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INTERNATIONAL JOURNAL OF RESEARCH AND INNOVATION IN APPLIED SCIENCE (IJRIAS)
ISSN No. 2454-6194 | DOI: 10.51584/IJRIAS |Volume X Issue XIII October 2025
Special Issue on Innovations in Environmental Science and Sustainable Engineering
Households Access to Water, Sanitation and Hygiene Facilities in
Some Selected Local Government Areas in Borno State, Northeast,
Nigeria
Mustapha Mala, Abubakar Lawan Gajerima, Ibrahim Usman, Muhammad Zanna Bultu
University of Maiduguri, Borno State, Nigeria
DOI: https://dx.doi.org/10.51584/IJRIAS.2025.101300005
Received: 07 October 2025; Accepted: 14 October 2025; Published: 13 November 2025
ABSTRACT
Borno State is among the states in Nigeria that is faced with numerous challenges related to sanitation and
hygiene issues. Access to water, sanitation and hygiene (WASH) services are very crucial in influencing
healthy conditions and general wellbeing of a society. The poor and unsafe access to WASH plays a key role
in transmission of various diseases. This study sought to assess respondents awareness and practices in relation
to access to water sources, treatment, storage, sanitation and personal hygiene in fifteen communities of three
local government areas in three senatorial districts of Borno State employing structured questionnaires and site
observations for data collection. The data were analyzed using percent and frequency distribution tables that
exhibits percent differences of the variables.
The study identified tvarious sources of water supply with boreholes (57.7%) as the major sources of drinking
water supply been utilized in the area. The study also identified few participants (32.7%) got their water
within 100 500meters distance and the study further demonstrates that majority of respondents (50.6%) do
not treat their water before consumption. Findings also revealed majority of young girls (39.7%) and women
(18.8%) were responsible for fetching water in households and with a relatively lower cost 25.3% of buying
water and some of the participants even claimed the cost is cheap 23.9% for households. Water storage facility
and collection, the study shows 38.2% of the respondents stored water in plastic covered container and 22.6%
of respondents use cups with handle to draw water in households.
The result revealed that majority of the households 37.7% use private latrine and 31.2% use shared latrine.
Respondents claimed lack of funds led to use of shared latrines, poor excreta disposal systems and high open
field defecation practices. On the aspects of hygiene, children’s faeces were mostly disposed into a toilet
(54.1%) and use soap to wash hands after defecation (19.3%). The major diseases reported in the communities
is typhoid (54.8%). Perception on exposed excreta of children, 43.9 % reported that children’s faeces are
harmful. Personal hygiene of the respondent’s exhibits respondents had poor knowledge of hygiene with
regards to hand washing hygiene, bathing, and clothes hygiene, irrespective of their educational level. The
results show 26.1% of respondents reported use of soap as the major opinion in all the selected LGAs for the
domestic washings. Despite WASH interventions which aim to prevent and control transmission of bacteria,
viruses and parasites. The poor knowledge of hygiene and unsafe access to WASH plays a key role in
transmission of various diseases. WASH interventions with regards to safe water, storage facility for portable
water, latrines for sanitation and soap for hygiene, bath and hand washing. This findings will be a useful
information on the consequences of poor hygiene practices and sanitation facilities for both residents and
authorities. The study recommends that the data obtained can serve as a blueprint to government or private
organizations working towards upgrading standard of WASH practices, which would assist in providing
appropriate facilities towards enforcing safe hygiene practices across the communities and state at large.
Keywords: Knowledge, Practice, Water, Sanitation, Hygiene, Environment.
INTRODUCTION
United Nations General Assembly (UNGA) recognised the right to drinking water and sanitation as a human
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ISSN No. 2454-6194 | DOI: 10.51584/IJRIAS |Volume X Issue XIII October 2025
Special Issue on Innovations in Environmental Science and Sustainable Engineering
right and called on states to intensify efforts to provide safe, clean, accessible and affordable drinking water
and sanitation for all (UNGA, 2010). Global access to water, sanitation, and hygiene services plays a vital role
in protecting the health and wellbeing of individuals and society (Olukanni, 2013; Olukanni and Okorie, 2015).
Access to safe and adequate water helps to promote hygiene practices, which helps to prevent diarrheal disease
(WHO 2022). Globally, over 2 billion people live in water-stressed countries (WHO 2022), which is expected
to be compounded in some regions due to climate change and population growth (Gebremichael et al.
2021).Without a safe drinking water supply, improved sanitation and effective hygiene practices in their
households, children are at increased risk of disease and even death. More than 700 children under age five die
every day from diarrheal diseases due to lack of access to WASH. Many acute respiratory infections, the
leading cause of death for children under age five, can be prevented by hand washing. Poor WASH is
responsible for an estimated 50% of child malnutrition (UN-Water), and WASH is also critical for the
prevention of neglected tropical diseases (NTDs) that affect more than 1 billion people.
Safe drinking water is anonymously accepted as an international agenda and priority, which is evident from the
MDGs and SDGs of the United Nations (UN) initiative and vision (MDGs7 and SDGs 6). Despite the MDGs
effort, still many people lack access to safe drinking water,even lack access to basic water. Globally, more than
1 billion people do not have access to safe drinking water. According to the Third World Academy of Sciences
(TWAS) report, contaminated/dirty water is killing more people than cancer, AIDS, wars or accidents.
Populationof the world is increasing and the available fresh water resources almost remain constant.
Sanitation refers to the hygienic means of protecting human contact from the dangers of waste to promote good
health (Pati et al., 2014). Sanitation includes the provision of facilities and services for the safe disposal of
waste. Sanitation is one of the most basic services in human life. Inadequate sanitation is a major cause of
disease worldwide and improving environmental sanitation is known to have a significant beneficial impact on
health in both household and across communities (Philip, 2010). Peoples access to improved sanitation
facilities that are basically designed to hygienically separate excreta from human contact was increased over
(WHO, 2021; WHO & UNICEF, 2018). However, in 2020, 494 million people were still practising open
defecation (WHO 2010). Of the world’s seven billion people, six billion have mobile phones. Yet only 4.5
billion people have access to toilets or latrines; meaning is that two and a half billion people, mostly in rural
areas, do not have proper sanitation. There are 1.1 billion people still defecating in the open. In many
countries, 95 per cent or more of the poorest fifth of the population practices open defecation (www.unric.org,
2024).
In addition, 670 million people do not have handwashing facilities with soap and water (WHO 2010). Also,
NEEDS (2007) recognized that good health is unobtainable unless the environments in which people live are
healthy? Many of the diseases that affect Nigerians such as Malaria, Tuberculosis, and Dysentery are due to
unhealthy environmentally sanitary condition. Also, hygiene refers to good practices that prevent disease and
lead to good health, especially in terms of cleanliness, proper disposal of wastewater, and supply of clean
drinking water, poor hygiene practices and inadequate sanitary conditions play major roles in the increased
burden of communicable diseases within developing countries. Provision of adequate water supply, sanitation;
hygiene and waste management have a number of positive effect (Murray and Lopez, 1996). WaSH practices
include a supply of cleanwater for drinking, washing and cleaning, safe disposal of waste (toilets and garbage
disposal), andhealth promotion activities promoting healthy practices among affected populations (UNDP,
2020 Goal 6). Accordingto World Helth Organization, potable water supply and sanitation is fundamental for
living a healthy life. Sufficient and quality water supply is not only a vital environmental health necessity to
live but plays significant roles in the socio-economic and political advancement of the human population. The
WHO also notes that water and sanitation for communities and households do not only contribute to physical
growth and human development but also people's socio-economic development. UNDP, 2020 Goal 6 reports
that over70 percent of the world population (about 5.2 billion people) who had safely managed drinking water
in 2015, still lacked essential drinking water while 39 percent of the world population that had safe sanitation
still lacked basic sanitation with worrisome statistics of about 892 million people still practicing open
defecation.
