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Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria
IJGM
Investigation of Groundwater Potential and Aquifer
Protective Capacity of Part of Effurun, Delta State,
Nigeria
Bello Rasaq
Department of Physics, University of Port Harcourt, Port Harcourt, Nigeria
Tel.: +234(0)8036684498; Email: rasaq.bello@uniport.edu.ng
The aim of this study was to investigate groundwater potential and aquifer protective capacity of
an area behind the College of Science, Federal University of Petroleum Resources, Effurun-Warri
area of Delta State, Nigeria. The data was acquired using ABEM SAS 4000 Terrameter and
processed using IPI2win and Interpex software. Five Vertical Electrical Soundings were carried
out with maximum current electrode separation (AB) of 120 m. The VES curves generated from
the data revealed HKH curve type for VES 1 and VES 2, KQH curve for VES 3 and KH curve for
VES 4 and 5. Five resistivity layers were identified for VES 1 - 3 while four resistivity layers were
identified for VES 4 – 5. Analysis and interpretation of VES data obtained from the study area
showed VES 3, VES 4 and VES 5 to be most appropriate locations to be explored for borehole
development due to low resistivity of the weathered/fractured aquiferous layers coupled with the
relatively high thicknesses of the weathered layers. However, all the aquifers in the VES locations
are poorly protected due to the very low aquifer protective capacity parameters in the VES
locations.
Keywords: Aquifer, Resistivity, Vertical Electrical Sounding, Groundwater, Protective Capacity
INTRODUCTION
Aquifer protection is essential for a sustainable use of the
groundwater resources, protection of the dependent
ecosystems, and a central part of spatial planning and
action plans Egbai et al., 2015). The key expression for a
quantification of aquifer protection is vulnerability. Aquifer
vulnerability solely indicates whether the physical and
biochemical characteristics of the subsurface prevent or
favour the transport of pollutants in and into aquifers. It
does not take into account the actual pollutant loading in
an area.
Transmissivity is a major property of an aquifer and aids in
the characterization of rocks as water conducting
media/strata. The ability of the overburden to retard and
filter percolating fluid is a measure of its protective
capacity. Estimating these properties from pumping tests
can be very expensive and time consuming. Surface
geoelectrical methods offer an alternative, rapid and cost-
effective approach for aquifer evaluation and groundwater
quality assessment using empirical relations between
hydraulic and geoelectric parameters (Ehirim and
Nwakwo, 2010).
Poor quality water and inadequate water supply have
accounted for a number of preventable diseases in many
communities across the world. These factors have also
affected agriculture in terms of the types of crops grown
and yield as well as animals (Anomohanran, 2014).
According to Anomohanran (2013), pollution has
continued to make good quality water unavailable for use
despite the fact that nature has endowed the world with so
much water.
Groundwater is contributing significantly in the
development of agricultural economy and domestic water
usage. Groundwater is the water that fills all pores and
International Journal Geology and Mining
Vol. 3(3), pp. 141-150, November, 2017. © www.premierpublishers.org. ISSN: XXXX-XXXX
Research Article
Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria
Bello R. 142
openings within the zone of saturation. Exploration for
groundwater in sedimentary environments involves
locating formations that possess appropriate porosity and
permeability. While the location of permeable clean sands
that are capable of yielding useful quantities of water to
wells is important, the quality of water yielded is also
crucial (Aweto, 2014).
The Niger Delta is endowed with rich groundwater
resources in several aquifers, but unfortunately, the public
water supply by State Water Agency is inadequate and
unable to satisfy the demanded quantities (Akpoborie et
al., 2000) and consumers must make alternative
arrangements. These arrangements in most cases consist
of hand dug wells or relatively cheaper shallow boreholes
that are constructed with the aid of augers operated
manually. These boreholes are usually slightly deeper
than the dug wells but also exploit the shallow aquifers that
are the most susceptible to contamination from various
sources.
According to Tijani et al., (2002), one of the commonest
ways of waste disposal in the Niger Delta is by open
dumping. The primary environmental consequence of
these indiscriminate dumping of waste in open dump is the
generation of leachates due to decomposition of the waste
materials. The leachates are subsequently released into
the groundwater by infiltration and this poses serious
environmental problems including health hazard.
Surface geophysical survey as a veritable tool in
groundwater exploration, has the basic advantage of
saving cost in borehole construction by locating target
aquifer before drilling is embarked upon (Obiora and
Ownuka, 2005). The vertical electrical sounding (VES)
survey used in this work has been used extensively for
location of the aquifer and determining their hydraulic
parameters because the instrument is simple and analysis
of the data is easy and less tedious than other methods
(Lashkaripour et al., 2005; Batayaneh, 2007; Sikandar et
al., 2009; Anomohanran, 2013; Anomohanran, 2014). VES
method with Schlumberger array assumes considerable
importance in the field of groundwater exploration because
of its ease of operation, low cost and its capability to
distinguish between saturated and unsaturated layers.
This method is regularly used to solve a wide variety of
groundwater problems such as determination of depth,
thickness and boundary of aquifer, determination of zones
with high yield potential in an aquifer, determination of the
boundary between saline and fresh water zones and
estimation of aquifer transmissivity (Hadi, 2009).
Therefore, the aim of this study is to investigate the aquifer
systems in order to provide information about the
subsurface layers of the area using geophysical tools and
also to determine the aquifer protective capacity of the
study area.
Study Area
This work was carried out behind the College of Science,
Federal University of Petroleum Resources, Effurun,
Nigeria. Table 1 shows the location of the study area. The
area lies within Longitude 050 50’ 31.4” – 050 50’ 31.5” E
and Latitude 050 34’ 14.0” – 050 34’ 14.5” N. The average
elevation in these areas is about 9 m above sea level.
Figures 1 and 2 show the contour map and surface map
respectively of the study area. The area is slightly flat as
the area was sand filled. Figure 3 shows the geological
map of the study area.
