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Arid Zone Journal of Engineering, Technology and Environment, April, 2017; Vol. 13(3):420-427
Copyright © Faculty of Engineering, University of Maiduguri, Maiduguri, Nigeria.
Print ISSN: 1596-2490, Electronic ISSN: 2545-5818, www.azojete.com.ng
420
Turbidity and Colour Reduction of Pond Water Using Extracts of Diospyros mespiliformis,
Mitragyna inermis, Piliostigma reticulatum and Tamarindus indica in Northern Nigeria
S. G. Yadima*, M. Muhammad and B. Usman
(Department of Civil and Water Resources Engineering, University of Maiduguri, P.M.B.1069,
Borno State, Nigeria)
*Corresponding author’s E-mail: sunday.yadima@gmail.com
Abstract
The study examined the coagulation performance of leaves and root bark extracts of Diospyros mespiliformis,
Mitragyna inermis, Piliostigma reticulatum and Tamarindus indica. The plant materials were collected along River
Kubwa in Damboa local Government area of Borno State, Nigeria. The crude extracts of these plant materials were
prepared based on soxhlet method using soxhlet solvent extractor. About 400mg of each pulverized sample was used
for the extraction process. Three (3) liters of distilled water was used for the extraction process. The extracts were
each added to highly turbid (422 NTU) pond water samples at various dosages of 60, 75, 90, 105, 120, and 135mg/l
and a conventional coagulation-flocculation jar tests were conducted. The nature of the flocs formation for all the
plant extracts were observed to be smoky rather than aggregating into denser masses and resulted in turbidity and
colour removal efficiencies of 0.71-18.57% and 1.17-22.38% respectively. The coagulation activities were subjected
to T-Test Analysis and it indicated that there was statistically (P< 0.05) significance difference at different
concentrations. The results also revealed slight decrease in pH in the range of 8.1-7.55 exhibited by all the extracts.
From the results of the turbidity and colour removal efficiencies, it can be concluded that these plant materials have
the potential of improving the quality of pond or surface water (which most rural communities in developing
countries depend for many purposes) that are heavily turbid; However, for them to perform effectively, a coagulant
aid is required.
Keywords: Extracts, Coagulation, Flocculation, Leaves, Root bark, Materials, Turbidity
1. Introduction
Access to safe drinking water is as important as a health and development issues at National,
Regional and Local government levels. In some regions of the world, it has been shown that
investment in water supply and sanitation can yield a net economic benefit, since the reduction in
adverse health effect and health care costs over weight the cost of undertaking the intervention
(Saritha et al., 2012).
Globally, the Middle East and parts of Africa are the continents with the most limited water
resources and critical resource issues, which is a greatly limiting input to food security, economic
and social development. In regions of Africa, Asia and Latin America; people living in extreme
poverty in rural and sub- urban communities are often forced to rely on polluted surface water
sources for their domestic uses and this poses a great risk to human health (Marobhe and
Gunaratna, 2012).
It is true that water related infections are responsible for more than 80% of diseases in all over
the world (Reuka and Jadhav, 2012). In an attempt to treat these infections, lack of adequate
finances to purchase the necessary antibiotics has led to abuse and poor compliance to treatment,
thus the increasing prevalence of antibiotic helicobacter pylori infections and many others have
rather compounded the pathogenicity and epidemiological pattern in the water. Given the time
and cost of developing or rehabilitating the improved communal water supply sources, it can be
cheaper in certain circumstances to rely on the existing traditional sources (Clasen and Bastable,
Arid Zone Journal of Engineering, Technology and Environment, April, 2017; Vol. 13(3):420-427
ISSN 1596-2490; e-ISSN 2545-5818; www.azojete.com.ng
421
2003). This is possible if traditional water sources can be treated using water purification
methods, which are inexpensive and suitable under local conditions. One area that holds a lot of
prospect for the future is the plant kingdom and particularly the use of these plant seeds, leaves,
root barks, stem barks and fruits as natural coagulants to remove turbidity and bacteria in surface
water (Ebobganya et al., 2013, Ghebremichael et al., 2005). It has also been observed by many
researchers that reduction in turbidity is associated with significant improvements in
bacteriological quality (Ghebremichael et al., 2006; Marobhe, 2008b; Conte et al., 2007; Phani
and Rajkumar, 2013).
The present study examined the performance of natural plant materials that are locally available
in North East Nigeria as renewable sources of natural coagulants using their leaves and root
barks aqueous extracts in pond water treatment.