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INTERNATIONAL JOURNAL OF RESEARCH AND INNOVATION IN APPLIED SCIENCE (IJRIAS)
ISSN No. 2454-6194 | DOI: 10.51584/IJRIAS |Volume X Issue XIII October 2025
Special Issue on Innovations in Environmental Science and Sustainable Engineering
WASH issues and challenges tend to be more pathetic in arid regions due to the extreme rainfall variability
which has been worsened by climate change. This has resulted in desertification, drying of water bodies
(ponds, streams and rivers), and growing water scarcity, thus increasing the challenges of providing adequate
WASH services by national governments and other water service providers in the region (Ohwo and
Agusomu,2018). In addition, the unsuitable climate has consequently resulted in poor hydro-geologic
formation in these arid zones due to low aquifer recharge thus, requiring huge capital which many in the
communities cannot afford.This has further aggravated the challenges, thus, forcing communities mostly
women and children trekking kilometers and spending hours searching for clean water (Adeleye et al., 2014,
USAID, 2019; Kurui et al., 2019).
Yet today many people lack access to safe drinking water. An estimated hundreds of thousands do not have
access to managed sanitation service and large inequality in access to basic services between the richest and
poorest. In study area, access to appropriate WASH facilities remains an issue. The development and
occurrence of water, sanitation, and hygiene problems has become more pronounced in recent years. This
challenge focuses heavily on low income disadvantaged groups, such as the poor and disabled who make a
significant contribution to the poverty cycle. Although recent time, Nigeria has made a giant stride in
providing safewater and sanitation both in urban and rural areas. At the household in urban and rural levels,
there are still exist great concerns about the adequate accessibility, and quality of water and use of the WASH
facilities.
While it is critical to have good WASH practices for better health, there are existing gaps in relation to
awareness, behavioural practices, accessibility, and availability to safe water and essential hygienic
commodities (Mustapha et al., 2022). Lack of WASH knowledge, unhygienic practices and poor attitudes
towards WASH facilities often times are significant factors to water borne diseases prevalence in communities
(Gebreeyessus and Adem, 2018; Berheet al., 2020; Mustapha et al., 2022; Mbuka - Nwosu, 2022). Very few
studies have been conducted on households’ limited access to drinking water and sanitation facilities in the
study area. And these studies have reported divergent perspectives to WaSH issues. Most of the studies
focused on sanitation facilities in IDPs Camps across the state (WSC, 2022; Tarek Jaber et al, 2023; SNRA,
2024).
However, the critical issue surrounding its impacts and implications for the residents in the study area have
not been dealt with. If the level of wash practices were known in the study area, this would be helpful to
provides critical insights for policymakers, development agencies, and practitioners aiming to implement
recovery-focused infrastructure interventions in fragile and crisis-affected settings on the sanitation facilities
and awareness creation in the communities studied and state at large. Thus, this study aims to assess the level
of awareness and practices of Water, Sanitation, and hygiene practices on (1) water sources of drinking and
other purposes, (2) methods of water treatment (3) methods of collection and storage of drinking water (3)
waste disposal operations, and personal and environmental hygiene practices and some related water borne
diseases within the selected communities of the three local government areas in Borno State, Nigeria.
MATERIALS AND METHODS
Study Area
Borno State is located on longitudes 11° 30'E and 14
0
45
; and latitudes 10° 15'N and 14° 60'N in Northeastern,
Nigeria, with a land area of 72,152sq km and a population of 4,171,104, according to the last official census in
2006, with a density of 84.70/km
2
. The state shares borders with the Adamawa to the south, Gombe to the
southeast and Yobe State to the west. The eastern border forms part of the national border with Republic of
Chad to the East, Niger Republic to the northern border and Cameroun to the northeastern border. Data was
obtained through questionnaires administered in a households within the study area where the survey could be
easily assessed as it is easier to meet people and interact.
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INTERNATIONAL JOURNAL OF RESEARCH AND INNOVATION IN APPLIED SCIENCE (IJRIAS)
ISSN No. 2454-6194 | DOI: 10.51584/IJRIAS |Volume X Issue XIII October 2025
Special Issue on Innovations in Environmental Science and Sustainable Engineering
Figure 1 showing study area
Sample Design and Data Collection
A survey design was employed. Following the observed even challenges of water stress in Borno state, a local
government area (LGA) was selected from each of the three senatorial zones using simple random sampling.
Fifteen (15) communities were sampled in the three LGA from the three Senatorial Zones in the State. The
number of communities randomly sampled from each local government was in accordance with proportional
sampling. Thus, five communities (Kasugula, Old Bama, Buwor Tela, Shehuri and Goniri) from Bama LGA,
five communities (Asur, kajjaf, Durba, Ndawak and Hembe) from Chibok LGA, and five communities (Ajari,
Low cost, Lawanti, Majeri, and Mangeiri) from Kaga LGA, respectively in the three Senatorial Zones. At p =
0.1, a sample size of 140 was deduced from Bama LGA and 120 each from Chibok and Kaga LGAs fifteen
communities were sampled from households using systematic random sampling (Yamane, 1967). Structured
questionnaires were used to collect data.
Data was collected by administering structured questionnaire and spot check observations adapted based on
UNHCR water, sanitation and hygiene survey standard questionnaire. The survey was both qualitative and
quantitative by questionnaire administration and spot-check observations which involved observing and
recording information on environmental conditions in the communities surveyed. The survey was classified
into five significant sections, which were Section A respondents’ demographic characteristics such as age,
gender, marital status, religion, house hold size, children age 5 and below in the households, education and
Area were collected. Section B, knowledge on sources of drinking water supply, sanitation and hygiene
variables on drinking water sources, collection, storage, and treatment; Section C Sanitation (type of facility,
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ISSN No. 2454-6194 | DOI: 10.51584/IJRIAS |Volume X Issue XIII October 2025
Special Issue on Innovations in Environmental Science and Sustainable Engineering
location, sharing of facility, cleaning, and emptying) Section D hygiene practices at household level were
collected and Section F Spot check Observation of possible contamination of water sources by environmental
condition.The population under study comprise of males and females from age 15 and above involved
indifferent socio-economic activities in these locations. Assistance was given to those unable to read and write.
A total number of three hundred and eighty (380) respondents were engaged in the study. This sample size was
arrived from Yamane’s formula for estimating sample sizes (Arthur and Imoro, 2021). Yamane formula:
n = N / (1+Ne
2
),
where n represent sample size,
N represent population size and
e represent the standard error (0.05).
Data Analysis
Data was analyzed through descriptive statistic tool in SPSS software (version 19) to obtain frequencies,
percentages, as well as minimum and maximum values. Cross-tabulation and Pearson chi-square was used to
compare the relationship between variables. Microsoft Excel was used to present data in charts and tables.
RESULT AND DISCUSSION
This section presents the results of the Water, Sanitation, and Hygiene practices survey that was conducted in
the selected LGAs of Borno State. Tabulation of data was adopted for easy understanding, and comparison
between the three (3) chosen LGAs. The results were presented through the use of frequency tables.
Section A: Demographic Characteristics of Respondents
This section presents the data on demographic characteristics of respondents interviewed in the fifteen
communities of the three selected local government areas of Borno State.