Table 1: Latitude, Longitude and Elevation of the Study area
Latitude Longitude Elevation (m)
VES 1 050 34’ 13.6” N 0050 50’ 31.3” E 9.5
VES 2 050 34’ 14.0” N 0050 50’ 31.4” E 9.0
VES 3 050 34’ 14.0” N 0050 50’ 31.4” E 9.0
VES 4 050 34’ 14.2” N 0050 50’ 31.5” E 9.0
VES 5 050 34’ 14.3” N 0050 50’ 31.4” E 9.5
Figure 1: Contour Map of the Study Area Figure 2: Surface Map of the Study Area
5.76 5.78 5.8 5.82 5.84 5.86 5.88 5.9 5.92 5.94
Longitude
5.48
5.5
5.52
5.54
5.56
5.58
5.6
5.62
5.64
5.66
Latitude
0 0.05 0.1 0.15 0.2
9.2
9.25
9.3
9.35
9.4
9.45
9.5
9.55
9.6
9.65
0 0.1 0.2 0.3 0.4
Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria
Int. J. Geol. Min. 143
Figure 3: Geologic map of the western Niger Delta showing location of Effurun-Warri
Metropolis (Akpoborie et al., 2015)
Climate, Geology and Hydrogeology of the Study Area
Climate
The study area enjoys a hot (230C - 370C) and humid
(Relative Humidity, 50 - 70 per cent) equatorial climate with
a dry season that extends from about November to
February, and a wet season that begins in March, peaks
in July and October. 30-year mean annual rainfall is 3000
mm (Akpoborie et al., 2015).
Geology of Niger Delta
The Niger Delta is situated in the Gulf of Guinea and
extends throughout the Niger Delta Province as defined by
Klett et. al., (1997). From the Eocene to the present, the
delta has prograded south-westward, forming depobelts
that represent the most active portion of the delta at each
stage of its development. These depobelts form one of the
largest regressive deltas in the world with an area of some
300,000 km2, a sediment volume of 500,000 km3 and a
sediment thickness of over 10 km in the basin depocenter
(Akpoborie, 2015).
Warri town is underlain by a sequence of sedimentary
formations with a thickness of about 8000 m, which include
from bottom to top, the Akata Formation, the Agbada
Formation, the Benin Formation and the Somebreiro Warri
Deltaic Plain Sands (Israel, 2012).
Hydrogeology
Local hydrogeological setting indicates that Warri is
underlain by the Somebreiro-Warri Plain Sands aquifer
which consists of fine to medium and coarse grained
unconsolidated sands, gravels and. shales. The aquifer in
most cases unconfined, has thickness that ranges from 60
to 95 m (Israel, 2012; Ariyo and Adeyemi, 2005).
MATERIALS AND METHODS
Geophysical resistivity techniques are based on the
response of the earth to the flow of electrical current. With
an electrical current passed through the ground and two
potential electrodes to record the resultant potential
difference between them, we can obtain a direct measure
of the electrical impedance of the subsurface material. The
resistivity of the subsurface, a material constant, is then a
function of the magnitude of the current, the recorded
potential difference, and the geometry of the electrode
array. Depending upon the survey geometry, the data are
plotted as 1-D sounding or profiling curves, or in 2-D cross-
section in order to look for anomalous regions. In the
shallow subsurface, the presence of water controls much
of the conductivity variation. Measurement of resistivity is,
in general, a measure of water saturation and connectivity
of pore space. Resistivity measurements are associated
Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria
Bello R. 144
with varying depths relative to the distance between the
current and potential electrodes in the survey, and can be
interpreted qualitatively and quantitatively in terms of a
lithologic and/or geohydrologic model of the subsurface.
VES survey can be used to determine aquifer parameters
and fresh groundwater formation below
ground surface. Vertical electric sounding (VES) employs
collinear arrays designed to output a 1-D vertical apparent
resistivity versus depth model of the subsurface at a
specific observation point. In this method a series of
potential differences are acquired at successively greater
electrode spacing while maintaining a fixed central
reference point. The induced current passes through
progressively deeper layers at greater electrode spacing.
The potential difference measurements are directly
proportional to the changes in the deeper subsurface.
Apparent resistivity values calculated from measured
potential differences can be interpreted in terms of
overburden thickness, water table depth, and the depths
and thicknesses of subsurface strata. The two most
common arrays used for VES are the Wenner array and
the Schlumberger array (Steve, 2017).
The geophysical method used in this work is the VES. For
adequate depth penetration, the Schlumberger electrode
configuration was used with maximum current electrode
separation (AB) of 120 m.
A total of five VES using Schlumberger configuration were
carried out in the study area in order to investigate the
aquifer characteristics, aquifer protective capacity and
groundwater potential of the subsurface layer. The field
data was interpreted using IPI2win and interpex softwares.
The depth and resistivity of the surface layers were
determined (Hadi, 2009). These surveys were performed
to also get information regarding potential of groundwater
resources in the area, thickness of fresh groundwater
layers and soil layering below the ground surface.
Resistivity, the inverse of electrical conductivity, is the
resistance of the geologic medium offered to current flow
when a potential difference is applied,
R=V/I 1
where R is resistance in ohms (Ω), V is voltage in Volt, I is
current in Ampere. For resistivity surveys, a direct current
was applied through ground surface between two metal
electrodes A and B. The voltage loss that occurs as the
current moves through the ground was measured at the
potential electrodes M and N placed in between the current
electrodes (figure 3). Resistivity values were measured
using electrical sounding for vertical exploration. In this
procedure, a series of stations were established and
careful depth soundings were taken. Resistivity survey
was conducted at the site using resistivity meter (ABEM
SAS 4000) (Hafiz and Allah, 2015).
Figure 3: Two current and two potential electrodes on the
surface of homogeneous isotropic ground of resistivity 𝜌
Correlation between the layer lithology and VES is
achieved by correlating the resistivity values with the
standard values of resistivity as shown in Table 2.
Table 2: Resistivity of common geologic materials.
Materials Normal Resistivity (Ω𝑚)
Ash 4
Laterite 800 – 1500
Lateritic Soil 120 – 750
Gravel (Dry) 1400
Gravel Saturated) 100
Dry sandy Soil 80 – 1050
Sand Clay/Clayed Sand 30 – 215
Sand and Gravel 30 – 225
Saturated Landfill 15 – 30
Glacier Ice (Temperate) 2 x 106 – 1.2 x 108
Glacier Ice (Polar) 5 x 104 – 3 x 105
Permafrost 103 - > 104
Source: AbdulRahim et al., 2016.
