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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 02 | Feb 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1032
Impact of Poor Sanitation Infrastructure (Pit Latrine and Septic Tank)
on Hand-Dug Well and Borehole in Voinjama, Liberia
Prof. Dr. Huseyin Gokcekus1, Assco. Prof. Dr. Youssef Kasseme. Ph.D2, Larry T. Woyea3
1Department of Civil Engineering, Civil and Environmental Engineering Faculty,Near East University, Nicosia (Via
Mersin 10, Turkey), 99138 Cyprus
2Department of Mehanical Engineering, Engineering Faculty, Near East University, Nicosia, (Via Mersin 10,
Turkey), 99138 Cyprus
3Department of Environmental Engineering, Civil and Environmental Engineering Faculty, Near East University,
Nicosia, (Via Mersin 10, Turkey), 99138 Cyprus
---------------------------------------------------------------------***----------------------------------------------------------------------
Abstract - In many rural areas of Liberia safedrinkingwater
does not occur and wherever it does it is infrequently
unreliable, therefore, in these areas,residentsmainlyrely on
groundwater for living, and as such, it is common to find
individual wells in each cell of such a country house. In
addition, in most cases, these houses do not have the town`s
drainage system, forcing residents to build latrines or septic
tanks near their wells. This study aimed to determine the
level of contamination in the samples and to estimate the
effect instigated by the building of septic tanks and latrines
near groundwater in Voinjama, Liberia.Watersamples were
taken in triplicate from seven sampling points and
transported to the Liberia Water Supply and Sewerage
Cooperation Quality Laboratory (LWSC) in Voinjama for
analysis. The pH, nitrate, and nitrite intensities were
examined in the samples by spectrophotometry using a
colorimeter DR890 (Hach).Leadstageswereanalyzedby the
use of a DR 5000 spectrophotometer (Hach). Bacterial
analysis (E. coli and coliforms instool)becomecompleted by
the use of the Palintest kit (Hach) at the same time as
turbidity stages had been calculated by the use of a T100
turbidimeter (Oakton). Furthermore, microbiological
isolates had been recognized for the use of API 20E assay.
Results were compared with World Health Organization
(WHO) and Water Sanitation and Hygiene (WASH Liberia)
standards. Coliforms Faecal and E.coli were found in all,
however very excessive in wells closest to septic tanksorpit
latrines. The physicochemical factors (pH, turbidity, nitrite,
nitrate, lead) were all beneath the acceptable standard in all
analyzed samples. The study, therefore, concludes that the
location of the septic tanks negativelyaffectsthewatervalue
in the study area with more noticeable magnitudes at hand-
dug wells constructed very close to the septic tank or pit
latrine system.
Key Words: (Pit Latrines; Septic Tanks; Boreholes and
hand-dug well; Pollution, Measurement;contamination)
1. INTRODUCTION
In many rural areas of Liberia, safe drinking water does not
occur and where it does it is hardly unreliable, therefore, in
these zones, inhabitants mainly depend on groundwater for
living, and as such, it is mutual to find specific wells in each
cell of such a country house. In addition, in most cases, these
houses do not have the town`s drainage system, forcing
residents to build latrines or septic tanks near their wells.
Voinjama is the capital metropolis of Lofa County is
confronted with extreme demanding situations of securing
water for its people; which can be attributed to the terrible
sanitation infrastructures and shortage of technical tips
when constructing pit latrines, septic tanks, and hand-dug
wells. This rural metropolis additionally lacks sewer and
drainage structures making its population depend upon
personal connection through the developmentofpitlatrines
and septic tanks to deliver the sewage that'spoorlybuiltand
controlled thereby contaminating the groundwatersources.
This study aimed to determine the level of contamination in
the samples and to estimate the impact caused by the
construction of septic tanks and latrines near groundwater
in Voinjama, Liberia. The study area is positioned along the
hills of the northernmost tip of the country, close to the
Guinean border. According to the 2008 census, it has a
population of approximately 26,594. The residents in this
area rely on agriculture for their livelihood, particularly
growing rice. In this rural metropolis, there's no sewage
system to serve the populace, and as such, all residential,
industrial and public homes rely upon pit latrines andseptic
tanks for wastewater deposition.
Figure 1-Map of Study area (Voinjama)
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 02 | Feb 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1033
2. Methodology
A set of seven (7) water samples was taken from separate
sites in the rural town of Voinjama, Lofa County, Liberia. At
each specimen point, the size (distance) between the
manually dug well and the nearest septic tank or latrine,
including depth, was measured with a 50 m tape measure
and recorded. Seven rapid resamplings exceed the 30m
distance requirement recommended by the Liberian Water
and Sanitation Authority/MPW (WASH/MPW, 2010).