Table 1: Demographic Characteristics of Respondents
Age Group
Frequency
Percentage (%)
017 years
3
0.8
1824 years
32
8.4
2534 years
117
30.8
3544 years
103
27.1
4554 years
54
15.5
55 years and above
66
17.4
Total
380
100
Gender
Percentage (%)
Male
67.9
Female
32.1
Total
100
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INTERNATIONAL JOURNAL OF RESEARCH AND INNOVATION IN APPLIED SCIENCE (IJRIAS)
ISSN No. 2454-6194 | DOI: 10.51584/IJRIAS |Volume X Issue XIII October 2025
Special Issue on Innovations in Environmental Science and Sustainable Engineering
Marital
Status
Percentage (%)
Never
Married
24.2
Married
65
Widowed
10.8
Total
100
Religion
Percentage (%)
Islam
60.5
Christianity
39.5
Total
100
Household Members
Frequency
Percentage (%)
15 members
190
50
510 members
108
28.4
More than 10 members
82
21.6
Total
380
100
Children (Age 5 and Below)
Frequency
Percentage (%)
15 members
120
26.3
510 members
160
68.4
More than 10 members
20
5.3
Total
380
100
Education Level
Frequency
Percentage (%)
No Education
42
11
Islamic Education
49
12.9
Primary
85
22.4
Secondary
150
39.5
Tertiary
54
14.2
Total
380
100
Area
Frequency
Percentage (%)
Urban
57.3
15.1
Rural
42.7
11.2
Source: Field Survey, 2025
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The data from table 2 firstly shows the distribution of respondents' age. Out of 380 respondents interviewed,
the data demonstrated that 0.8% of the respondents are between 0 -17 years, 8.4% between 18-24 years, 30.8%
between 25-34 years, and 27.1% between respondents aged 35-44 years, 15.5% represented 45-54 years and
over 55-year-olds represents 17.4%, respectively. The result shows that majority of the respondent's age
composition is between 25 44 years of age bracket which is quite similar in context to all the communities.
This implies the dominance of the respondents by youth category of below the age of 45 years 66.3% (Table
1). These category of people who are productive and agile engaged in most of the activities of Wash in their
respective areas and have assisted in providing information during administering the questionnaire based on
their individual experiences. Also, the result revealed information on gender 67.9% of the respondents were
male while 32.1% of the respondents were female. There are more males participated in the answering the
questionnaire, suggesting balanced male involvement in evaluating WASH services. As heads of households in
many communities, they mostly response to questions regarding infrastructure quality, water accessibility, and
economic benefits. However, men may not fully capture the day-to-day challenges related to water collection,
sanitation, and hygiene which are typically experienced by women and children. Regarding marital status of
the respondents, the result further indicated majority of the participants 65% were married, while 24.2% were
not married and 10.8% were widowed. Majority of the respondents 60.5% were Muslims while 39.5% were
Christians. Data from Table 1 showed that majority of the respondents had received secondary education
39.5% while the 85% of the respondents had attended. The data further revealed those with tertiary education
constitute 54%, and Islamic education 49% whereas respondents with no formal education were 42%
respectively. Among the study respondents, about 37.3 (15.1%) lived in an urban area at the time of the survey,
while 42.7 (11.2%) were in rural area.
Section B: Responses On Sources of Drinking Water Supply
This section present the responses of households on sources of drinking water as shown in Tables 2 - 7 below.
Table 2 Sources of Drinking Water for the Respondents
Sources of Drinking Water
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Boreholes
86.4
52.5
80.5
57.7
Well
13.6
32.5
7
14
Rainwater
0
4.2
2.5
1.8
Bottled water
0
10.8
0.5
3
River/Stream
0
0
5.5
1.4
Water truck
0
0
4
1.1
Other
0
0
0
0
Source: Field Survey, 2025
Response on Sources of Drinking Water
The primary sources of drinking water supply in households across the three local government areas surveyed
were borehole 57.7%, wells 14%, bottled water 3%, rainwater 1.8%, river / stream 1.4% and water truck 1.1%
were shown to be main sources from the responses in the questionnaire.
This analysis clearly demonstrates various sources of water supply have been generally utilized, especially
borehole as most common source of water supply with 86.4% in Bama, 80.5% in Kaga and in 52.2% Chibok
respectively. Nonetheless, the analysis also indicated a slight disparity in well water supply as 32.5% Chibok,
recorded the highest number of wells, while Bama and Kaga were only 13.6% and 7% respectively.
Accessing improved water sources for drinking typically comes through boreholes, rather than piped
connections. However, various sources indicate widespread challenges with infrastructure in the region. From
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Special Issue on Innovations in Environmental Science and Sustainable Engineering
personal oral interview, it was gathered that the most used source of water supply are public boreholes initially
provided by the governments, particularly through its agency Rural Water Supply and Sanitation Agency
(RUWASSA) and local government councils. However, most of these water infrastructures were vandalized
amidst the insurgency. But these infrastructures were rehabilitated by Non-Governmental Organization
(NGOs) as well as well-meaning individuals. These interventions significantly improved access to clean water
and sanitation for vast majority of the communities, contributing to better health outcomes, reduced disease
transmission, and enhanced dignity and quality of life particularly for women, children, and other vulnerable
groups. The solar-powered boreholes, in particular, offer a sustainable and energy-efficient solution, ensuring
continuous access to water even in remote or off-grid communities. However, there are a few boreholes that
are commercial and private that also supply drinking water in the neighborhood in all the communities.
Considering the survey areas, the majority of the households have their water supplied by more than one
sources of water supply. It is noteworthy that the categories are not exclusionary. The communities surveyed in
all the LGAs have access to water from more than one water supply, considering as options public network,
borehole, well and surface water. Findings from this study shows that majority of the residents relying on
borehole as principal source of water supply is similar to that of Mbuka - Nwosu et al., (2022) who stated that
a large proportion of households (99.89% in the dry season and 99.56% in the wet season) in rural
communities of Imo State use borehole water daily.
Table 3: Distance of water source from your households
Distance to Water Source
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Less than 100 meters
57
11.7
47.5
30.6
100 500 meters
20
54.1
50
32.7
500 meters 1 kilometer
12
32.5
2.5
12.4
More than 1 kilometer
11
1.7
0
3.3
Source: Field Survey, 2025
The distance of water source from your households
The proportion of responses on the proximity of the water source to the households in Table 3 shows 32.7% of
respondents get water from 100 meters 500 meters away in all the three LGAs, This implies, varying
distances, yet a relatively short distance across the LGAs with 54.1% in Chibok recorded the highest, while
50% in Kaga and 20% in Bama. The result also show majority of respondents 57% in Bama access water
source within a closest distance of less than 100 meters, whereas 47.5% in Kaga and the least 11.7% in
Chibok. Furthermore, 28.6% of households reported accessing water within 10 to 30 minutes of walking from
their dwellings, while about 22.5% reported spending less than 10 minutes on foot to reach water sources and
21% of the respondents claimed 30 minutes 1 hour in all the LGAs respectively.
This analysis demonstrates that households in Bama and Kaga LGAs have shortest possible distance to source
of water when compared to Chibok as illustrated in (Table 3). Since the majority of the respondents get their
water supply from public boreholes, which most times is available within the respondent's residence, this
reduces the distance of getting water supply to the nearest distance. The long distances covered to access water
by residents in Chibok LGA could lead to underusing this vital resource in their households. In this regard,
sanitation could be undermined and this exacerbates the existing poor conditions of these residents. The links
between affordable water, sanitation and poverty have been widely established and cannot be relegated by any
society with a quest to achieve sustainable development (World Bank Group, 2018). Similarly, such distances
could make a girl child more vulnerable to sexual abuse and its interconnected risks which impede
achievement of her full human potential. Reducing the distance required to fetch water is associated with lower
prevalence of diarrhea, improved nutrition, as well as reductions in under-five child mortality (Rabie and
Curtis, 2006), possibly because it enables better hygiene practices (Semmelweis, 1983) and frees up time for
child care or income generating activities (Blencowe et al., 2011) , resulting in healthier children.