A multilayer resistivity interpreted model consists of layer
apparent resistivities, thickness and depth. Further
derivatives are convolved to generate the geoelectric
parameters. These show electric boundaries separating
layers of different resistivity (Zohdy et al., 1990). A
geoelectric layer is described by two fundamental
parameters: its layer apparent resistivity (𝜌a) and its
thickness (h). The geoelectric parameters derived based
apparent resistivity and thickness,
Longitudinal conductance (S)
The longitudinal conductance (S) is the geoelectric
parameter used to define target areas of groundwater
potential. High S values usually indicate relatively thick
succession and should be accorded the highest priority in
terms of groundwater potential (Olusegun et al., 2016).
S = h/𝜌a
2
Where S is the longitudinal conductance, h is thickness
and ρa is apparent resistivity of the aquiferous layer.
Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria
Int. J. Geol. Min. 145
Transverse resistance (R)
The transverse resistance (R) is one of the parameters
used to define target areas of good groundwater potential.
It has a direct relation with transmissivity and the highest
R values reflect most likely the highest transmissivity
values of the aquifers or aquiferous zones.
R = h.𝜌a 3
Where R is the transverse resistance, h is thickness and
ρa is apparent resistivity of the aquiferous layer. The
parameters R and S were named the “Dar – Zarrouk
parameters“ by Maillet (1947).
The concept of Dar Zarrouk parameters was first proposed
by Maillet (1947). This postulation holds from the fact that,
when the thickness and resistivity of a lithologic
subsurface layer is known, its transverse resistance (R)
and longitudinal conductance (S) can be calculated easily.
Hence their correlative resistivities determined. Dar –
Zarrouk parameters have since been used in the
estimation/study of the hydraulic properties of aquifers
(Austin and Gabriel, 2015).
RESULTS AND DISCUSSION
The analyses of the VES survey data were made using the
computer software IP12win and Interpex. The summary of
resistivity and thicknesses of the geo-electric/lithology
layers within the subsurface are presented in table 3. Table
4 shows the longitudinal conductance and the transverse
resistance of the aquifer, while the aquifer protective
capacity as modified by Olusegun et al., (2016) are
presented in table 5. The iterative curves generated for the
apparent resistivity data using IPI2win and interpex
software are presented in figures 5 – 9 for the VES carried
out in this study. The geo-electric section for the study area
is presented in figure 10.
Figure 5: VES Curve for Traverse 1
Figure 6: VES Curve for Traverse 2
Figure 7: VES Curve for Traverse 3
Figure 8: VES Curve for Traverse 4
1 10 100
1000
4
10
T raverse 1
ApparentResistivity(Ohm-m)
A B /2 (m )
100 1000
4
10
5
10
0.1
1
10
Depth(m)
R esistivity (O hm-m )
Unregistered Version
1 10 100
100
1000
4
10
traverse 2
ApparentResistivity(Ohm-m)
A B /2 (m )
1 10 100
100
1000
4
10
T raverse 3
ApparentResistivity(Ohm-m)
A B /2 (m )
1 10 100
1000
4
10
T raverse 4
ApparentResistivity(Ohm-m)
A B /2 (m )
Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria
Bello R. 146
Figure 9: VES Curve for Traverse 5 Figure 10: Geoelectric Section for the Five VES
Figure 11: Contour Map of the Aquifer Protective Capacity
1 10 100
100
1000
4
10
T raverse 5
ApparentResistivity(Ohm-m)
A B /2 (m )
100 1000
4
10
5
10
6
10
0.1
1
10
100
Depth(m) R esistivity (O hm -m )
U nregistered V ersion
5.35 5.4 5.45 5.5 5.55 5.6 5.65 5.7 5.75 5.8 5.85 5.9 5.95 6
Longitude
5.3
5.35
5.4
5.45
5.5
5.55
5.6
5.65
5.7
5.75
5.8
5.85
5.9
5.95
Latitude
0 0.1 0.2 0.3 0.4
Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria
Int. J. Geol. Min. 147
Figure 12: Surface Map of the Aquifer Protective Capacity
Table 3: Summary Table for the Vertical Electrical
Sounding Interpretation
VES 1 VES 2
𝜌 𝑎 (Ω𝑚) h (m) Depth
(m)
Remarks 𝜌 𝑎 (Ω𝑚) h (m) Depth
(m)
Remarks
Layer
1
1659.7 0.46 0.46 3023.2 0.62 0.62
Layer
2
768.0 0.24 0.70 371.5 0.61 1.23
Layer
3
1080.9 1.81 2.51 3964.3 3.01 4.24
Layer
4
777.4 5.06 7.57 220.5 8.06 12.30
Layer
5
36214.0 - - 69143.0 - -
VES 3 VES 4
Layer
1
3192.3 1.05 1.05 1457.8 0.21 0.21
Layer
2
5967.3 1.49 2.54 2348.2 3.81 4.02
Layer
3
811.4 8.17 10.71 720.1 14.96 18.98
Layer
4
625.1 15.41 26.12 3219.7 - -
Layer
5
3931.0 - - - - -
VES 5
Layer
1
2260.3 0.19 0.19
Layer
2
2676.9 3.52 3.71
Layer
3
666.5 18.85 22.56
Layer
4
44064.0 - -
Layer
5
- - -
Table 4: Table Showing Longitudinal Conductance and
Transverse Resistance of the Aquifer
h (m) 𝜌 𝑎 (Ω𝑚) Longitudinal
Conductance
Transverse
Resistance
VES 1 5.063 777.40 0.0065 3935.98
VES 2 8.062 220.45 0.0370 1777.27
VES 3 15.420 625.05 0.0250 9638.27
VES 4 14.960 720.13 0.0210 10,773.15
VES 5 18.850 666.51 0.0280 12,563.71
Table 5: Table showing Aquifer protective Capacity Rating
(Olusegun et al., 2016)
Rating Remarks
Greater than 10 Excellent
5 t0 10 Very Good
0.2 to 4.9 Moderate
0.1 to 0.19 Weak
Less than 0.1 Poor
Figure 5 shows that VES 1 is HKH curve. The curve
revealed five resistivity layers for VES 1. The first layer
which is the top soil has resistivity value of 1659.7 Ωm. It
is thought that the survey area being semi-swamp area
was sand filled with sandy soil. The layer has thickness of
0.46 m. This was followed by another layer of resistivity
768.0 Ωm. This layer has a thickness of 0.24 m. This layer
is interpreted to be sandy clay. The third layer has a
resistivity of 1080.9 Ωm. This layer has a thickness 0f 1.81
m and interpreted to be fine-medium sand. The fourth layer
has a resistivity value of 777.4 Ωm with a thickness of
0 0.1 0.2 0.3 0.4
0.01
0.012
0.014
0.016
0.018
0.02
0.022
0.024
0.026
0.028
0.03
Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria
Bello R. 148
5.06m. This layer is interpreted to be coarse sand and the
layer constitute the aquifer. Underlain the fourth layer is
the fifth layer having resistivity of 36214.0 Ωm with an
infinite thickness. This layer is interpreted to contain fine-
medium sand.