Samples were collected in easy 1.5 L flexible flasks, clearly
marked for clear identification, and stored in an insulated
container with an ice ratio before being shipped to our
laboratory substation in Liberia for analysis; samples were
examined within 24hrs of collection. The factors measured
during the study were pH, turbidity, nitrate, nitrite, lead,
general microbial count (TBC), and E.coli. The investigative
method used for every factor is indexed in Table 1.0.
Additionally, the microbiological isolates have been
identified by the use of the Analytical ProfileIndex(API20E)
assay created in the Seventies through Pierre Janin (Holmes
et al 1978).
Table 1.0 Investigative procedures and factors
Investigative procedure/
Equipment
Parameter Unit
Multi parameter (in-situ)-pH Meter PH
Absorptometric method (USEPA
8237)- Turbidity Meter (T100
Oakton)
Turbidity (NTU
Diazotization method (USEPA
8507)-DR 890 (Hach)
Nitrite (ppm)
Cadmium reduction (USEPA 8192)-
DR 890 (Hach)
Nitrate(ppm)
Flame Spectrophotometry – DR
5000 (Hach)
Lead (ppm)
Microbiological Assay – PalintestKit TBC (ufc/100ml)
Microbiological Assay – PalintestKit E.coli (ufc/100ml)
3.0 Results and Discussion
The study evaluated an effect of a septic tank or pit latrine
placement near groundwater infrastructures (Hand-dug
wells). Samples were taken fromseven(7)hand-dug wellsin
the rural metropolis of Voinjama, Lofa County, Liberia. To
verify the effect, physicochemical parameters (pH,turbidity,
nitrate, nitrite, lead) and microbiological (TBC, E.coli) were
examined from the samples collected, and the distance from
the hand-dug wells to the pit latrines or septic tank. Table
(2) shows the measured distances from the septic tanks or
pit latrine system to hand-dug wells. Table (3) indicates the
outcomes of physicochemical parameters fromtheanalyzed
water samples. The pH concentrations from the samples
collected ranged from 6.03 to 6.60withall samples dropping
in WHO allowable limits of 6. 0 to 9.0 and of the Quality
Consistent Type I limits. Liberia (LWQS) is 6.5 to 8.5.
Turbidity samples ranged from 0.8 to 6.5 NTU from analysis
recorded in Well (5) which became the sampling factor
(18.29m) far from a pit latrine. The maximum turbidity
analysis was recorded in well (1), a well-positioned 9.04m
from a pit latrine to the wetland that was used as a dumpsite
of stable waste. Altogether, but one (Well 5) of the samples
went above the WHO acceptable limit of one NTU and the
Liberian Water Quality Standard (LWQS) Class I of five NTU
(UNDP, 1978). The nitrate and nitrite concentrations in all
samples were decreasing as per d WHO and LWQS
standards. Well (2), 15.19m from a pit latrine system,
documented the best nitrate and nitrite values. The lead
stayed unobserved in all samples examined (WHO, 2011).
The outcomes of bacteriological analysis (Table 4)
discovered the presenceofmicroorganisms(TBCandE-Coli)
in all of the samples wells. The existence of microorganisms
became even extra obtrusive in Well (2). This fashion looks
to be regular with the findings of Fubara Manuel and Jumbo,
2014, who mentioned that water infrastructures that have
been situated near pit latrines or septic tanksare extra liable
to be contaminated through microorganisms. Bacteria have
been detected from the use of the API 20E assay. Outcomes
confirmed the existence of each Escherichia coli and
Salmonella type in all of the seven (7) samples tested.
Escherichia adecarboxylata and Klebsiella pneumonia have
been detected in all examined samples. Therefore, the
revealing of fecal infection is a sign of health threat to
humans consuming water from those hand-dug wells.These
findings show that septic tank place unpleasantly influences
the microbial excellence of waterand devoursa far-attaining
effect on human well-being.