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Table 4: Time it takes to get there, get water and come back
Time Duration
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Less than 10 minutes
47.1
10
28.3
22.5
10 minutes 30 minutes
28.6
30
50
28.6
30 minutes 1 hour
14.3
50
15
21
More than 1 hour
10
10
6.7
7
Source: Field Survey, 2025
Time it takes to get there, get water and come back
From Table 4 shows regarding time it takes to go to the water source, get water and come back, the
respondents reported 28.6% get in 10 minutes 30 minutes, 22.5% said in less than 10 minutes and 21% 30
minutes 1 hour in all the LGAs respectively. The highest response on short time to get water was found in
Bama 47.1% and longest time in Chibok 50% (Table 4). According to UNDP (2019), when a household
spends at least 30 minutes’ walk from home roundtrip in order to access domestic water, such a household is
considered deprived in accessing domestic water supply, a limitation which undermines their ability to combat
multidimensional poverty. The time spent and distance roundtrip does not only stress the individual in walking
and conveying the water, but could degenerate to reluctance in fetching water. This is interconnected to
underusing the resource and degenerates to problems of poor sanitation and human health, while increasing
vulnerability to poverty. Findings from this study reveal that respondents from across the selected communities
varies as response on short time to get water was found in Bama 47.1% and longest time in Chibok 50% (Table
4).
Table 5: How many trips do you make to the water source daily
Number of Trips
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
1 trip
24.3
25.8
38
23.2
2 trips
57.9
60
41
41.8
3 trips
17.8
11.7
8
9.9
More than 3 trips
0
2.5
13
4.1
Source: Field Survey, 2025
Trips to the water source daily
Regarding the number of household’s trip to the water source on daily basis, majority of the respondents
41.8% reported 2 trips, 23.3% one trip, 9.9% said 3 trips and only 4.1% said they get more than 3 trips daily.
Table 2: The cost of buying drinking water for household
Cost Category
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Expensive
16
20
16
13.7
Moderate
12
28
21
16.1
Cheap
30
20
41
23.9
No cost
42
32
22
25.3
Source: Field Survey, 2025
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The Cost of Buying Water
Data on the cost of buying water for households in the survey areas revealed that majority of the respondents
25.3% buy water at no cost and 23.9% of the population reported the cost of buying water as cheap, while
16.1% of the respondents find it moderate. A least percent 13.7 of the respondents get their water supply at
expensive rate. This result indicates a general lower cost of buying water for households in almost all the
communities surveyed. This is due to the fact that private boreholes are the primary source of water supply to
the respondents, which they arrive at no charge. However, water is meant to be cheap for all. The government
still needs to improve water supply for all citizens.
Table 6: Duration of storing drinking water in your household
Duration
Bama
(%)
Chibok
(%)
Kaga
(%)
Total
(%)
1 day
40
20.8
41.7
27
2 days
44.3
64.2
43.3
39.9
5 days
15.7
15
4.2
9.2
7 days
0
0
5.8
1.5
Others
0
0
5
1.3
Source: Field Survey, 2025
Storage of drinking water for households
Results in Table 6 revealed the large number of respondents 39.9% reported they do stored their water for 2
days. This followed by 27% respondents who also reported storing water for only 1 day. Other responses
reported 9.2% 5 days, 1.5% 7 days and 1.3% reported others. The contributing factor is the fact there is a
constant supply of water from the public, private and commercial boreholes in all the communities surveyed in
the three LGAs. This is due to continuous supply of water from solar power and rare generators.
Table 7: Persons responsible for fetching drinking water for the household
Category
Bama
(%)
Chibok
(%)
Kaga
(%)
Total
(%)
Girls (under 18 years)
50
48.2
52.5
39.7
Boys (under 18 years)
5
6.7
2.5
3.7
Women
22.9
34.2
14.2
18.8
Men
7.1
4.2
5
4.3
Water vendor
15
0
25.8
10.7
Source: Field Survey, 2025
Persons responsible for fetching drinking water for the household
The analysis in Table 7 reveals that persons responsible for fetching water in the households shows 39.7% girls
under 18 years, 18.8% adult women, 10.7% water vendor, 4.3% boys under 18 years and 3.7% Adult men.
Although, the practice of whom responsible for fetching water for the household vary among the LGAs. The
highest number of girls under 18 years were recorded in Kaga 52.5%, while for boys under 18 years were seen
in Chibok 6.7%. Also, adult women were mentioned in Chibok 34.2% and adult men in Bama 7.1%. Water
vendors were mainly reported highest in Kaga 25.8%.
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SECTION C: WATER TREATMENT METHODS AND RELATED ILLNESSES
Table 8: Water Treatment Methods and Related Illnesses
Water treatment for safe drinking
Yes 32.9 54.2 20.8 28.4
No 67.1 45.8 79.2 50.6
Methods of water treatment
Boiling 44.3 15.0 25.0 22.2
Chlorination 41.4 33.0 66.0 36.9
Filtering 5.0 23.0 8.0 9.8
Strain with clothing material 5.0 21.0 1.0 7.1
Others 4.3 8.0 0.0 3.2
Last time of water treatment
Previous day 3.6 32.5 2.5 10.2
Less than a week 8.6 16.7 4.2 7.8
Less than a month 17.1 14.2 17.5 12.8
More than a month 25.0 8.3 60.0 24.6
Dont remember 45.7 28.3 15.8 23.6
Have you experience any illnesses in your households in the past 6 months
Yes 59.0 62.0 16.7 36.2
No 41.0 38.0 83.3 42.7
If yes, specify the illnesses
Diarrhea 7.1 4.2 12.3 6.2
Cholera 1.4 32.5 1.7 9.4
Typhoid 91.5 41.6 75.0 54.8
Hepatitis A 0.0 0.0 8.3 2.2
Others 0.0 21.7 2.7 6.4
Source: Field Survey, 2025
Response on Water treatment for safe drinking
From Table 8 responses to water treatment by the respondents in all the LGAs revealed more than half 50.6%
of the households reported did not treat their water before use. The vast majority of respondents that get their
water from boreholes and wells water sometimes do not address the water treatment because they assume that
the borehole and wells water is already clean for usage. Accessing improved water sources for drinking
typically comes through hand pumps or boreholes, rather than piped connections. However, various sources
indicate widespread challenges with infrastructure in all the communities surveyed due to partially
functionality or not functional boreholes or hand pumps and most privately constructed water sources are not
adequately designed to eliminate contamination. While some proportion of respondents 28.4% said they
always treat the water through boiling. The highest 79.2% was found in communities under Kaga L.G.A and
the least 45.8% was in Communities under Chibok L.G A. Other persons who were unsure stated that they buy
sachet water rather than drink the borehole water because they are not sure of the pure nature of the borehole
water source.
Methods of water treatment
The data revealed that the practice of chlorination of water was seen higher 36.9% among the selected
communities in all the three L.G.As to make water safe (Table 8). Other methods of water treatment in the
areas shows boiling 22.2%, through filtration 9.8%, strain with clothing material only 7.1% and others 3.2%.
