ABSTRACT
The bacteriological and physico-chemical characteristics were carried out for fifteen boreholes in three selected hospitals in Umuahia. The bacteriological analysis was carried out using the Most Probable Number Technique (Multiple-Tube Technique) for the detection of faecal coliform and subsequently organisms present in the samples of water were identified following the Standard Methods. The identified organisms include: Escherichia coli, Staphylococcus aureus and staphylococcus epidermidis. The Total Heterotrophic Plate Count (THLPC) gave a range of 1.5 x103-20.0 while the Total Conform Plate Count (TCPC) gave a range of 1 .0 x103-10.5 x103CFU mL-1.The presumptive faecal coliform ranged between 0-180 coliforms 100 mL-1 giving a mean of 18.73 coliforms per 100 mL. E. coli faecal coliforms were detected in 60% of the water samples. The aesthetic properties of the water samples were acceptable in comparison with local and international standards. These results showed that there is need for treatment of these water boreholes by the borehole proprietors and also by simple treatment methods such as boiling and agitation by the consumers.
TABLE OF CONTENT
Title Page i
Declaration ii
Certification iii
Dedication iv Acknowledgements v
Table of Contents vi
List of Tables viii
Abstract ix
CHAPTER
ONE: INTRODUCTION 1
1.1
Background to the study 1
1.2
Problem statement and Justification 2
1.3 Aims
and Objectives 2
1.3.1
Specific objectives 2
1.4
Significance of the study 3
CHAPTER
TWO: LITERATURE REVIEW 4
2.1
Bacterial Water Quality 4
2.2
Water Quality Changes 4
2.3 Water Quality Challenges 5
2.4
Biological Indicators of
Water Quality 6
2.4.1
Heterotrophic plate counts 6
2.4.2 Thermotolerant
coliforms 7
2.4.3
Faecal Streptococci and
Enterococci 8
2.4.4 Pathogenic
bacteria 9
2.4.4.1 Salmonella spp. 9
2.4.4.2 Shigella spp. 10
2.4.5
Bacterial water quality risk assessment 11
2.4.6
Physico-chemical indicators of water quality 11
2.4.6.1
Hydrogen ion potential – pH 11
2.4.6.2
Turbidity - NTU (Nephelometric Turbidity Units) 12
2.4.6.3 Total
organic carbon (TOC) 12
2.4.7 Water
pollution by organic matter 13
2.5 Common Water Treatment Methods 14
2.5.1 Solar disinfection 14
2.5.2 Chemical
water treatment methods 14
2.5.2.1 Alum
coagulation 14
2.5.2.2
Chlorine treatment 15
2.5.3
Treatment with plant extracts 15
2.6 Microbial Reduction by
Coagulation-Flocculation 16
CHAPTER
THREE: MATERIALS AND METHSODS 18
3.1
Sample collection 18
3.2 Media Preparation 18
3.3
Physico-chemical Properties 18
3.3.1 pH 18
3.3.2
Temperature 18
3.3.3
Electrical conductivity 19
3.3.4
Dissolved oxygen 19
3.3.5
Turbidity 19
3.4 Most
Probable Number (MPN) of Total and Faecal Coliforms per 100 ml 19
3.4.1
Presumptive test 20
3.4.2
Confirmatory test 20
3.4.3
Completed test 21
3.5
Faecal Coliforms (thermotolerant Escherichia coli) 21
3.5.1
Confirmatory test 21
3.5.2
Completed test 21
3.5.3
Heterotrophic plate counts 22
3.6 Identification of Bacteria 22
3.6.1 Gram
staining 22
3.6.2
Oxidase test 22
3.6.3
Motility test 23
3.6.4
Indole test 23
3.6.5
Citrate test 23
3.7
Statistical Analysis 23
CHAPTER
FOUR: RESULTS 24
CHAPTER
FIVE: DISCUSSION, CONCLUSION AND RECOMMENDATIONS 28
5.1 Discussion 28
5.2 Conclusion 29
5.3 Recommendations 29
References 30
LIST
OF TABLES
Tables Pages
1 Bacteriological counts of water samples from
selected Hospitals 25
2 Physico-chemical analysis of water samples from
selected Hospitals 26
3 Biochemical characteristics of Bacterial Isolates
27
CHAPTER ONE
INTRODUCTION
1.1 Background to
the study
The
Millennium Development Goals include halving the
proportion of people without access
to safe drinking water by 2015. The assessment of the health risk from naturally
occurring
microbes in drinking water continues to be of a high interest to microbiologists, public health practitioners and water supply
regulators (Richards et al., 1992; Hunter 1993). Although a
number of studies have investigated water supply and quality
in sub-Saharan Africa (Shier et
al., 1966), very
limited information is available from the more sparsely populated arid and semi-arid
regions. Livestock movement and migratory
wildlife in search of water can contaminate water by
carrying pathogens from one
source to another. High water
evaporation rates increase the
concentration of
dissolved ions in the water, which
favour
high microbial growth. Ground
water is invariably
cleaner than surface water sources in rural areas. However, the latter may need
treatment
to reduce the
load of suspended solids and to kill microorganisms
Removal of suspended solids presents the
greatest treatment challenge, and there
is a need to develop and choose technologies that will be sustainable in the medium to long
term.