Table 2: Results of measured seven (7) samples wells
depth, type, water level, distance from a point source,
and WASH standards of Liberia for a septic tank or pit
latrine from wells)
Well# T.W DW
P
(m)
W.L(m
)
D.P.S
(m)
WAS
H (m)
PC RM
Well#
1
Hand
-dug
well
5.18 3.80 9.14 30 NO NT
S
Well#
2
Hand
-dug
well
6.09 4.09 15.1
9
30 NO NT
S
Well#
3
Hand
-dug
well
6.09 4.71 14.0
4
30 NO NT
S
Well#
4
Hand
-dug
well
5.18 3.28 13.1
1
30 NO NT
S
Well#
5
Hand
-dug
well
6.40 4.39 18.2
9
30 NO NT
S
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 02 | Feb 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1034
Well#
6
Hand
-dug
well
5.94 4.04 13.7
2
30 NO NT
S
Well#
7
Hand
-dug
well
5.92 4.03 13.4
4
30 YE
S
NT
S
AVG 5.83 4.05 13.4
9
WHO-World Health Organization; WASH- Water, Sanitation,
And Hygiene; TW-Types of Well; DWP-Depth of Well; WL-
Water Level; DPS-Distance from Point Source (pit
latrine/septic tank); PC-Pipe Culvert; RM-Remark; AVG.
DW-Average Depth of Well; AVG. WT-Average Water Table;
ST-Septic Tank; NTS- Not to Standard.
Table 3: The physio-chemical quality results of water
samples from the seven hand-dug wells
Sampl
e #
Ty
pe
of
wel
l
D.P
.S
(m
)
P
H
Turbi
dity
(NTU
Nitr
ite
(pp
m)
Nitrate(
ppm
Lea
d
(pp
m)
Well#
1
H.D
W
9.1
4
6.
40
6.5 2.1
2
0.12 BD
L
Well#
2
HD
W
15.
19
6.
05
6.3 6.2
7
0.20 BD
L
Well#
3
HD
W
14.
04
6.
20
3.1 4.4
7
0.14 BD
L
Well#
4
HD
W
13.
11
6.
30
2.3 2.4
1
0.11 BD
L
Well#
5
HD
W
18.
29
6.
72
0.8 0.1
0
0.05 BD
L
Well#
6
HD
W
13.
72
6.
35
2.6 2.2
3
0.30 BD
L
Well#
7
HD
W
13.
44
6.
60
2.2 0.1
2
0.13 BD
L
WHO
Stand
ards
6.0
-
9.0
≤ 7 ≤
30
≤ 3 ND
LWQS
Stand
ar#1
6.5
-
8.5
≤ 7 ≤
30
≤ 3 ≤
0.0
01
BDL=Below Detection Limit; LWQS= Liberia Water
Quality Standard; Standard#1=Drinking; ND= Not
Detected; HDW=Hand-dug well
Table 4 Bacteriological quality of sample wells water
Well# Total bacteria
count
(CFU/100ml)
E-coli (CFU/100ml)
Well#1 TNTC TNTC
Well#2 TNTC TNTC
Well#3 TNTC TNTC
Well#4 TNTC TNTC
Well#5 TNTC TNTC
Well#6 TNTC TNCT
Well#7 TNTC TNTC
WHO
Standard
Value
ND/100ml ND/100ml
LWQS
(Standard#1)
ND/100ml ND/100ml
TNTC= Too numerous to count; ND= No detectable;
WHO= WorldHealthOrganization;LWQS=LiberiaWater
Quality Standard
Table 5: Identity of micro-organism isolates using
API20E assay (Smith et al, 1970)
Microb
es
isolate
d
Well
#1
Well
#3
Well
#4
Well
#5
Well
#6
Well
#7
Escher
ichia
coli
Positi
ve
(+)
Positi
ve
(+)
Positi
ve
(+)
Positi
ve
(+)
Positi
ve
(+)
Positi
ve
(+)
Escher
ichia
decarb
oxylate
Negat
ive (-
)
Negat
ive (-
)
Negat
ive (-
)
Negat
ive (-
)
Negat
ive (-
)
Negat
ive (-
)
Samon
ella
Chloler
aesuis
Positi
ve
(+)
Positi
ve
(+)
Positi
ve
(+)
Positi
ve
(+)
Positi
ve
(+)
Positi
ve
(+)
Salmo
nella
pullor
um
Positi
ve
(+)
Positi
ve
(+)
Positi
ve
(+)
Positi
ve
(+)
Positi
ve
(+)
Positi
ve
(+)
Salmo
nella
typhi
Positi
ve(+)
Positi
ve(+)
Positi
ve(+)
Positi
ve(+)
Positi
ve(+)
Positi
ve(+)
Samon
ella
parath
yphi
Positi
ve
(+)
Positi
ve
(+)
Positi
ve
(+)
Negat
ive (-
)
Positi
ve
(+)
Negat
ive (-
)
Kelebs
ie
Pneum
oiae
Negat
ive (-
)
Negat
ive (-
)
Negat
ive (-
)
Negat
ive (-
)
(Neg
ative
-)
Negat
ive (-
)
4.0 Conclusion
This study evaluated the impact of the location of septic
tanks and latrines on groundwater quality in a total of seven
(7) groundwater sources (all dug wells in rural areas) in the
rural city of Voinjama, Lofa County, Liberia. To fully evaluate
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 02 | Feb 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1035
the effect, designated Physio-chemical and microbiological
factors were examined in the samplesanda relationship was
established between the distance of the septic system or
latrine at the source and the measured water quality.
