PHYSICO-CHEMICAL AND BACTERIOLOGICAL ASSESSMENT OF RIVER MUDZIRA WATER IN MUBI, ADAMAWA STATE.

International Journal of Technical Research and Applications e-ISSN: 2320-8163,
www.ijtra.com Volume 3, Issue 4 (July-August 2015), PP. 01-04
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PHYSICO-CHEMICAL AND BACTERIOLOGICAL
ASSESSMENT OF RIVER MUDZIRA WATER IN
MUBI, ADAMAWA STATE.
Alexander, P.1 Maitera, O.N2 and Anyawu, J.1
1
Department of Chemistry, Adamawa State University, Mubi, Nigeria
2
Department of Chemistry, Moddibo Adama University of Tectnology, Yola Adamawa State, Nigeria.
priscillaalexander21@yahoo.com
ABSTRACT- Many people in Africa depend on water from
rivers and borehole, but purity of the drinking water from these
sources remains questionable. Mudzira River being the longest
River in a village called Vimtim located in Mubi North Local
government area in Adamawa State was studied in the months of
September to December, 2012 to ascertain the suitability of the
water for human consumption and other related uses. Five study
point: inlet (A, B), middle (C) and out let (D, E) were adopted for
monitoring the physico-chemical parameters using standard
procedures. The mean total temperature values were A (25.000
C),
B (24.500
C), C (25.500
C), D (24.000
C) and E (24.000
C. Average PH
values were A (8.00), B (7.87), C (8.20) D (8.37) and E (8.13). The
average conductivity values were A (73.90
1
cms ), B
(73.11
1
cms ), D (74.00
1
cms ) and E (73. 80
1
cms ). The
average total dissolves solid value of each sample were A (17.10),
B (17.10), C (20.00) D (21.64) and E (21.60.). The average
turbidity value of sample were A (47.00), B (47.00), C (50.00) D
(53.00) and E (50.00). Average total hardness value are A
(20.00mg/l), B (20.00mg/L) C (24.00mg/L), D (20.00mg/L) and E
(20.00mg/L). The average chloride content were A (12mg/L), B
(16mg/L), C (12 mg/L) D (16mg/L) and E (16mg/L). The average
calcium content were A (0.3mg/L) B (0.4mg/L), C (0.3mg/L), D
(0.3mg/L) and E (0.2mg/L). The average content of magnesium
were A (12mg/L), B (16mg/L), C (16Mg/L), D (12mg/L), E
(12mg/L). The lead content of River Mudzira water was
negligible. The mean coliform count were A (4), B (3), C (6), D
(7), and E (4).The values of the parameters studied were within
the WHO/NAFDAC recommended standards, excepts for total
coliform levels. In conclusion Vimtim residents consuming
untreated water from River Mudzira are potentially exposed to
possible acute, sub chronic or even chronic water borne diseases
like typhoid fever, dysentery, diarrhea etc.
Key words: River Mudzira, Physico-chemical parameters,
coliform.
I. INTRODUCTION
One of the major environmental issues of our time is the
rising demand of water quality conditions suitable for use by
human as well as aquatic organisms. Rivers, lakes and dams
are valuable ecological resource that serves many human
needs and therefore enhances life by providing a lot of
opportunities, (Calamari, 1994).
A large number of Nigeria populations live near small
water bodies such as lakes reservoir, swamps and coastal
lagoons. They depend on such water bodies as their main
sources of family income. Usually, such small systems are
subjected to several internet environmental factors as well as
more large system. It is a well known fact that water quality
conditions are constantly being threatened by pollution from
large quantities of waste influences by urbanization,
industrialization and Agriculture. The increasing level of using
chemical herbicides, pesticides and improper domestic and
salvage disposal has created a using awareness of national
management of aquatic resources and control of waste
discharged from the environment (Egborge, 1991).
Water quality conditions according to Boyd and
Lichokoper (1990) include all the physical, chemical and
biological factors that influence the beneficial use of that
water.
II. STUDY AREA
Mubi region refers to the Northern part of Sardauna
province which now forms Adamawa Northern Senatorial
district as defined by INEC (1996). The region lies between
latitude 90
and 110
North of the equator and longitude 130
and
130
451
East of the Greenwich Meridian. Mubi region is
bounded in the North by Borno State, in the West by Hong
and Song L.G.A and in the South and East by the Republic of
Cameroon.
Mubi has a land area of 4728.77km and a population of
759645 in 2003 (1991census project figure) (Adebayo, 2004).
Rainfall in Mubi region is controlled by the movement of
the inter-tropical discontinuity (I.T.P). It divides the zone
between cool and dust air mass and the warm and wet air
mass. The movement of ITP determines the onset and
cessation at a particular time of the year.
Between November and March, the whole Mubi region is
under the influence of ITP zone weather. There is hardly any
rainfall received during this period. April is a month of
transition between the dry and wet season in Mubi region.
During this period, there is scanty rainfall in most parts of the
region. Such rains are often accompanied by strong and
devastating wind storms, (Adebayo, 2004).
The month of May to October constitute the wet season in
Mubi region. During this period, the region is under the
influence of ITD zone B weather. Rainfall increases from May
to August which has the highest amount and from September
to October decreases at a sharp rate. This abrupt decrease is
due to south ward movement of the ITD which is twice faster
than its northward passage (Adabayo 2004).
Agriculture is a major employer of Labour in Mubi region
as such is important sector in the region economy. Three
agricultural systems can be identified in Mubi namely terrace
Farming practiced by hill – top settlers, Sedimentary
cultivation and mixed faming, (Yohanna, 2004).

