown after 5000 days Discharge of the wells in m3/day and drawdown after 5000 days Discharge of the wells in m3/day and drawdown after 5000 days Discharge of the wells in m3/day and drawdown after 5000 days Discharge of the wells in m3/day and drawdown after 5000 days
Lake Name Distance from the well field, m 207360 414720 518400 725760 1036800
LakeBishoftu Guda 3025 2.68 5.36 6.69 9.37 13.39
Lake Hora 2663 0.89 1.79 2.23 3.12 4.46
Lake Bishoftu 3650 0.89 1.79 2.23 3.12 4.46
42
C. ECGPAP IMPACT ON THE LAKES
  • The result of analysis shows that the maximum
    drawdown created on the lakes is less than 14
    meters on the nearest lake Bishoftu Guda. Here it
    is found possible to shift further to the east
    the well field by two kilometers and the draw
    down on Lake Bishoftu Guda decrease similar to
    the other lakes.
  • Further Numerical modeling shall be conducted to
    verify this analytical calculation in the final
    report. The estimated exploitable resources is
    estimated about 378 MCM/year on site B.

43
C. ECGPAP NEXT STAGE
  • Drilling of 5 pilot wells each well discharge
    100 l/s
  • Detail design of 500 ha Pressurized irrigation
  • Ground water modelling
  • Feasibility design of 10, 000 ha pressurized
    irrigation

44
MAIN OUTPUTS OF THE PROJECT
  • D. Interaction of Debre Zeit Lakes with the
    groundwater
  • Hydrogeological method of analysis
  • Water quality monitoring
  • Monthly water balance of DZ lakes (hydrologic
    method

45
MAIN OUTPUTS OF THE PROJECT
  • D. Interaction of Debre Zeit Lakes with the
    groundwater
  • Hydrogeological method of analysis
  • Constructing a groundwater level elevation
    contour two groundwater flow regimes within
    Adaa plain caused by Debre Zeit lakes and
    Mountain Bede Gababa which they act as a
    groundwater divide and Barrier to the ground
    water system (fig 19)
  • Water Quality monitoring (fig 20)
  • Lake Water balance of DZ lakes (fig21)

F1
46
Fig 19 Groundwater flow paths at DZ lakes area
47
Fig 20 EC versus time monitored BH (WQM)
48
Fig 21 Time series of groundwater Inflow-outflow
(1000 m3)
49
MAIN OUTPUTS OF THE PROJECT
  • D. Interaction of Debre Zeit Lakes with the
    groundwater
  • All the methods (Hydrogeological, water quality
    monitoring and Water balance of DZ lakes showed
    method the lakes except Kurftu lake acts as
    groundwater divide (recharge boundary) and Bede
    gebaba ridge as a barrier.

50
MAIN OUTPUTS OF THE PROJECT
  • Interaction of Awash river with the groundwater
  • Awash river monitored two stations (upstream at
    Melkakunture and down stream at Ombole river
    gauging stations) far apart more than 50kms. From
    July- September, the EC at the two stations are
    nearly similar (about 100µS/cm). During dry
    season the electrical conductivity value measured
    at the two stations shows larger gap (400µS/cm at
    Melka Kunture and 600-650µS/cm at Ombole
    respectively). The conductivity of the regional
    groundwater of the area between Melka Kunture and
    Ombole vary from 600 to 650 µS/cm. The higher EC
    value measured at Ombole site verifies the fact
    that the river is being recharged by regional
    groundwater and the base flow from November to
    June at this station is from the regional
    groundwater

SN19
51
Fig 22 Interaction of Awash with the groundwater
52
TEM Interpretation at Inchini
53
Segno Gebeya
54
Sululta
55
Chancho
56
THANK YOUFOR YOUR ATTENTION!!
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