Outcomes were matched with World Health Organization
(WHO) and Liberian Water Quality (LWQ) standards. Fecal
coliforms and E.coli were existing in all seven (7) wells
sampled from well No. 1 of well No. 7. The physicochemical
factors (pH, turbidity, nitrite, nitrate, lead) were all below
the allowable limit in the sample. All sampleswereanalyzed.
Nevertheless, the recognition of Escherichia coli and
Salmonella species in all of the seven (7) samples examined
submits that water from these hand-dug wells may pose a
health risk to consumers and is therefore not suitable for
direct human ingestion without onsite handling. Inaddition,
a resilient relationship was detected among water quality
and the immediacy of the source to septic facilities; with
contamination levels higher than observed at bases near
septic tanks. The study, therefore, concludes that the
location of the septic tanks negativelyaffectsthewater value
in the study area with morenoticeablemomentsathand-dug
wells constructed very close to the septic tank or pit latrine
system Finally, maintaining a safe minimum distance of
30m away from potential sources of pollution such as a pit
latrine, septic tanks, and gravecanreducethecontamination
of the hand-dug wells and borehole which are majorsources
of drinking water of the resident of Voinjama.
References
1. Banerjee, Sudeshna, HeatherSkilling,VivienFoster,Cecilia
Briceño-Garmendia, Elvira Morella,andTarik Chfadi,Ebbing
Water, Surging Deficits: Urban Water SupplyinSub-Saharan
Africa.‖ AICD Background Paper 12, Africa Region, World
Bank, Washington, DC. (2008)
2.Gulyani, Sumila, Debabrata Talukdar, and Darby Jack,
Poverty, Living Conditions, and Infrastructure Access: A
Comparison of Slums in Dakar, Johannesburg, and Nairobi.‖
AICD Working Paper 10, World Bank, Washington, DC.
(2008)
3.Yachiyo Engineering Co., Ltd. Katahira & Engineers
International, The Master Plan Study on Urban Facilities
Restoration and Improvement in Monrovia: Groundwater
Development Plan in Paynesville Area Final Report, 2010
4. Siqueira, L. et al., Groundwater Potential Zone
Identification in the Crystalline Basement Rock Terrain of
Liberia Using Integrated Remote Sensing and GIS, ( 2018)
5. Morella, Elvira, Vivien Foster, and Sudeshna Ghosh
Banerjee. Climbing the Ladder: The State of Sanitation in
Sub-Saharan Africa.‖ AICD Background Paper 13, Africa
Region, World Bank, and Washington, DC. (2008)
6. Mwangi, Lawrence W. Kenya’s Experience: Small-Scale
Water Service Providers.‖ Presentation by a chief executive
officer of Athi Water Services Board to PPIAF Annual
Meeting, May 23–24, 2007.
7. Final Report on Liberia’s Environmental Threats &
Opportunities 118/119 Assessment, (2014)
8. Banerjee, Sudeshna, Vivien Foster, Yvonne Ying, Heather
Skilling, and Quentin Wodon. Cost Recovery, Equity, and
Efficiency in Water Tariffs: Evidence from African Utilities.‖
AICD Working Paper 7, World Bank, Washington, DC.