These methods were common in all communities in the three selected LGAs and were visible practices to most
households. Certain proportion of respondents even reported that they do not practice any of the water
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treatment methods and that water they used was already clean and safe and to them treated water did not taste
good therefore, avoiding any form of treatment.
Last time of water treatment
Regarding responses on when last they treated water for safe drinking, the households responses were more
than one month 24.6%, less than a month 12.8%, previous day 10.2% and less than a week 7.8%, and some
respondents don’t remember 23.6%. Although, there were interventions by UNICEF, ICRC and Borno State
rural water Supply and Sanitation (RUWASSA). A significant observation from the data is that unsafe water
sources were predominant before this WASH intervention. Since the data indicates some communities relied
on open wells 14% and rivers/streams 1.4% and water truck 1.1% as other sources of drinking water. These
sources are typically unprotected and highly susceptible to contamination, particularly during the rainy season
when runoff can carry fecal matter, debris, and other pollutants into the water supply. This situation posed a
high baseline risk of waterborne diseases such as cholera, typhoid, and diarrhea within the affected
communities. High rates of unimproved water usage for drinking is generally due to accessing water from
unprotected wells in most LGAs.
Have you experience any illnesses in your households in the past 6 months
Majority of the respondents 42.7% reported they did not experience any illnesses related to water treatment in
their households in last six months. However, some respondents 34.2% said yes their households witnessed
some illnesses during the last six months. If yes, specify the illnesses experienced in the selected communities
in the three LGAs in the last six months, the responses were Typhoid 54.8%, Cholera 9.4%, others 6.4%,
Diarrhea 6.2%, and Hepatitis 2.2%. These illnesses experience in some of the communities were not
unconnected with the activities of households contaminating sources of water. Despite majority of the
population accessing the main source of drinking water from improved sources, the level of spread of Typhoid
in all the LGAs as shown in Table 8 raises major concerns about water quality and contamination. This large
outbreak could be attributed to widespread contamination of sources.
Section D: Storage Of Household Drinking Water Facility
Table 9: Storage of Household Drinking Water Facility
Storage Facility Type
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Open container
20.0
16.7
8.0
11.8
Plastic covered container
37.1
48.3
59.9
38.2
Clay pots with cover
32.9
35.0
18.0
22.6
Clay pots without cover
10.0
0.0
3.0
3.4
Iron buckets without cover
0.0
0.0
9.0
2.3
Plastic buckets with tap
0.0
0.0
3.0
0.9
Basin without cover
0.0
0.0
0.0
0.0
Others
0.0
0.0
0.0
0.0
Table 2: Items Used in Fetching Drinking Water from
Storage Facility
Item Used
Bama
(%)
Chibok
(%)
Kaga
(%)
Total (%)
Cup with
handle
60.7
62.5
66.7
50
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Cup
without
handle
27.1
19.1
30.8
20.3
Calabash
7.9
11.7
2.5
5.8
Bowl
4.3
6.7
0
2.9
Others
0
0
0
0
Table 3: Frequency of Cleaning Water Storage Container
Cleaning
Frequency
Bama
(%)
Chibok
(%)
Kaga
(%)
Total (%)
Every day
37.1
19.2
31
23
Before
fetching water
11.4
61.6
28
26.6
When dirty
48.6
19.2
41
28.6
Never
2.9
0
0
0.8
Table 4: Perceived Quality of Safe Drinking Water
Quality
Indicator
Bama
(%)
Chibok
(%)
Kaga
(%)
Total (%)
Visually
clear
65
54.2
15
35.3
Sweet
taste
10.7
19.2
15.8
12
Odourless
16.4
13.3
69.2
26
Salty
5
8.3
0
3.5
Free from
germs
2.9
5
0
2.1
If animals
can drink
0
0
0
0
Others
0
0
0
0
Source: Field Survey, 2025
Type of drinking water storage facility
From Table 9 responses from households shows that majority of the facilities used for storing drinking water
were 38.2% plastic covered container, 22.6% clay pots with cover, 11.8 open container, 3.4% clay pots with
cover, 2.3% Iron buckets container without cover and 0.9% plastic buckets with tap. Water storage facility
that mentioned often by respondents in all the surveyed LGAs was plastic covered container. Nonetheless,
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majority of the respondents used clay pots with cover in Chibok 35%, which is slightly similar to what is
obtainable in Bama 32.9%.
Item used in fetching drinking water from storage facility
A closer look at the responses regarding items used in fetching drinking water from the storage facility, the
analysis shows cups with handle 50%, cups without handle 20.3%, calabash 5.8% and bowl 2.9%. The items
used in fetching water were mostly kept on the storage container or hung on the wall. These practices of using
different common containers look similar in all the selected LGAs as depicted in Table 9. The result indicates
that most of the communities in all the LGAs reported cup with handle is the most common item used in
fetching water for drinking in majority of households. Perhaps, it is important to note that using a container
with handle can helps in promoting the quality and safety of water for drinking.
Cleaning water storage container
The response about cleaning of storage containers, vast majority of respondents 28.6% said they clean their
water storage facility when dirty was seen higher in all the LGAs , while those who reported cleaning the water
storage facility before fetching water is 26.6% as shown in Table 9. Cleaning of the storage facilities was done
daily 23% and never 0.8%. Again, the frequency of cleaning varied widely across the LGAs.
Quality of safe drinking water
From the results, the respondents clearly mentioned their views regarding qualities of safe drinking water such
as visually clear 35.3%, Odourless 26%, sweet taste 12%, salty 3.5% and free from germs 2.1% in all the
communities surveyed. The primary source of water for households determines the quality of water used by the
household. This, in turn, affects the amount of water intake available to members of the household. From the
result it shows borehole is the dominant source of drinking water for the households. As such, least problem of
water quality related issue from the sources. The widespread access to improved water sources, particularly
boreholes, is likely to result in lower rates of waterborne illnesses, better hygiene practices, and overall
enhanced health outcomes. Moreover, the reduced need to travel long distances to fetch water may
significantly lessen the burden on women and children, who are typically responsible for water collection. This
change could translate into greater time for education, economic activity, and personal wellbeing, thereby
contributing to long-term community development and resilience.
Means of transportation used in fetching the water
Results concerning the means of transportation used in fetching water in the household shows majority of the
respondents 62.3% reported by bicycle. This followed by pay others 40.6%, by foot 33.4%, animal or drawn
cart 18.3%, and motor vehicle 14.2% as shown in Table 9. The results exhibit bicycle as means of transport in
Chibok LGA, while respondents in Bama and Kaga reported utilizing foot as the major means of transporting
water in their areas (Table 9). Most of the households mentioned that their transport means was bicycle,
however, frequently employed was by foot in Kaga 54% and the least was motor vehicle reported also in Kaga.