2. Materials and Methods
2.1 Collection of Plant Materials
The fresh root barks and matured leaves of Diospyros mespiliformis, Mitragyna inermis,
Piliostigma reticulatum and Tamarindus indica were collected from bush along Kubwa riverside
in Damboa local Government area of Borno State, Nigeria in the month of April, 2013, when the
leaves of these trees were green. The root barks and matured leaves of these plants were
removed, chopped into pieces using mortar and pestle and shade dried at room temperature. Each
dried sample was subjected to a size reduction using mechanical grinding machine.
2.2 Preparation of Plant Extracts
The extraction process was conducted based on soxhlet method using soxhlet solvent extractor.
About 400mg of each pulverized sample was used for the extraction process. Three liters of
distilled water was added to cover the sample into solution. The heating mantle on the extractor
was switched on and allowed to reflux the mixture for 2hrs. The solution was removed and
filtered to remove debris. The aqueous extracts were evaporated to dryness on rotary evaporator.
2.3 Source of Raw Water
The raw water having turbidity strength of 422 NTU was collected from a pond along Molai
Road, Maiduguri, Nigeria. Maiduguri the capital of Borno State lies within the latitude 11°
51’ N
and 13°
40’ N and longitude 10°
0’ E and 13°
E. The water sample was collected towards the
middle of the pond to serve as representative sample of the whole pond water and a laboratory
test was carried out each day the sample was collected.
2.4 Coagulation Tests
The coagulation activities of the aqueous crude root bark and leave extracts of the plant materials
on highly turbid water (422 NTU) were evaluated using an experimental jar tester of Phipps and
Birds fitted with six (1000ml) beakers. The coagulation tests (jar test experiments) were carried
out at varying dosages of the aqueous crude extracts using standard procedure described by
Gurchran and Jagdish (2009).
2.5 Statistical Analysis
Yadima et al.: Turbidity and colour reduction of pond water using extracts of diospyros mespiliformis,
mitragyna inermis, piliostigma reticulatum and tamarindus indica in northern Nigeria. AZOJETE,
13(3):420-427. ISSN 1596-2490; e-ISSN 2545-5818, www.azojete.com.ng
422
T-Test analysis was used to compare the significant differences of turbidity and colour removals
of the aqueous leaves and root bark extracts of the plant materials on the raw water
3. Results and Discussions
The Percentage of turbidity and colour removal using aqueous root bark extracts of the plants are
shown in table 1.
Table 1: Percentage of turbidity and colour removal using aqueous root bark extracts
Number of
Jars
Concentrations of
extracts (mg/l)
Settling
time (min)
Plant
extracts
Percent turbidity
removal (%)
Percent colour
removal (%)
J1 60 20
DR 9.00 8.71
MR 8.53 8.25
PR 0.95 1.24
MR 10.24 12.35
J2 75 23
DR 9.48 9.17
MR 8.77 8.48
PR 1.9 2.25
MR 12.38 14.92
J3 90 24
DR 9.95 9.62
MR 10.09 9.77
PR 2.38 3.19
MR 11.9 14.64
J4 105 26
DR 9.72 9.4
MR 9.86 9.54
PR 7.62 8.03
MR 14.76 17.79
J5 120 28
DR 8.53 8.25
MR 7.82 7.57
PR 2.62 3.99
MR 10.71 12.92
J6 135 30
DR 14.22 13.76
MR 10.31 9.97
PR 2.14 2.59
MR 11.67 14.34
Key: DR = Diospyros mespiliformis root bark MR = Mitragyna inermis root bark PR = Piliostigma reticulatum root bark TR=Tamarindus indica
root bark
The percentage of turbidity and colour removal using root bark extracts of the plant materials are
presented in Table 1. From the Table, it can be seen that the highest turbidity removal of
Diosppyros mespiliformis extract was 14.22% at the dosage of 135mg/l, for Mitragyna inermis, it
was 10.31% at a dose concentration of 135mg/l, for Piliostigma reticulatum, it was 7.62% at a
dosage of 105mg/l and for Tamarindus indica, it was 14.76% at a dose concentration of 105mg/l.