9. Clement Kiprotich Kiptum and Julius Musyoka Ndambuki,
Well Water Contamination by Pit Latrines: A Case Study of
Langas,(2012)
10. Systematic Review, Water, Sanitation, and Hygiene
(UNicef Liberia 2016)
11. Guideline for Water and Sanitation Services in Liberia,
(2010)
12. Water Supply and Sanitation Services in Liberia, (MOH,
MPW, and LWSC, 2009)
13. George Owusu (2010) Social effects of poor sanitation
and waste management on poor urban communities: a
neighborhood‐specific study of Sabon Zongo, Accra, Journal
of Urbanism, 3:2, 145-160, DOI:
10.1080/17549175.2010.502001, (2010)
14. Henn S. Totin Voldounon, Alternative Sanitation and
Strategic Directives for the Well Water Security in Cotonou
(Benin) and Lome, Togo, (2021)
15. Jay P. Graham and Matthew L. Polizzotto,PitLatrinesand
Their Impact on Groundwater Quality: A SystematicReview,
(2013)

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Impact of Poor Sanitation Infrastructure (Pit Latrine and Septic Tank) on Hand-Dug Well and Borehole in Voinjama, Liberia

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 02 | Feb 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1032 Impact of Poor Sanitation Infrastructure (Pit Latrine and Septic Tank) on Hand-Dug Well and Borehole in Voinjama, Liberia Prof. Dr. Huseyin Gokcekus1, Assco. Prof. Dr. Youssef Kasseme. Ph.D2, Larry T. Woyea3 1Department of Civil Engineering, Civil and Environmental Engineering Faculty,Near East University, Nicosia (Via Mersin 10, Turkey), 99138 Cyprus 2Department of Mehanical Engineering, Engineering Faculty, Near East University, Nicosia, (Via Mersin 10, Turkey), 99138 Cyprus 3Department of Environmental Engineering, Civil and Environmental Engineering Faculty, Near East University, Nicosia, (Via Mersin 10, Turkey), 99138 Cyprus ---------------------------------------------------------------------***---------------------------------------------------------------------- Abstract - In many rural areas of Liberia safedrinkingwater does not occur and wherever it does it is infrequently unreliable, therefore, in these areas,residentsmainlyrely on groundwater for living, and as such, it is common to find individual wells in each cell of such a country house. In addition, in most cases, these houses do not have the town`s drainage system, forcing residents to build latrines or septic tanks near their wells. This study aimed to determine the level of contamination in the samples and to estimate the effect instigated by the building of septic tanks and latrines near groundwater in Voinjama, Liberia.Watersamples were taken in triplicate from seven sampling points and transported to the Liberia Water Supply and Sewerage Cooperation Quality Laboratory (LWSC) in Voinjama for analysis. The pH, nitrate, and nitrite intensities were examined in the samples by spectrophotometry using a colorimeter DR890 (Hach).Leadstageswereanalyzedby the use of a DR 5000 spectrophotometer (Hach). Bacterial analysis (E. coli and coliforms instool)becomecompleted by the use of the Palintest kit (Hach) at the same time as turbidity stages had been calculated by the use of a T100 turbidimeter (Oakton). Furthermore, microbiological isolates had been recognized for the use of API 20E assay. Results were compared with World Health Organization (WHO) and Water Sanitation and Hygiene (WASH Liberia) standards. Coliforms Faecal and E.coli were found in all, however very excessive in wells closest to septic tanksorpit latrines. The physicochemical factors (pH, turbidity, nitrite, nitrate, lead) were all beneath the acceptable standard in all analyzed samples. The study, therefore, concludes that the location of the septic tanks negativelyaffectsthewatervalue in the study area with more noticeable magnitudes at hand- dug wells constructed very close to the septic tank or pit latrine system. Key Words: (Pit Latrines; Septic Tanks; Boreholes and hand-dug well; Pollution, Measurement;contamination) 1. INTRODUCTION In many rural areas of Liberia, safe drinking water does not occur and where it does it is hardly unreliable, therefore, in these zones, inhabitants mainly depend on groundwater for living, and as such, it is mutual to find specific wells in each cell of such a country house. In addition, in most cases, these houses do not have the town`s drainage system, forcing residents to build latrines or septic tanks near