Section E: Sanitation Facility of the Hosueholds
Table 10: Sanitation Facility of the Households
Type of Toilet Facility
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Private latrine
60
30
53.3
37.7
Shared latrine
35.7
36
46.7
31.2
Communal toilet
0
28
0
7.4
Open defecation
4.3
3
0
1.9
Others
0
3
0
0.8
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Table 4: Perceived Quality of Safe Drinking Water
Quality
Indicator
Bama
(%)
Chibok
(%)
Kaga
(%)
Total (%)
Visually
clear
65
54.2
15
35.3
Sweet
taste
10.7
19.2
15.8
12
Odourless
16.4
13.3
69.2
26
Salty
5
8.3
0
3.5
Free from
germs
2.9
5
0
2.1
If animals
can drink
0
0
0
0
Others
0
0
0
0
Table 3: Number of Households Sharing the Facility
Number of
Households
Sharing
Bama
(%)
Chibok (%)
Kaga
(%)
Total (%)
12 households
67.9
65.8
56
50.6
35 households
25
34.2
16
19.8
More than 5
households
7.1
0
28
9.2
Table 4: Views About Cover of the Facility
View
Bama
(%)
Chibok
(%)
Kaga (%)
Total (%)
Always
47.9
56.7
18
32.3
Sometimes
42.9
25.8
66.6
35.6
Never
9.2
17.5
4
8.1
Dont
know
0
0
11
2.9
Sanitary facility
The situations of sanitation facilities across the three local government areas under study were analyzed. The
analysis revealed majority of the households 37.7% use private latrine and 31.2% use shared latrine. While,
7.4% of the households use communal toilets as well as 1.9% and 0.8% of households use open defecation and
others respectively. The overall situation for sanitation is more concerning still. Use of unimproved sanitation
appears to be common across the communities in the three senatorial zones. Access to sanitation continues to
be diminished due to wear and tear of emergency-type construction, continuous displacements and seasonal
flooding, all of which contribute to higher open defecation rates, reduced levels of hand washing practices, the
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adoption of negative coping mechanisms and associated loss of dignity and gender-based violence risks. It is
important to note that sanitation needs for persons with special needs, women and children to ensure safety and
equitable access are a critical gap compounded by overcrowding and financial constraints to construct
sanitation facilities have been the major impediments. However, this is not withstanding water and sanitation
are essential in ensuring healthy living (WHO & UNICEF, 2017).
Toilet facility shared among households
Regarding the household latrine accessibility, approximately 38.4% of households reported sharing latrines
with others, while 35.5% households reported not sharing their latrines. The most commonly reported types of
latrines were pit latrines 37.7%. The data indicate a high proportion of respondents used shared toilet facilities.
Some of these toilets facility may be structurally improved, shared facilities are generally considered
unimproved by global standards due to concerns over privacy, cleanliness, and maintenance. Shared use can
increase the risk of disease transmission and may compromise the safety and dignity of users, particularly in
overcrowded or underserved areas. Sharing sanitation facilities is common especially in Bama 63.6% and
Kaga 46.7%, where the data further revealed majority of households shared with at least one other household.
These combined sanitation conditions pose a high risk of adverse public health outcomes. Limited access toilet
facility as has been consistently shown by the responses, heightening the risk of communicable disease
outbreaks and public health crises (UNDP, 2021). The practice of shared toilet facility has placed a strain on
already underdeveloped services, including water and sanitation infrastructure (UNDP, 2021).
Number of households share the facility
Regarding household latrine accessibility, findings show 50.6% households shared latrines ranged 1 - 2 and
19.8% reported more than 5 households shared the toilet facility, while only 9.2% households shared toilet
facility among 3 -5 households. These combined sanitation conditions pose a high risk of adverse public health
outcomes. The prevalence of shared toilet facility practice suggests that basic sanitation infrastructure was
either inaccessible or unaffordable for a significant portion of the population in all the communities across the
LGAs. Hence, households resorted to using shared facilities.
Views about cover of the facility
Regarding views about covering of the toilet facility among the households in all the three LGAs, result
reveals 35.6% reported they cover toilet facility sometimes while 32.3% opined they cover their toilet facility
always. The analysis also revealed 8.1% of the households in all the said never they cover their toilet facility
and 2.9% reported they dont even know about it.
Section F: Perception Of A Good Toilet, Type and Preferred Ownership
Table 11: Perception of a Good Toilet, Type and Preferred Ownership
Perception Category
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Privacy
17.9
42
7
17.6
Safety
53.6
30
64
38.8
Prevent disease
25.7
14
19
15.4
Easy to use
2.8
14
10
7.1
Table 2: Type of Toilet Preferred
Toilet Type
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Flush
40.7
33
31.5
27.7
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Traditional pit
54.3
60
59.2
45.7
Others
5
7
9.5
5.7
Table 3: Affordability of Preferred Toilet Type
Response
Bama
(%)
Chibok
(%)
Kaga
(%)
Total (%)
Yes
63.6
81.7
64.2
55.1
No
33.6
18.3
35.8
23.1
Table 4: Views About Exposed Excreta of Children
View
Bama
(%)
Chibok
(%)
Kaga
(%)
Total (%)
Harmful
70
49.2
47.5
43.9
Harmless
1.4
20
42.5
16.8
Dont know
28.6
30.8
10
18.3
Perception of a Good Toilet, Type and Preferred Ownership
The analysis on the responses of households across the LGAs about a good toilet, the type of toilet and
preferred ownership in Table 11.
Perception of a good toilet
The analysis regarding perception of a good toilet across the three LGAs, 38.8% of the respondents expressed
their opinion that safety were the most responses. The respondents also reported privacy 17.6%, disease
prevention 15.4% and easy to use 7.05% were the responses.
Type of toilet preferred
The data regarding preferred toilet type, respondents reported traditional pit 45.7% was the most preferred type
of toilet in all the communities of the three selected LGAs. Some respondents reported they preferred flush
toilet 27.7% and 5.7% preferred other toilets.
Affordability of preferred toilet type
Information on affordability of preferred toilet type, 55.1% respondents said yes they could afford the
preferred toilet type and only 23.1% said they could not afford the preferred type of toilet facility.
Views about exposed excreta of children
The information about respondent’s perception on exposed excreta of children, 43.9 % reported that children’s
faeces are harmful while 16.8% reported children’s faeces are harmless and 18.3% reported don’t even know
about it. The practice of exposed excreta is only harmful to the people living in that locality, but also exposes
the water sources, especially the surface water sources such as ponds and lakes in the rural communities are at
the risk of contamination and health related issues.in the environment at large.
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SECTION G: PRACTICE OF PERSONAL HYGIENE
Table 12: Practice of Personal Hygiene
Hygiene Practice
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Use of soap
23
44.2
32
26.1
Washed clothes
10
15
16
10.8
Took my bath
7
15.8
5.3
7.4
Washed hands after
preparing food
11
4.2
6.7
5.8
Washed hands before
feeding child
10
3.1
7
5.3
Washed hands before
eating
5
3.5
8
4.3
Washed hands after
defecation
34
14.2
25
19.3
Time to Wash Hands
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Before meal
33.6
60.8
50
38
After meal
17.1
7.5
9.2
8.9
After defecation
25
24.2
21.3
18.6
After cleaning childrens
faeces
19.3
5
11.5
9.4
Others
5
2.5
8
4.1
Item Used
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Water only
22.9
28.3
21
19
Water and soap
60.7
55.3
71
49.2
Water with ashes
11.4
10
5
6.9
Sand and water
5
6.2
3
3.7
Others
0
0.2
0
0.1
Response
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
No
64.3
59.2
61.7
48.7
Yes
35.7
40.8
38.3
30.2
Hygiene Practice
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Bathing
52.9
51
64
44.2
Weaving/Cutting hair
22.1
18
12
13.7
Washing clothes
18.6
28
20
17.5
Cutting nails
6.4
3
4
3.5
Personal Hygiene
Data about personal hygiene of the respondent’s exhibits respondents had poor knowledge of hygiene with
regards to hand hygiene, bathing, and clothes hygiene, irrespective of their educational level. The results show
26.1% of respondents reported use of soap as the major opinion in all the selected LGAs for the domestic
washings. The respondents also reported washing hands after defecation 19.3%, washed clothes 10.8%, and
taking bath 7.4%, washing hands after preparing food 5.8%, washing hands after feeding child 5.3%, and the
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least reported was washing hands before eating 4.3%. It was noticeable that most respondents did not received
any special training on hygiene yet observed some recommended hygienic practices.