Figure 6 shows that VES 2 is typically HKH curve. The
curve also revealed five resistivity layers for VES 2. The
first layer which is the top soil has resistivity of 3023.2 Ωm
with a thickness of 0.62 m. The second layer has resistivity
of 371.5 Ωm with a thickness of 0.62 m. This layer is
interpreted to be sandy clay. The third layer has a
resistivity of 3964.3 Ωm with a thickness of 3.01 m. This
layer is interpreted to contain fine-medium sand. Underlain
this layer is the fourth layer with a resistivity of 220.45 Ωm
with a thickness of 8.06 m. This layer is interpreted to be
sand and the layer constitute the aquifer. The fifth layer
has a resistivity value of 69143.0 Ωm with a infinite
thickness. This layer is interpreted to contain fine-medium
sand.
Figure 7 shows that VES 3 is typically KQH curve. The
curve also revealed five resistivity layers for VES 3. The
first layer which is the top soil has resistivity value of
3192.3 Ωm with a thickness of 1.05 m. This layer is
underlain by the second layer having resistivity value of
5967.3 Ωm with a thickness of 1.49 m. This layer is
interpreted to be fine-medium sand. The third layer has a
resistivity value of 811.4 Ωm with a thickness of 8.12 m.
This layer is interpreted to be clayed sand. The fourth layer
has a resistivity value of 625.1 Ωm with a thickness of
15.41 m. This layer is interpreted to be coarse sand and
the layer constitute the aquifer. The fifth layer has a
resistivity value of 3931.0 Ωm with an infinite thickness.
This layer is interpreted to contain fine-medium sand.
VES4 exhibit typical KH curve as shown in figure 8. The
curve revealed four resistivity layers. The first layer which
is the top soil has resistivity value of 1457.8 Ωm with a
thickness of 0.21 m. This layer is underlain by the second
layer with resistivity value of 2348.2 m with a thickness of
3.81 m. This layer is interpreted to be fine-medium sand.
The third layer has resistivity value of 720.1 Ωm with a
thickness of 14.96 m. This layer is interpreted to be coarse
sand and the layer constitute the aquifer. The fourth layer
has resistivity value of 3219.7 Ωm with an infinite
thickness. This layer is interpreted to contain fine-medium
sand.
Figure 9 shows that VES 5 exhibit typical KH curve. The
curve revealed four resistivity layers. The first layer which
is the top soil has resistivity value of 2260.3 Ωm with a
thickness of 0.19 m. The layer is underlain by the second
layer with resistivity value of 2676.9 Ωm with a thickness
of 3.52 m. This layer is interpreted to be fine-medium sand.
The third layer has a resistivity value of 666.5 Ωm with a
thickness of 18.85 m. This layer is interpreted to be coarse
sand and the layer constitute the aquifer. The fourth layer
has resistivity value of 44064.0 Ωm with an infinite
thickness. This layer is interpreted to contain fine-medium
sand.
The aquifer protective capacity was determined using the
parameters longitudinal conductance and transverse
resistance presented in table 5. The parameters were
calculated using equations 2 and 3. Using the results
obtained from the study area presented in table 3,
estimation of the aquifer longitudinal conductance and
transverse resistance were made and presented in table
4. The contour map of the aquifer protective capacity is
shown in figure 11 while figure 12 shows the surface map
of the aquifer protective capacity for the study area. The
result shows that all the aquifers in VES 1, VES 2, VES 3,
VES 4 and VES 5 show evidence of poor aquifer protective
capacity having longitudinal conductance values ranging
from 0.0065 to 0.037 and transverse resistance values
ranging from 1,777.27 to 12,563.71. The aquifer in this
area may be prone to contamination resulting from short
residence time in the coarse sand layers. The thicknesses
of the overlain layers for the aquifers are not enough to
protect the aquifers from percolating fluids. The
thicknesses of the overlain layers range from 2.5 m to
maximum of 4.25 m except in VES 3 where the thickness
is up to 10.71 m. Usually, groundwater is given protection
by geologic barriers having sufficient thickness and also
called protective layers and low hydraulic conductivity.
Silts and clays are suitable protective layers and when they
are found as thick layers above aquifer, they constitute a
protective cover (Olusegun et al., 2016). However, this is
not the case for this study.
CONCLUSION
This study investigated the groundwater potential and
aquifer protective capacity of an area behind the College
of Science, Federal University of Petroleum Resources,
Effurun, Nigeria. Five VES using the Schlumberger array
configuration were acquired in the study area. Analysis
and interpretation of VES data obtained from the study
area showed VES 3, VES 4 and VES 5 to be most
appropriate locations to be explored for borehole
development due to low resistivity of the porous and
permeable sand in the aquiferous layers coupled with the
relatively high thicknesses of the sandy layers. However,
all the aquifers in the VES locations are poorly protected
due to the very low aquifer protective capacity parameters
in the VES locations.
It is therefore recommended that for future groundwater
development in the study area, measures should be taken
to ensure treatment of groundwater that may be explored
from the area to make it fit for domestic use.
Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria
Int. J. Geol. Min. 149
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Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria
Bello R. 150
Zohdy AAR, Eaton GP, Mabey DR (1990). Application of
surface Geophysics to ground – water investigation”.
USGS publications. 4th Edition. Pp116.
Accepted 30 October 2017,
Citation: Bello R. (2017). Investigation of Groundwater
Potential and Aquifer Protective Capacity of Part of
Effurun, Delta State, Nigeria. International Journal
Geology and Mining 3(3): 141-150.
Copyright: © 2017 Bello R. This is an open-access article
distributed under the terms of the Creative Commons
Attribution License, which permits unrestricted use,
distribution, and reproduction in any medium, provided the
original author and source are cited.

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Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria

  • 1. Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria IJGM Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria Bello Rasaq Department of Physics, University of Port Harcourt, Port Harcourt, Nigeria Tel.: +234(0)8036684498; Email: rasaq.bello@uniport.edu.ng The aim of this study was to investigate groundwater potential and aquifer protective capacity of an area behind the College of Science, Federal University of Petroleum Resources, Effurun-Warri area of Delta State, Nigeria. The data was acquired using ABEM SAS 4000 Terrameter and processed using IPI2win and Interpex software. Five Vertical Electrical Soundings were carried out with maximum current electrode separation (AB) of 120 m. The VES curves generated from the data revealed HKH curve type for VES 1 and VES 2, KQH curve for VES 3 and KH curve for VES 4 and 5. Five resistivity layers were identified for VES 1 - 3 while four resistivity layers were identified for VES 4 – 5. Analysis and interpretation of VES data obtained from the study area showed VES 3, VES 4 and VES 5 to be most appropriate locations to be explored for borehole development due to low resistivity of the weathered/fractured aquiferous layers coupled with the relatively high thicknesses of the weathered layers. However, all the aquifers in the VES locations are poorly protected due to the very low aquifer protective capacity parameters in the VES locations. Keywords: Aquifer, Resistivity, Vertical Electrical Sounding, Groundwater, Protective Capacity INTRODUCTION Aquifer protection is essential for a sustainable use of the groundwater resources, protection of the dependent ecosystems, and a central part of spatial planning and action plans Egbai et al., 2015). The key expression for a quantification of aquifer protection is vulnerability. Aquifer vulnerability solely indicates whether the physical and biochemical characteristics of the subsurface prevent or favour the transport of pollutants in and into aquifers. It does not take into account the actual pollutant loading in an area. Transmissivity is a major property of an aquifer and aids in the characterization of rocks as water conducting media/strata. The ability of the overburden to retard and filter percolating fluid is a measure of its protective capacity. Estimating these properties from pumping tests can be very expensive and time consuming. Surface geoelectrical methods offer an alternative, rapid and cost- effective approach for aquifer evaluation and groundwater quality assessment using empirical relations between hydraulic and geoelectric parameters (Ehirim and Nwakwo, 2010). Poor quality water and inadequate water supply have accounted for a number of preventable diseases in many communities across the world. These factors have also affected agriculture in terms of the types of crops grown and yield as well as animals (Anomohanran, 2014). According to Anomohanran (2013), pollution has continued to make good quality water unavailable for use despite the fact that nature has endowed the world with so much water. Groundwater is contributing significantly in the development of agricultural economy and domestic water usage. Groundwater is the water that fills all pores and International Journal Geology and Mining Vol. 3(3), pp. 141-150, November, 2017. © www.premierpublishers.org. ISSN: XXXX-XXXX Research Article
  • 2. Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria Bello R. 142 openings within the zone of saturation. Exploration for groundwater in sedimentary environments involves locating formations that possess appropriate porosity and permeability. While the location of permeable clean sands that are capable of yielding useful quantities of water to wells is important, the quality of water yielded is also crucial (Aweto, 2014). The Niger Delta is endowed with rich groundwater resources in several aquifers, but unfortunately, the public water supply by State Water Agency is inadequate and unable to satisfy the demanded quantities (Akpoborie et al., 2000) and consumers must make alternative arrangements. These arrangements in most cases consist of hand dug wells or relatively cheaper shallow boreholes that are constructed with the aid of augers operated manually. These boreholes are usually slightly deeper than the dug wells but also exploit the shallow aquifers that are the most susceptible to contamination from various sources. According to Tijani et al., (2002), one of the commonest ways of waste disposal in the Niger Delta is by open dumping. The primary environmental consequence of these indiscriminate dumping of waste in open dump is the generation of leachates due to decomposition of the waste materials. The leachates are subsequently released into the groundwater by infiltration and this poses serious environmental problems including health hazard. Surface geophysical survey as a veritable tool in groundwater exploration, has the basic advantage of saving cost in borehole construction by locating target aquifer before drilling is embarked upon (Obiora and Ownuka, 2005). The vertical electrical sounding (VES) survey used in this work has been used extensively for location of the aquifer and determining their hydraulic parameters because the instrument is simple and analysis of the data is easy and less tedious than other methods (Lashkaripour et al., 2005; Batayaneh, 2007; Sikandar et al., 2009; Anomohanran, 2013; Anomohanran, 2014). VES method with Schlumberger array assumes considerable importance in the field of groundwater exploration because of its ease of operation, low cost and its capability to distinguish between saturated and unsaturated layers. This method is regularly used to solve a wide variety of groundwater problems such as determination of depth, thickness and boundary of aquifer, determination of zones with high yield potential in an aquifer, determination of the boundary between saline and fresh water zones and estimation of aquifer transmissivity (Hadi, 2009). Therefore, the aim of this study is to investigate the aquifer systems in order to provide information about the subsurface layers of the area using geophysical tools and also to determine the aquifer protective capacity of the study area. Study Area This work was carried out behind the College of Science, Federal University of Petroleum Resources, Effurun, Nigeria. Table 1 shows the location of the study area. The area lies within Longitude 050 50’ 31.4” – 050 50’ 31.5” E and Latitude 050 34’ 14.0” – 050 34’ 14.5” N. The average elevation in these areas is about 9 m above sea level. Figures 1 and 2 show the contour map and surface map respectively of the study area. The area is slightly flat as the area was sand filled. Figure 3 shows the geological map of the study area. Table 1: Latitude, Longitude and Elevation of the Study area Latitude Longitude Elevation (m) VES 1 050 34’ 13.6” N 0050 50’ 31.3” E 9.5 VES 2 050 34’ 14.0” N 0050 50’ 31.4” E 9.0 VES 3 050 34’ 14.0” N 0050 50’ 31.4” E 9.0 VES 4 050 34’ 14.2” N 0050 50’ 31.5” E 9.0 VES 5 050 34’ 14.3” N 0050 50’ 31.4” E 9.5 Figure 1: Contour Map of the Study Area Figure 2: Surface Map of the Study Area 5.76 5.78 5.8 5.82 5.84 5.86 5.88 5.9 5.92 5.94 Longitude 5.48 5.5 5.52 5.54 5.56 5.58 5.6 5.62 5.64 5.66 Latitude 0 0.05 0.1 0.15 0.2 9.2 9.25 9.3 9.35 9.4 9.45 9.5 9.55 9.6 9.65 0 0.1 0.2 0.3 0.4