their wells. Voinjama is the capital metropolis of Lofa County is confronted with extreme demanding situations of securing water for its people; which can be attributed to the terrible sanitation infrastructures and shortage of technical tips when constructing pit latrines, septic tanks, and hand-dug wells. This rural metropolis additionally lacks sewer and drainage structures making its population depend upon personal connection through the developmentofpitlatrines and septic tanks to deliver the sewage that'spoorlybuiltand controlled thereby contaminating the groundwatersources. This study aimed to determine the level of contamination in the samples and to estimate the impact caused by the construction of septic tanks and latrines near groundwater in Voinjama, Liberia. The study area is positioned along the hills of the northernmost tip of the country, close to the Guinean border. According to the 2008 census, it has a population of approximately 26,594. The residents in this area rely on agriculture for their livelihood, particularly growing rice. In this rural metropolis, there's no sewage system to serve the populace, and as such, all residential, industrial and public homes rely upon pit latrines andseptic tanks for wastewater deposition. Figure 1-Map of Study area (Voinjama)
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 02 | Feb 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1033 2. Methodology A set of seven (7) water samples was taken from separate sites in the rural town of Voinjama, Lofa County, Liberia. At each specimen point, the size (distance) between the manually dug well and the nearest septic tank or latrine, including depth, was measured with a 50 m tape measure and recorded. Seven rapid resamplings exceed the 30m distance requirement recommended by the Liberian Water and Sanitation Authority/MPW (WASH/MPW, 2010). Samples were collected in easy 1.5 L flexible flasks, clearly marked for clear identification, and stored in an insulated container with an ice ratio before being shipped to our laboratory substation in Liberia for analysis; samples were examined within 24hrs of collection. The factors measured during the study were pH, turbidity, nitrate, nitrite, lead, general microbial count (TBC), and E.coli. The investigative method used for every factor is indexed in Table 1.0. Additionally, the microbiological isolates have been identified by the use of the Analytical ProfileIndex(API20E) assay created in the Seventies through Pierre Janin (Holmes et al 1978). Table 1.0 Investigative procedures and factors Investigative procedure/ Equipment Parameter Unit Multi parameter (in-situ)-pH Meter PH Absorptometric method (USEPA 8237)- Turbidity Meter (T100 Oakton) Turbidity (NTU Diazotization method (USEPA 8507)-DR 890 (Hach) Nitrite (ppm) Cadmium reduction (USEPA 8192)- DR 890 (Hach) Nitrate(ppm) Flame Spectrophotometry – DR 5000 (Hach) Lead (ppm) Microbiological Assay – PalintestKit TBC (ufc/100ml) Microbiological Assay – PalintestKit E.coli (ufc/100ml) 3.0 Results and Discussion The study evaluated an effect of a septic tank or pit latrine placement near groundwater infrastructures (Hand-dug wells). Samples were taken fromseven(7)hand-dug wellsin the rural metropolis of Voinjama, Lofa County, Liberia. To verify the effect, physicochemical parameters (pH,turbidity, nitrate, nitrite, lead) and microbiological (TBC, E.coli) were examined from the samples collected, and the distance from the hand-dug wells to the pit latrines or septic tank. Table (2) shows the measured distances from the septic tanks or pit latrine system to hand-dug wells. Table (3) indicates the outcomes of physicochemical parameters fromtheanalyzed water samples. The pH concentrations from the samples collected ranged from 6.03 to 6.60withall samples dropping in WHO allowable limits of 6. 