In general,
complex solutions should be avoided.
Most drinking waters, even with residual disinfectants,
have a natural bacterial population. This is because they use naturally available
carbon and nitrogen sources in water to multiply (Manaia et al., 1990; Reasoner, 1990).
Addition of phosphates to water bodies influences growth of bacteria even at concentrations of less than 20 µg L-1 (Sathasivan et al., 1997; Lehtola et al.,
2002). Animal and human
wastes are major sources of nitrogen, phosphates and pathogenic bacteria contamination of aquatic environments. These nutrients can promote growth of pathogenic bacteria implicated
in causing disease in humans,
wildlife and domestic animals. The type
of treatment
technology or combination of technologies to be used depends on the quality of water to be treated. Hence, there is need for monitoring the quality of water bodies and to explore the efficacy of various
treatment
options such as
coagulants from
plant extracts
to
reduce
bacterial load and dissolved solutes.
1.2 Problem statement
and Justification
Information on the bacteriological quality
of water from various sources used for domestic
purposes and for livestock watering in Umuahia is limited. Livestock faecal wastes may
contain pathogenic microorganisms such as Salmonella and Escherichia coli. When livestock drink water contaminated with enteric bacteria, they
may
be exposed to potential
pathogens like Salmonella, which cause salmonellosis in cattle and enteric fever (Typhoid) in
humans.
Such waterborne diseases have been shown
to be capable of infecting large numbers of
animals over
a short time.
The water treatment potential of natural coagulants to purify water has not
been explored. Use of chemical treatments like chlorine as a disinfectant of polluted drinking water is only practiced to a small extent in Umuahia. Apart from the high cost of commercial disinfectants,
their use has been reported to lead to the formation of trihalomethane products (Milot et al., 2000), which are
potentially carcinogenic (King
et al., 1996). There
is, therefore, a need to develop water purification methods
that are cost effective, locally
available and environmentally
friendly. Determination of the physico-chemical properties of water such as
turbidity, pH, salinity, temperature, dissolved
oxygen, nitrogen and phosphorus will provide useful information on overall water quality and its
potential to support bacterial growth
(APHA, 2005).
The study
examines the relations between the physico-chemical properties and the bacterial properties of ground water sources.
1.3 Aims and Objectives
1.3.1 Specific
objectives
i. To determine the level of bacterial contamination of water from common water sources in selected
hospitals/clinics in Umuahia.
ii. To
compare bacterial
load, type with
type
of water source.
iii. To compare bacterial
load, type and physico-chemical
properties of water.
1.4 Significance
of the study
This study evaluated the level of health risk that is
associated with direct use of water from the various water
sources. The
documented information
will be important in the formulation of guidelines on water resource use
in the division. Information
on the bacterial load in water from different sources will be used by
local public
health officers to determine the sources of contamination and to educate the
local community
on how to protect the water sources from contamination.
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