  • 3. Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria Int. J. Geol. Min. 143 Figure 3: Geologic map of the western Niger Delta showing location of Effurun-Warri Metropolis (Akpoborie et al., 2015) Climate, Geology and Hydrogeology of the Study Area Climate The study area enjoys a hot (230C - 370C) and humid (Relative Humidity, 50 - 70 per cent) equatorial climate with a dry season that extends from about November to February, and a wet season that begins in March, peaks in July and October. 30-year mean annual rainfall is 3000 mm (Akpoborie et al., 2015). Geology of Niger Delta The Niger Delta is situated in the Gulf of Guinea and extends throughout the Niger Delta Province as defined by Klett et. al., (1997). From the Eocene to the present, the delta has prograded south-westward, forming depobelts that represent the most active portion of the delta at each stage of its development. These depobelts form one of the largest regressive deltas in the world with an area of some 300,000 km2, a sediment volume of 500,000 km3 and a sediment thickness of over 10 km in the basin depocenter (Akpoborie, 2015). Warri town is underlain by a sequence of sedimentary formations with a thickness of about 8000 m, which include from bottom to top, the Akata Formation, the Agbada Formation, the Benin Formation and the Somebreiro Warri Deltaic Plain Sands (Israel, 2012). Hydrogeology Local hydrogeological setting indicates that Warri is underlain by the Somebreiro-Warri Plain Sands aquifer which consists of fine to medium and coarse grained unconsolidated sands, gravels and. shales. The aquifer in most cases unconfined, has thickness that ranges from 60 to 95 m (Israel, 2012; Ariyo and Adeyemi, 2005). MATERIALS AND METHODS Geophysical resistivity techniques are based on the response of the earth to the flow of electrical current. With an electrical current passed through the ground and two potential electrodes to record the resultant potential difference between them, we can obtain a direct measure of the electrical impedance of the subsurface material. The resistivity of the subsurface, a material constant, is then a function of the magnitude of the current, the recorded potential difference, and the geometry of the electrode array. Depending upon the survey geometry, the data are plotted as 1-D sounding or profiling curves, or in 2-D cross- section in order to look for anomalous regions. In the shallow subsurface, the presence of water controls much of the conductivity variation. Measurement of resistivity is, in general, a measure of water saturation and connectivity of pore space. Resistivity measurements are associated
  • 4. Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria Bello R. 144 with varying depths relative to the distance between the current and potential electrodes in the survey, and can be interpreted qualitatively and quantitatively in terms of a lithologic and/or geohydrologic model of the subsurface. VES survey can be used to determine aquifer parameters and fresh groundwater formation below ground surface. Vertical electric sounding (VES) employs collinear arrays designed to output a 1-D vertical apparent resistivity versus depth model of the subsurface at a specific observation point. In this method a series of potential differences are acquired at successively greater electrode spacing while maintaining a fixed central reference point. The induced current passes through progressively deeper layers at greater electrode spacing. The potential difference measurements are directly proportional to the changes in the deeper subsurface. Apparent resistivity values calculated from measured potential differences can be interpreted in terms of overburden thickness, water table depth, and the depths and thicknesses of subsurface strata. The two most common arrays used for VES are the Wenner array and the Schlumberger array (Steve, 2017). The geophysical method used in this work is the VES. For adequate depth penetration, the Schlumberger electrode configuration was used with maximum current electrode separation (AB) of 120 m. A total of five VES using Schlumberger configuration were carried out in the study area in order to investigate the aquifer characteristics, aquifer protective capacity and groundwater potential of the subsurface layer. The field data was interpreted using IPI2win and interpex softwares. The depth and resistivity of the surface layers were determined (Hadi, 2009). These surveys were performed to also get information regarding potential of groundwater resources in the area, thickness of fresh groundwater layers and soil layering below the ground surface. Resistivity, the inverse of electrical conductivity, is the resistance of the geologic medium offered to current flow when a potential difference is applied, R=V/I 1 where R is resistance in ohms (Ω), V is voltage in Volt, I is current in Ampere. For resistivity surveys, a direct current was applied through ground surface between two metal electrodes A and B. The voltage loss that occurs as the current moves through the ground was measured at the potential electrodes M and N placed in between the current electrodes (figure 3). Resistivity values were measured using electrical sounding for vertical exploration. In this procedure, a series of stations were established and careful depth soundings were taken. Resistivity survey was conducted at the site using resistivity meter (ABEM SAS 4000) (Hafiz and Allah, 2015). Figure 3: Two current and two potential electrodes on the surface of homogeneous isotropic ground of resistivity 𝜌 Correlation between the layer lithology and VES is achieved by correlating the resistivity values with the standard values of resistivity as shown in Table 2. Table 2: Resistivity of common geologic materials. Materials Normal Resistivity (Ω𝑚) Ash 4 Laterite 800 – 1500 Lateritic Soil 120 – 750 Gravel (Dry) 1400 Gravel Saturated) 100 Dry sandy Soil 80 – 1050 Sand Clay/Clayed Sand 30 – 215 Sand and Gravel 30 – 225 Saturated Landfill 15 – 30 Glacier Ice (Temperate) 2 x 106 – 1.2 x 108 Glacier Ice (Polar) 5 x 104 – 3 x 105 Permafrost 103 - > 104 Source: AbdulRahim et al., 2016. A multilayer resistivity interpreted model consists of layer apparent resistivities, thickness and depth. Further derivatives are convolved to generate the geoelectric parameters. These show electric boundaries separating layers of different resistivity (Zohdy et al., 1990). A geoelectric layer is described by two fundamental parameters: its layer apparent resistivity (𝜌a) and its thickness (h). The geoelectric parameters derived based apparent resistivity and thickness, Longitudinal conductance (S) The longitudinal conductance (S) is the geoelectric parameter used to define target areas of groundwater potential. High S values usually indicate relatively thick succession and should be accorded the highest priority in terms of groundwater potential (Olusegun et al., 2016). S = h/𝜌a 2 Where S is the longitudinal conductance, h is thickness and ρa is apparent resistivity of the aquiferous layer.