0 to 9.0 and of the Quality Consistent Type I limits. Liberia (LWQS) is 6.5 to 8.5. Turbidity samples ranged from 0.8 to 6.5 NTU from analysis recorded in Well (5) which became the sampling factor (18.29m) far from a pit latrine. The maximum turbidity analysis was recorded in well (1), a well-positioned 9.04m from a pit latrine to the wetland that was used as a dumpsite of stable waste. Altogether, but one (Well 5) of the samples went above the WHO acceptable limit of one NTU and the Liberian Water Quality Standard (LWQS) Class I of five NTU (UNDP, 1978). The nitrate and nitrite concentrations in all samples were decreasing as per d WHO and LWQS standards. Well (2), 15.19m from a pit latrine system, documented the best nitrate and nitrite values. The lead stayed unobserved in all samples examined (WHO, 2011). The outcomes of bacteriological analysis (Table 4) discovered the presenceofmicroorganisms(TBCandE-Coli) in all of the samples wells. The existence of microorganisms became even extra obtrusive in Well (2). This fashion looks to be regular with the findings of Fubara Manuel and Jumbo, 2014, who mentioned that water infrastructures that have been situated near pit latrines or septic tanksare extra liable to be contaminated through microorganisms. Bacteria have been detected from the use of the API 20E assay. Outcomes confirmed the existence of each Escherichia coli and Salmonella type in all of the seven (7) samples tested. Escherichia adecarboxylata and Klebsiella pneumonia have been detected in all examined samples. Therefore, the revealing of fecal infection is a sign of health threat to humans consuming water from those hand-dug wells.These findings show that septic tank place unpleasantly influences the microbial excellence of waterand devoursa far-attaining effect on human well-being. Table 2: Results of measured seven (7) samples wells depth, type, water level, distance from a point source, and WASH standards of Liberia for a septic tank or pit latrine from wells) Well# T.W DW P (m) W.L(m ) D.P.S (m) WAS H (m) PC RM Well# 1 Hand -dug well 5.18 3.80 9.14 30 NO NT S Well# 2 Hand -dug well 6.09 4.09 15.1 9 30 NO NT S Well# 3 Hand -dug well 6.09 4.71 14.0 4 30 NO NT S Well# 4 Hand -dug well 5.18 3.28 13.1 1 30 NO NT S Well# 5 Hand -dug well 6.40 4.39 18.2 9 30 NO NT S
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 02 | Feb 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1034 Well# 6 Hand -dug well 5.94 4.04 13.7 2 30 NO NT S Well# 7 Hand -dug well 5.92 4.03 13.4 4 30 YE S NT S AVG 5.83 4.05 13.4 9 WHO-World Health Organization; WASH- Water, Sanitation, And Hygiene; TW-Types of Well; DWP-Depth of Well; WL- Water Level; DPS-Distance from Point Source (pit latrine/septic tank); PC-Pipe Culvert; RM-Remark; AVG. DW-Average Depth of Well; AVG. WT-Average Water Table; ST-Septic Tank; NTS- Not to Standard. Table 3: The physio-chemical quality results of water samples from the seven hand-dug wells Sampl e # Ty pe of wel l D.P .S (m ) P H Turbi dity (NTU Nitr ite (pp m) Nitrate( ppm Lea d (pp m) Well# 1 H.D W 9.1 4 6. 40 6.5 2.1 2 0.12 BD L Well# 2 HD W 15. 19 6. 05 6.3 6.2 7 0.20 BD L Well# 3 HD W 14. 04 6. 20 3.1 4.4 7 0.14 BD L Well# 4 HD W 13. 11 6. 30 2.3 2.4 1 0.11 BD L Well# 5 HD W 18. 29 6. 72 0.8 0.1 0 0.05 BD L Well# 6 HD W 13. 72 6. 35 2.6 2.2 3 0.30 BD L Well# 7 HD W 13. 44 6. 60 2.2 0.1 2 0.13 BD L WHO Stand ards 6.0 - 9.0 ≤ 7 ≤ 30 ≤ 3 ND LWQS Stand ar#1 6.5 - 8.5 ≤ 7 ≤ 30 ≤ 3 ≤ 0.0 01 BDL=Below Detection Limit; LWQS= Liberia Water Quality Standard; Standard#1=Drinking; ND= Not Detected; HDW=Hand-dug well Table 4 Bacteriological quality of sample wells water Well# Total bacteria count (CFU/100ml) E-coli (CFU/100ml) Well#1 TNTC TNTC Well#2 TNTC TNTC Well#3 TNTC TNTC Well#4 TNTC TNTC Well#5 TNTC TNTC Well#6 TNTC TNCT Well#7 TNTC TNTC WHO Standard Value ND/100ml ND/100ml LWQS (Standard#1) ND/100ml ND/100ml TNTC= Too numerous to count; ND= No detectable; WHO= WorldHealthOrganization;LWQS=LiberiaWater Quality Standard Table 5: Identity of micro-organism isolates using API20E assay (Smith et al, 1970) Microb es isolate d Well #1 Well #3 Well #4 Well #5 Well #6 Well #7 Escher ichia coli Positi ve (+) Positi ve (+) Positi ve (+) Positi ve (+) Positi ve (+) Positi ve (+) Escher ichia decarb oxylate Negat ive (- ) Negat ive (- ) Negat ive (- ) Negat ive (- ) Negat ive (- ) Negat ive (- ) Samon ella Chloler aesuis Positi ve (+) Positi ve (+) Positi ve (+) Positi ve (+) Positi ve (+) Positi ve (+) Salmo nella pullor um Positi ve (+) Positi ve (+) Positi ve (+) Positi ve (+) Positi ve (+) Positi ve (+) Salmo nella typhi Positi ve(+) Positi ve(+) Positi ve(+) Positi ve(+) Positi ve(+) Positi ve(+) Samon ella parath yphi Positi ve (+) Positi ve (+) Positi ve (+) Negat ive (- ) Positi ve (+) Negat ive (- ) Kelebs ie Pneum oiae Negat ive (- ) Negat ive (- ) Negat ive (- ) Negat ive (- ) (Neg ative -) Negat ive (- ) 4.0 Conclusion This study evaluated the impact of the location of septic tanks and latrines on groundwater quality in a total of seven (7) groundwater sources (all dug wells in rural areas) in the rural city of Voinjama, Lofa County, Liberia. To fully evaluate