Health Consequences of poor hygiene lead to the transmission of pathogens through faecal-oral pathway.
Diseases transmitted via the faecal pathway are diarrheal and other diseases. In this study, hand washing
practice before meal was least in this study. Critical hand washing was preferred as the best washing practices
but it was not high in this study. The study revealed that personal hygiene with regards to hand hygiene
(washing with soap and clean fingernails) and regular bathing were not properly been practiced by the
households. The result shows. This is incongruent with the report by OCHA (2004) stated that colossal number
of people practiced good hygiene, which revealed that more than half (54%) of the global population
maintained good personal hygiene.
Important time to wash hands
Regarding important time to wash hands, the analysis shows majority opinion among the respondents from the
study LGAs claimed to wash hands before meal 38%, after defecation 18.6% and after cleaning childrens
faeces 9.4%. Small percent or respondents admitted to wash hands after meal 8.9% and others 4.1%. Improved
hand hygiene has been recognized as an essential public health measure. Thus, proper hand washing remains
the most effective way of removing germs and harmful bacteria from our hands. This, in turn, helps to prevent
the spread of diseases and keeps our environment safe, fresh, and clean.
Opinion on items for washing hand after cleaning child defecation
The opinion of the respondents regarding washing their hands after cleaning child defecation, the result shows
on average, 49.2% reported using water and soap, those who said only water 19%, water and ashes 6.9%, 3.7%
sand and water 3.7% and others 0.1%.
Functional hand hygiene facility within 5 meters of latrine
Regarding functional hygiene facility within 5 meters of latrine in households, majority 48.7% reported yes
while 30.2% said there was no functional hand hygiene facility within the short distance.
Hygiene practices
Awareness of personal hygiene practice in households, the result shows close to 44.2% of the respondents
reported bathing, 17.5% washing clothes, 13.7% weaving and or cutting of hair and 3.5% cutting of nails were
practices referred to as household and environmental hygiene by the respondents. This level of awareness is
common to all the studied LGAs as shown in Table 12.
Section H: Site Check Observations
This section presents information on physical observations around the compound.
Table 13: Type of faeces around the premises
Type of Faeces
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Infant/young children’s faeces
34.3
35
28.3
25.7
Adult’s faeces
20
21.7
23.4
17.1
Cow dung/other animal excreta
45.7
43.3
48.3
36.1
Toilet Type
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Traditional pit toilet
59.3
56.7
50
43.7
Dig, defecate and bury in soil
5
11.7
7
23.7
Improved pit toilets
18.6
23.3
21
16.6
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VIP toilets
5
8.3
7
5.3
Water closet toilets
12.1
0
15
7.1
Place of Defecation
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Around the house
10.7
20.8
27.5
15.5
In the potty/chamber pot
12.1
10.8
4.2
0.7
In the toilet
20
31
50
26.6
In the pampers
54.3
36.7
7.5
25.9
Within the compound
2.9
0.7
15
4.9
Others
0
0
0
0
Disposal Method
Bama (%)
Chibok (%)
Kaga (%)
Total (%)
Dropped into a toilet facility
62.9
72.5
70.3
54.1
Eaten by animals
9.3
5.5
4.2
5
Buried in the soil
8.6
5
9.7
6.1
Thrown into the bush
1.4
7.8
2.8
3.2
Disposed with solid waste
16.4
8
10.8
9.3
Do nothing / left it there
1.4
1.2
2.2
1.3
Source: Field Survey, 2025
Site check observations
Type of faeces around the premises
During the survey, most commonly observed faeces in the premises of the households and water sources are
31.6% Cow dungs/other animal excreta, 25.7% Infant / young children’s faeces and 17.1% adults’ faeces. It
also observed that during the survey of the communities in the three LGAs, Cow dung / other animal excreta
were commonly practice in Kaga 48.3% and Infant / children’s faeces were conspicuous seen in the premises
in Bama, while adult’s faeces was prevalent in Kaga.
Type of toilet observed in households
Physical observations shows traditional pit toilet system 43.7% were the most common form of basic toilet
facility observed in households, use by nearly a half of total population in all the communities of the three
LGAs. This is because. These facilities are used because they are not expensive, with maintenance at ease and
some respondents cannot afford standard toilets facilities.
The check observations further reveals dig, defecate and burry in soil 23.7%. Toilet facility is not commonly
available in these communities to the global standard, likely because majority of the population lives in
traditional buildings which have not been constructed with modernized toilet facilities. However, the data
indicates those use improved pit toilets 16.6%, while water close toilets 7.1% and VIP toilets 5.3%. The result
shows Bama having the highest number of households using the Traditional pit toilet while improved pits and
VIP toilets were both highest in Chibok 23.3% and 8.3% while water close toilet were observed to be 15% and
12.1% in Kaga and Bama LGAs respectively. Although the pits latrine represent a step up from open
defecation, many pit latrines are unimproved or poorly constructed. These conditions pose hygiene and safety
risks, especially in areas prone to flooding or with high water tables, where contamination of groundwater is a
concern.
Children under-5 defecation
Regarding children’s under - 5 defecation, it was observed that children’s defecate in the toilet 26.6% is the
most common practice observed, which similar in all the areas surveyed. Those defecate in pampers 25.9%,
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around the house 15.5% in the potty or chamber pot 7.1% and within the compound 4.9%. The result further
demonstrates defecation in pampers is most common in Bama 54.3%, Chibok 36% and Kaga 7.5%. Also,
defecation in the toilets were more frequent in Kaga 50%, Chibok 31%, and Bama 20% respectively. Around
the house 27.5% and within the compound 15% were both common in Kaga. The use of potty/chamber pot is
more frequent in Bama 12.1%) and Chibok 10.8%. Despite the widespread use of unimproved facilities, the
proportion of households using open defecation is generally low 4.9% within compounds across the three
LGAs. This result is consistent with the outcome of research by IMPACT, 2021 which very low percent of
open defecation by residents in Borno State.
Understanding of disposal of children’s faeces
The descriptive analysis on perception of respondent’s shows 54.1% reported dropped into toilet facility and
was the commonest disposal method in all the communities surveyed. Disposed with solid waste 9.3% and
some respondents 6.1% claimed that they buried in the soil. In the households, 5% said eaten by animals, 3.2%
and thrown into the bush and do nothing or left it there were 1.3% respectively. This system of waste disposal
implies that it does not only destroy the aesthetics of the environment, but it also attracts vectors of various
diseases, which can pose a severe health risk to the residents of such locality because it causes serious air and
water pollution in the environment.
DISCUSSIONS
The overall analysis of WASH practices in the study areas show various sources of water for water supply
across the selected L.G.As communities. This implies various sources of water supply in the study
communities are generally utilized equally across the selected communities of three senatorial zones of Borno
State. Clean source of drinking water is essential to healthy living (IWA/WHO, 2011). In the study area, water
supply has been insufficient in all communities surveyed, Water, sanitation and hygiene (WASH) conditions
are being driven by the ongoing insurgency, climate change and desertification, and associated displacement.
This is likely driven by poor access to improved sanitation, water quality issues, and low levels of access to
basic hygiene.