  • 5. Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria Int. J. Geol. Min. 145 Transverse resistance (R) The transverse resistance (R) is one of the parameters used to define target areas of good groundwater potential. It has a direct relation with transmissivity and the highest R values reflect most likely the highest transmissivity values of the aquifers or aquiferous zones. R = h.𝜌a 3 Where R is the transverse resistance, h is thickness and ρa is apparent resistivity of the aquiferous layer. The parameters R and S were named the “Dar – Zarrouk parameters“ by Maillet (1947). The concept of Dar Zarrouk parameters was first proposed by Maillet (1947). This postulation holds from the fact that, when the thickness and resistivity of a lithologic subsurface layer is known, its transverse resistance (R) and longitudinal conductance (S) can be calculated easily. Hence their correlative resistivities determined. Dar – Zarrouk parameters have since been used in the estimation/study of the hydraulic properties of aquifers (Austin and Gabriel, 2015). RESULTS AND DISCUSSION The analyses of the VES survey data were made using the computer software IP12win and Interpex. The summary of resistivity and thicknesses of the geo-electric/lithology layers within the subsurface are presented in table 3. Table 4 shows the longitudinal conductance and the transverse resistance of the aquifer, while the aquifer protective capacity as modified by Olusegun et al., (2016) are presented in table 5. The iterative curves generated for the apparent resistivity data using IPI2win and interpex software are presented in figures 5 – 9 for the VES carried out in this study. The geo-electric section for the study area is presented in figure 10. Figure 5: VES Curve for Traverse 1 Figure 6: VES Curve for Traverse 2 Figure 7: VES Curve for Traverse 3 Figure 8: VES Curve for Traverse 4 1 10 100 1000 4 10 T raverse 1 ApparentResistivity(Ohm-m) A B /2 (m ) 100 1000 4 10 5 10 0.1 1 10 Depth(m) R esistivity (O hm-m ) Unregistered Version 1 10 100 100 1000 4 10 traverse 2 ApparentResistivity(Ohm-m) A B /2 (m ) 1 10 100 100 1000 4 10 T raverse 3 ApparentResistivity(Ohm-m) A B /2 (m ) 1 10 100 1000 4 10 T raverse 4 ApparentResistivity(Ohm-m) A B /2 (m )
  • 6. Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria Bello R. 146 Figure 9: VES Curve for Traverse 5 Figure 10: Geoelectric Section for the Five VES Figure 11: Contour Map of the Aquifer Protective Capacity 1 10 100 100 1000 4 10 T raverse 5 ApparentResistivity(Ohm-m) A B /2 (m ) 100 1000 4 10 5 10 6 10 0.1 1 10 100 Depth(m) R esistivity (O hm -m ) U nregistered V ersion 5.35 5.4 5.45 5.5 5.55 5.6 5.65 5.7 5.75 5.8 5.85 5.9 5.95 6 Longitude 5.3 5.35 5.4 5.45 5.5 5.55 5.6 5.65 5.7 5.75 5.8 5.85 5.9 5.95 Latitude 0 0.1 0.2 0.3 0.4
  • 7. Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria Int. J. Geol. Min. 147 Figure 12: Surface Map of the Aquifer Protective Capacity Table 3: Summary Table for the Vertical Electrical Sounding Interpretation VES 1 VES 2 𝜌 𝑎 (Ω𝑚) h (m) Depth (m) Remarks 𝜌 𝑎 (Ω𝑚) h (m) Depth (m) Remarks Layer 1 1659.7 0.46 0.46 3023.2 0.62 0.62 Layer 2 768.0 0.24 0.70 371.5 0.61 1.23 Layer 3 1080.9 1.81 2.51 3964.3 3.01 4.24 Layer 4 777.4 5.06 7.57 220.5 8.06 12.30 Layer 5 36214.0 - - 69143.0 - - VES 3 VES 4 Layer 1 3192.3 1.05 1.05 1457.8 0.21 0.21 Layer 2 5967.3 1.49 2.54 2348.2 3.81 4.02 Layer 3 811.4 8.17 10.71 720.1 14.96 18.98 Layer 4 625.1 15.41 26.12 3219.7 - - Layer 5 3931.0 - - - - - VES 5 Layer 1 2260.3 0.19 0.19 Layer 2 2676.9 3.52 3.71 Layer 3 666.5 18.85 22.56 Layer 4 44064.0 - - Layer 5 - - - Table 4: Table Showing Longitudinal Conductance and Transverse Resistance of the Aquifer h (m) 𝜌 𝑎 (Ω𝑚) Longitudinal Conductance Transverse Resistance VES 1 5.063 777.40 0.0065 3935.98 VES 2 8.062 220.45 0.0370 1777.27 VES 3 15.420 625.05 0.0250 9638.27 VES 4 14.960 720.13 0.0210 10,773.15 VES 5 18.850 666.51 0.0280 12,563.71 Table 5: Table showing Aquifer protective Capacity Rating (Olusegun et al., 2016) Rating Remarks Greater than 10 Excellent 5 t0 10 Very Good 0.2 to 4.9 Moderate 0.1 to 0.19 Weak Less than 0.1 Poor Figure 5 shows that VES 1 is HKH curve. The curve revealed five resistivity layers for VES 1. The first layer which is the top soil has resistivity value of 1659.7 Ωm. It is thought that the survey area being semi-swamp area was sand filled with sandy soil. The layer has thickness of 0.46 m. This was followed by another layer of resistivity 768.0 Ωm. This layer has a thickness of 0.24 m. This layer is interpreted to be sandy clay. The third layer has a resistivity of 1080.9 Ωm. This layer has a thickness 0f 1.81 m and interpreted to be fine-medium sand. The fourth layer has a resistivity value of 777.4 Ωm with a thickness of 0 0.1 0.2 0.3 0.4 0.01 0.012 0.014 0.016 0.018 0.02 0.022 0.024 0.026 0.028 0.03