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 02 | Feb 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1035 the effect, designated Physio-chemical and microbiological factors were examined in the samplesanda relationship was established between the distance of the septic system or latrine at the source and the measured water quality. Outcomes were matched with World Health Organization (WHO) and Liberian Water Quality (LWQ) standards. Fecal coliforms and E.coli were existing in all seven (7) wells sampled from well No. 1 of well No. 7. The physicochemical factors (pH, turbidity, nitrite, nitrate, lead) were all below the allowable limit in the sample. All sampleswereanalyzed. Nevertheless, the recognition of Escherichia coli and Salmonella species in all of the seven (7) samples examined submits that water from these hand-dug wells may pose a health risk to consumers and is therefore not suitable for direct human ingestion without onsite handling. Inaddition, a resilient relationship was detected among water quality and the immediacy of the source to septic facilities; with contamination levels higher than observed at bases near septic tanks. The study, therefore, concludes that the location of the septic tanks negativelyaffectsthewater value in the study area with morenoticeablemomentsathand-dug wells constructed very close to the septic tank or pit latrine system Finally, maintaining a safe minimum distance of 30m away from potential sources of pollution such as a pit latrine, septic tanks, and gravecanreducethecontamination of the hand-dug wells and borehole which are majorsources of drinking water of the resident of Voinjama. References 1. Banerjee, Sudeshna, HeatherSkilling,VivienFoster,Cecilia Briceño-Garmendia, Elvira Morella,andTarik Chfadi,Ebbing Water, Surging Deficits: Urban Water SupplyinSub-Saharan Africa.‖ AICD Background Paper 12, Africa Region, World Bank, Washington, DC. (2008) 2.Gulyani, Sumila, Debabrata Talukdar, and Darby Jack, Poverty, Living Conditions, and Infrastructure Access: A Comparison of Slums in Dakar, Johannesburg, and Nairobi.‖ AICD Working Paper 10, World Bank, Washington, DC. (2008) 3.Yachiyo Engineering Co., Ltd. Katahira & Engineers International, The Master Plan Study on Urban Facilities Restoration and Improvement in Monrovia: Groundwater Development Plan in Paynesville Area Final Report, 2010 4. Siqueira, L. et al., Groundwater Potential Zone Identification in the Crystalline Basement Rock Terrain of Liberia Using Integrated Remote Sensing and GIS, ( 2018) 5. Morella, Elvira, Vivien Foster, and Sudeshna Ghosh Banerjee. Climbing the Ladder: The State of Sanitation in Sub-Saharan Africa.‖ AICD Background Paper 13, Africa Region, World Bank, and Washington, DC. (2008) 6. Mwangi, Lawrence W. Kenya’s Experience: Small-Scale Water Service Providers.‖ Presentation by a chief executive officer of Athi Water Services Board to PPIAF Annual Meeting, May 23–24, 2007. 7. Final Report on Liberia’s Environmental Threats & Opportunities 118/119 Assessment, (2014) 8. Banerjee, Sudeshna, Vivien Foster, Yvonne Ying, Heather Skilling, and Quentin Wodon. Cost Recovery, Equity, and Efficiency in Water Tariffs: Evidence from African Utilities.‖ AICD Working Paper 7, World Bank, Washington, DC. 9. Clement Kiprotich Kiptum and Julius Musyoka Ndambuki, Well Water Contamination by Pit Latrines: A Case Study of Langas,(2012) 10. Systematic Review, Water, Sanitation, and Hygiene (UNicef Liberia 2016) 11. Guideline for Water and Sanitation Services in Liberia, (2010) 12. Water Supply and Sanitation Services in Liberia, (MOH, MPW, and LWSC, 2009) 13. George Owusu (2010) Social effects of poor sanitation and waste management on poor urban communities: a neighborhood‐specific study of Sabon Zongo, Accra, Journal of Urbanism, 3:2, 145-160, DOI: 10.1080/17549175.2010.502001, (2010) 14. Henn S. Totin Voldounon, Alternative Sanitation and Strategic Directives for the Well Water Security in Cotonou (Benin) and Lome, Togo, (2021) 15. Jay P. Graham and Matthew L. Polizzotto,PitLatrinesand Their Impact on Groundwater Quality: A SystematicReview, (2013)