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III. MATERALS AND MATHODS
Five (5) sampling stations were selected along River
Mudzira, Mubi Adamawa state for this study. The stations
include the inlet of the River as station A and B, middle of the
river as station C and D and the outlet of the river as station E.
The study was carried out in the months of September to
December; 2010.The water samples were collected inside a
clean dry, 1 liter transparent glass bottle. Water samples from
each station were collected about a dept of 30cm and were
transported to the laboratory immediately for analysis using
standard procedures for the collection of the water samples
(APHA, 1998). The temperature of the water samples was
determined on spot using digital thermometer at the point of
collection. The pH and conductivity of the water samples were
determined using combine pH and conductivity meter, model
EC500.
The turbidity of the water samples was determined in
laboratory using water analyzer (Lamotte Scl 04).
The total dissolved solids of each water samples collected
were determined using the T.D.S meter (model EC500). The
chloride content of the water samples were determined using
calorimeter. The total hardness of the water samples were
determined by filling the test tube to the 12.9ml line with the
samples water and 5 drops of hardness reagent was added and
swirl to mix.
The metals such as magnesium and calcium were
analyzed in accordance with the standard method of analysis
of raw water samples (APHA, 2002).
The lead concentration was determined in each of the
water samples using a Bulk scientific Atomic Absorption
Spectrophotometer model 210 at appropriate wave length.
IV. ENUMERATION OF COLIFORM
Total Coliform counts in the samples were determined
using the multiple tube fermentation technique (APHA, 2002).
This involved inoculating multiple fermentation tubes
containing Mac Conkey broth with 1 ML of water sample at
370
C for 24 hour, after which the count was done with a
suwtex 560 colony counter. Detection of E. Coli in the water
was carried using the presumptive and confirmative tests
(APHA, 1998).
V. RESULTS AND DISCUSSION
The results of physico chemical parameters of the river
Mudzira water was as presented in figure 1:
The mean temperature of the river was 24.6  0.5. The
highest and the lowest mean temperature were 25:50
C and
240
C. They all fall within the range given by W.H.O (2006)
which is 250
C.
The mean PH
Value of River Mudzira water was 8  0.17.
The highest and the lowest mean pH values ranges from 7.87
in sample C to 8.37 in sample D. This range is in line with the
standard given by NAFDAC 2004. The variation in pH is very
small, 0.036 and this may be due to the concentration of
different salts present at each point. The range of pH is in line
with that reported by of Ugwu and Mgbenka (2006). pH is
generally considered to have no direct impact on humans.
However, long -term intake of acidic water can invariably lead
to mineral deficiencies (Adekola, et al., 2015).
The conductivity values of River Mudzira showed some
little variation, it ranges from 68.00  ms-1
in sample D. The
reason for this variation can be attributed to the amount of
waste and agricultural chemicals, discharge into the stream at
different times.
The maximum total dissolved solid content recorded was
21.64mg/L in sample D while the minimum was 17.1mg/L in
sample A and B. These values are relatively small compared
to the maximum given by W.H.O (2006) which is 500mg/L.
This shows that the amount of dissolved suspended solid
particles is very low.
The mean turbidity values was 49.4  2.24. It ranges from
47mg/L in sample A and B to 53mg/L in sample D. This range
does not exceed the turbidity value given by W.H.O (2004).
The turbidity of River Mudzira may be due to the presence of
undissolved and suspended solids, mud, silt, algae and micro-
organism.
The total hardness ranges from 20mg/L to 24 mg/L. This
may be due to the presence of magnesium and calcium salts
which dissolved as the river flows. This value though small, is
not good for industrial purposes especially in dyeing, washing,
and in water boiler but could be good for drinking to develop
strong teeth, bones and perhaps for its taste.
The chloride content ranges from 12ppm in sample A and
C to 16ppm in sample B, D, and E. Chloride is a measure of
protection against any contamination which may occur. This
value if compared to the value given by W.H.O (2006) and
NAFDAC (2004) which is 200mg/L is within the permissible
limits, which also agrees with those obtained by Maitera, et.al
(2011) for Rivers Gongola.
The Calcium content of River Mudzira water is very
small. It ranges from 0.2mg/L to 0.4mg/L. This is still within
the standard given by NAFDAC 2004.
The magnesium content of the River Mudzira water
ranges from 12ppm in sample A, D and E to 16ppm in sample
B and C. This may be due to the presence of magnesium salt
present in the River. This value is also within the allowable
value given my NAFDAC and W.H.O.
From the Atomic Absorption Spectrophotometric
analysis, the absorbance of lead ion ranges from 0.004 to
0.005mg/L. Its concentrations could not be computed from the
calibration curve. Therefore, the concentration of lead
compound is negligible.
Copper, cadmium and manganese are not detected in
water sample which differ from those obtained for Rivers
Benue by Maitera, et.al (2011).
The result of the microbial examination of the River
Mudzira water was shown in Fig II. The result shows that
River Mudzira water contains numerous coliform bacteria
which range from 3 to 7 per sample. Data as obtained was
disturbing since the presence of any type of coliform bacteria
in drinking water is not accepted by WHO water quality
standards. This observation supports reports by Anaele (2004),
Erah, et al (2002) and Egwari and Aboaba (2002), that most
underground and surface water sources in urban centers of
Nigeria contain substantial microbial contaminants including
very harmful ones like E.coli, S. typhii among others. This