  • 8. Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria Bello R. 148 5.06m. This layer is interpreted to be coarse sand and the layer constitute the aquifer. Underlain the fourth layer is the fifth layer having resistivity of 36214.0 Ωm with an infinite thickness. This layer is interpreted to contain fine- medium sand. Figure 6 shows that VES 2 is typically HKH curve. The curve also revealed five resistivity layers for VES 2. The first layer which is the top soil has resistivity of 3023.2 Ωm with a thickness of 0.62 m. The second layer has resistivity of 371.5 Ωm with a thickness of 0.62 m. This layer is interpreted to be sandy clay. The third layer has a resistivity of 3964.3 Ωm with a thickness of 3.01 m. This layer is interpreted to contain fine-medium sand. Underlain this layer is the fourth layer with a resistivity of 220.45 Ωm with a thickness of 8.06 m. This layer is interpreted to be sand and the layer constitute the aquifer. The fifth layer has a resistivity value of 69143.0 Ωm with a infinite thickness. This layer is interpreted to contain fine-medium sand. Figure 7 shows that VES 3 is typically KQH curve. The curve also revealed five resistivity layers for VES 3. The first layer which is the top soil has resistivity value of 3192.3 Ωm with a thickness of 1.05 m. This layer is underlain by the second layer having resistivity value of 5967.3 Ωm with a thickness of 1.49 m. This layer is interpreted to be fine-medium sand. The third layer has a resistivity value of 811.4 Ωm with a thickness of 8.12 m. This layer is interpreted to be clayed sand. The fourth layer has a resistivity value of 625.1 Ωm with a thickness of 15.41 m. This layer is interpreted to be coarse sand and the layer constitute the aquifer. The fifth layer has a resistivity value of 3931.0 Ωm with an infinite thickness. This layer is interpreted to contain fine-medium sand. VES4 exhibit typical KH curve as shown in figure 8. The curve revealed four resistivity layers. The first layer which is the top soil has resistivity value of 1457.8 Ωm with a thickness of 0.21 m. This layer is underlain by the second layer with resistivity value of 2348.2 m with a thickness of 3.81 m. This layer is interpreted to be fine-medium sand. The third layer has resistivity value of 720.1 Ωm with a thickness of 14.96 m. This layer is interpreted to be coarse sand and the layer constitute the aquifer. The fourth layer has resistivity value of 3219.7 Ωm with an infinite thickness. This layer is interpreted to contain fine-medium sand. Figure 9 shows that VES 5 exhibit typical KH curve. The curve revealed four resistivity layers. The first layer which is the top soil has resistivity value of 2260.3 Ωm with a thickness of 0.19 m. The layer is underlain by the second layer with resistivity value of 2676.9 Ωm with a thickness of 3.52 m. This layer is interpreted to be fine-medium sand. The third layer has a resistivity value of 666.5 Ωm with a thickness of 18.85 m. This layer is interpreted to be coarse sand and the layer constitute the aquifer. The fourth layer has resistivity value of 44064.0 Ωm with an infinite thickness. This layer is interpreted to contain fine-medium sand. The aquifer protective capacity was determined using the parameters longitudinal conductance and transverse resistance presented in table 5. The parameters were calculated using equations 2 and 3. Using the results obtained from the study area presented in table 3, estimation of the aquifer longitudinal conductance and transverse resistance were made and presented in table 4. The contour map of the aquifer protective capacity is shown in figure 11 while figure 12 shows the surface map of the aquifer protective capacity for the study area. The result shows that all the aquifers in VES 1, VES 2, VES 3, VES 4 and VES 5 show evidence of poor aquifer protective capacity having longitudinal conductance values ranging from 0.0065 to 0.037 and transverse resistance values ranging from 1,777.27 to 12,563.71. The aquifer in this area may be prone to contamination resulting from short residence time in the coarse sand layers. The thicknesses of the overlain layers for the aquifers are not enough to protect the aquifers from percolating fluids. The thicknesses of the overlain layers range from 2.5 m to maximum of 4.25 m except in VES 3 where the thickness is up to 10.71 m. Usually, groundwater is given protection by geologic barriers having sufficient thickness and also called protective layers and low hydraulic conductivity. Silts and clays are suitable protective layers and when they are found as thick layers above aquifer, they constitute a protective cover (Olusegun et al., 2016). However, this is not the case for this study. CONCLUSION This study investigated the groundwater potential and aquifer protective capacity of an area behind the College of Science, Federal University of Petroleum Resources, Effurun, Nigeria. Five VES using the Schlumberger array configuration were acquired in the study area. Analysis and interpretation of VES data obtained from the study area showed VES 3, VES 4 and VES 5 to be most appropriate locations to be explored for borehole development due to low resistivity of the porous and permeable sand in the aquiferous layers coupled with the relatively high thicknesses of the sandy layers. However, all the aquifers in the VES locations are poorly protected due to the very low aquifer protective capacity parameters in the VES locations. It is therefore recommended that for future groundwater development in the study area, measures should be taken to ensure treatment of groundwater that may be explored from the area to make it fit for domestic use.
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  • 10. Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria Bello R. 150 Zohdy AAR, Eaton GP, Mabey DR (1990). Application of surface Geophysics to ground – water investigation”. USGS publications. 4th Edition. Pp116. Accepted 30 October 2017, Citation: Bello R. (2017). Investigation of Groundwater Potential and Aquifer Protective Capacity of Part of Effurun, Delta State, Nigeria. International Journal Geology and Mining 3(3): 141-150. Copyright: © 2017 Bello R. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are cited.