However, this narrative have been changed with increased community participation and the perceived
inclusiveness of the intervention programs by NGOs and private individuals such as such as I.C.R.C in Bama,
MOI in Kaga and others in providing water supply facilities such as solar powered bore holes, hand dug wells,
hand washing facilities among others in the surveyed areas (Figure 2, 3 & 4). However, these facilities are
inadequate and functional because of the intervention programs across the communities. Thus, these
communities now largely depend on relatively protected boreholes for drinking water supply. These
interventions significantly improved access to clean water and sanitation for hundreds of thousands of
residents, contributing to better health outcomes, reduced disease transmission, and enhanced dignity and
quality of life particularly for women and children.
The solar-powered boreholes, in particular, offer a sustainable and energy-efficient solution, ensuring
continuous access to water even in remote or off-grid communities. This report on the use of protected bore
holes and hand dug wells is contrary to studies in arid regions by Mustapha et al., (2022); Kurui et al., (2019)
and Morales et al., (2020), where most communities consumed unprotected springs, subterranean water and
unprotected wells as their major water source.
The study shows large participation of young girls and boys in fetching water in this study is consistent to the
practice in Nigeria and in many African countries, where women and children were mainly the group
responsible for fetching water (Mustapha et al., 2022; Adeleye et al., (2014), Across the studied communities,
children and womens involvement in water fetching was essentially based on cultural practices. The water
stress in the study area has subjected many young girls and women in the communities to hardship of water
fetching as it affects many of their other livelihood activities (Adeleye et al., 2014).
This study demonstrates that various storage facilities were used and that storage facilities were mostly
covered by majority of the respondents. The findings show most commonly used facility is plastic cover
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container. This is similar to reports by Reddy et al. (2017); Pradhan et al. (2018); and Semugabo et al. (2019)
and Sridhar et al. (2020). Household water collection and storage practices are integral to safeguarding
waterborne disease infections (Mbuka-Nwosu et al., 2022).
General perception regarding items used in fetching drinking water from storage facility shows quite a large
number of respondents reported cups with handles (50%) were mainly used to fetch water as, which is critical
in avoiding tendencies of household water recontamination (Edokpayi et al., 2018). The result shows very low
perception of cleaning storage facility as vast majority of respondents 28.6% said they clean their water storage
facility when dirty was seen higher in all the LGAs, uncovered and uncleansed storage containers make water
vulnerable to contamination and diseases (Meierhofer et al., 2019).
This study shows various methods were used for water treatment. Chlorination was the commonest method
used among households (36.9%) while 22.2% of respondents used boiling method because it was relatively
cheap and quite effective especially in the rural areas. 9.8% of participants stated they practices treating their
water through filtration method. This method was relatively cheap and quite effective, particularly with less
turbid water (Okwadha and Ahmed, 2017), therefore, preventing the outbreak of bacterial diseases (Huq et al.,
2010).
The study also shows responses on water treatment practices were generally low as most participants did not
treat their household’s water for drinking. The absence of home treatment practices is consistent with many
communities across developing countries, as shown by various researchers (SNRA, 2024; Mustapha et al.,
2022; Mbuka-Nwosu et al., 2022; Genet and Desta, 2017; Bitew et al., 2017), especially in the rural areas. The
practice was however, less frequent in the study areas as quite a large proportion has not treated water for more
than a week, similar to Mustapha et al. (2022) report. Improvements in drinking water through household
water treatment can significantly reduce waterborne disease infection and transmission among people
(WHO/UNICEF, 2019). Most respondents stated the reason for not treating their water for drinking, replied
that water was clean and safe to drink.
The study shows lack of unimproved toilet facilities in the study areas have led participants to the improper
practice of open defecation both in communities and at households, which is a serious public health and
environmental consequences (Bawankule et al., 2017). The study identified some environmental sanitation
facility challenges such as shared household toilet facilities, inconsistency in cleaning, and odour from the
toilet facility within households. This is congruent to studies in developing countries (Orimoleye et al., 2015;
Reddy et al., 2017) that shows the practice of improper excreta disposal, especially around water sources that
may dispose communities to water disease (Okullo et al., 2017).
This is not unconnected with low income level of most respondents was the reason for unavailability of
improved toilets. This assertion agrees with the results of Sridhar et al. (2020). Poverty is one of the major
barriers to WASH access and affordability among people (NSC, 2022). Although children’s faeces were
largely perceived harmful, children were commonly defecating around the houses and the faeces were disposed
improperly in the bush. This finding is similar a study by Sridhar et al. (2020) in Kaduna, Northwestern
Nigeria, where majority disposed childrens faeces in a toilet facility. However, it sharply contradicts the
report of Mustapha et al 2022 in Sokoto, Semi-Arid, Northwestern Nigeria.
Regarding personal hygiene practice, this study shows a very low level hygiene practice, as few participants
responses indicates using water and soap for hand washing after defecating and cleaning children’s faeces,
which could transmit disease and cause illness (Dey et al., 2019). This findings contradicts other studies in
Nigeria by Mustapha et al. (2022) in Sokoto, Sridhar et al (202) in Kaduna; Miner et al. (2016) in Jos and
Orimoleye et al. (2015) in Ibadan in which hand washing with soap was largely practiced.
This finding revealed a low level of knowledge of household and environmental hygiene in the study areas, as
quite a large number of respondents clean their compounds. However, indiscriminate dumping was a common
waste disposal practice and water stagnation within and around water points was largely reported and
observed. The stagnant water could lead to proliferation of mosquitoes and consequently occurrences of high
malaria as perceived in the communities. Also, in the study areas, majority of the respondents said typhoid and
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diarrhea were the common perceived household and communities’ illnesses across the surveyed areas. This
could be attributed to bad environmental hygiene practices such as water stagnation around the premises and
the high use of water from unsafe sources of unprotected wells, this in tandem with low level practice of
effective water treatment practices.
CONCLUSION
This study established that water supply is fairly adequate largely due to involvement of Non-Governmental
Organizations and private individuals on intervention programs that provides vast majority of the people with
water supply from boreholes. This could be attributed to solar powered boreholes from interventions that
constantly pumping water from the boreholes to the overhead tanks is still a significant issue. These WASH
intervention programs have immensely contributed to public health, social stability, and resilience in semi-arid
Borno. The analysis reveals that inadequate infrastructure is key to persistent WASH challenges, particularly
across all the surveyed communities, resulting to poor health conditions and bad economic opportunities. The
knowledge and practice of Water, Sanitation and Hygiene (WASH) in the surveyed areas is still poor. The
knowledge of WASH and practices of Water, Sanitation and Hygiene (WASH) at those selected communities
are critically poor.
The results of this study have well provided useful information on the consequences of poor hygiene practices
and sanitation facilities for both residents and authorities. The data can serve as a blueprint to the government
or private organizations working towards upgrading the standard of WASH practices in the state. It will also
help in identifying gaps and challenges in the provision of Water, Sanitation, and Hygiene practices and offer
recommendations.
RECOMMENDATIONS
1. There is need for collaborative effort that encourages participation of government, private sector
partners and local communities to invest in invest in water infrastructure, enhance sanitation services,
and support hygiene education initiatives.
2. Public and private stakeholders should advocate and encourage community participatory sanitation and
hygiene practice activities at households, community and state at large.
3. A behavioural change is needed among residents to have the knowledge of good WASH practices.
WASH education and financial empowerment are necessary towards protecting public health in the
study area. .
4. The need for construction of standardized latrines and hygiene education for community members to
help them develop good hygiene practices, particularly for women and children responsible for water
collection.
5. Installation and setting up of maintenance and management systems for drinking water points and the
implementation of hygiene and sanitation trainings as well as close collaboration with local authorities
for the management and maintenance of the installed systems.
6. Seasonal monitoring of water sources and consumption patterns would help assess variability and risk
throughout the year.
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