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contamination may be due to the attitude of the people living
around the River. They defecate in bush around the River
which were washed into the river whenever rain fall. Also
animal dumping around the river as they gaze and drink water
from the river increases the microbial load of the river.
Fig I: Histogram Distribution of Samples
Table II: Total coliform count of each sample of the River Mudzira water
Water Samples Coliform Count
Sample A 4
Sample B 3
Sample C 6
Sample D 7
Sample E 4
Fig II: Coliform Distribution of Water Samples

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VI. CONCLUSION
Data obtained in this study agree with several other
surveys earlier carried out in other surface and underground
waters. It can therefore be concluded from the study that Mubi
(Vimtim) residents consuming untreated water from River
Mudzira are potentially exposed to possible acute, sub chronic
or even chronic water borne diseases like typhoid fever,
dysentery, diarrhea etc.
VII. RECOMMENDATION
It is recommended here that chlorinating agents be
provided by the government at heavily subsidized prices for
all and Sundry to assist in the elimination of pathogenic
microorganism in the River Mudzira water supplies. River
Mudzira is also recommended for irrigation and other
domestic work and not for human consumption. Activities
around the river Mudzira such as washing of cloth, bathing
and swimming in the river and grazing around the river should
be restricted by educating the community on the health effect
of polluted water.
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PHYSICO-CHEMICAL AND BACTERIOLOGICAL ASSESSMENT OF RIVER MUDZIRA WATER IN MUBI, ADAMAWA STATE.

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PHYSICO-CHEMICAL AND BACTERIOLOGICAL ASSESSMENT OF RIVER MUDZIRA WATER IN MUBI, ADAMAWA STATE.