Diosppyros mespiliformis had colour removal efficiency in the range of 8.25% to 13.76% and the
highest removal was achieved at dose concentration of 135mg/l. For mitragyna inermis extract,
is from 7.54% to 9.97% and had the highest colour removal ability at the dose concentration of
135mg/l. The percentage of colour removal for Piliostigma reticulatum and Tamarindus indica
Arid Zone Journal of Engineering, Technology and Environment, April, 2017; Vol. 13(3):420-427
ISSN 1596-2490; e-ISSN 2545-5818; www.azojete.com.ng
423
ranged from 1.24% to 8.03% and 12.35% to 17.79% respectively and the highest efficiencies
were achieved at dose concentration of 105mg/l for the extracts.
The Percentage of turbidity and colour removal using aqueous leaves bark extracts of the plants
are shown in table 2.
Table 2: Percentage of turbidity and colour removal using aqueous leaves extracts
Number
of Jars
Concentrations of
extracts (mg/l)
Settling time
(min)
Plant extracts Percent turbidity
removal (%)
Percent colour
removal (%)
J1 60 20
DL 9.00 8.71
ML 8.77 8.64
PL 0.71 1.17
TL 14.05 16.94
J2 75 23
DL 10.19 9.86
ML 9.24 8.94
PL 3.1 5.1
TL 15.48 18.66
J3 90 24
DL 9.9 9.58
ML 8.59 8.58
PL 5.24 6.22
TL 15 18.09
J4 105 26
DL 9.72 9.4
ML 10.19 9.86
PL 2.62 4.31
TL 14.29 17.21
J5 120 28
DL 9.48 9.17
ML 8.91 8.62
PL 2.38 3.92
TL 17.14 20.66
J6 135 30
DL 11.02 10.66
ML 8.53 8.23
PL 3.81 6.27
TL 18.57 22.38
Key: DL=Diospyros mespiliformis leave ML=Mitragyna inermis leave PL=Piliostigma reticulatum leave
TL=Tamarindus indica leave
The percentage of turbidity and colour removal using leave extracts of the plant materials are
presented in Table 2. The percentage of turbidity removal efficiency by Diosppyros
mespiliformis leaves extract varied from 9.00% to 11.02%, for mitragyna inermis, it varied from
8.53% to 10.19%, for Piliostigma reticulatum, it varied from 0.71% to 5.14% and for
Tamarindus indica, it varied from 14.05% to 18.57%. The highest percentage turbidity removal
for Diosppyros mespiliformis, Mitragyna inermis, Piliostigma reticulatum and Tamarindus
indica were achieved at dose concentrations of 135mg/l, 105mg/l, 90mg/l and 135mg/l
respectively.
The percentage of colour removal using the leave extracts (table 2) indicated that for Diosppyros
mespiliformis, it varied from 6.71% to 10.66%, for Mitragyna inermis, it was from 8.23% to
9.86% with the lowest percentage removal of 8.23% at the dosage of 135mg/l. Piliostigma
Yadima et al.: Turbidity and colour reduction of pond water using extracts of diospyros mespiliformis,
mitragyna inermis, piliostigma reticulatum and tamarindus indica in northern Nigeria. AZOJETE,
13(3):420-427. ISSN 1596-2490; e-ISSN 2545-5818, www.azojete.com.ng
424
reticulatum extract had percentage of colour removal which varied from 1.17% to 6.27% and
Tamarindus indica extract had percentage removal of colour which varied from 16.94% to
22.38%.
TheT-Test analysis for the coagulation property (turbidity removal) of the aqueous root bark and
leaves extracts of the plants are shown in table 3
Table 3: T-Test analysis for the coagulation property (turbidity removal) of the aqueous root
bark and leaves extracts
Diospyros mespiliformis root extract Diospyros mespiliformis leave extract
N Mean StDev T Df P-value Decision N Mean StDev T Df P-value Decision
IT 6 422.00 0.00 12.09 5 0.000 Reject Ho IT 6 422.00 0.00 35.30 5 0.000 Reject. Ho
FT 6 397.17 8.68 FT 6 380.29 2.89
Mitragyna inermis root bark extract Mitragyna inermis leave extract
N Mean StDev T Df P-value Decision N Mean StDevT T Df P-value Decision
IT
FT
6
6
422.00
383.05
0.00
4.22
22.62 5 0.000 Reject Ho IT
FT
6
6
422.00
383.07
0.00
2.62
35.72 5 0.000 Reject Ho
Piliostigma reticulatum root bark extract Piliostigma reticulatum leave extract
N Mean StDev T Df P-value Decision N Mean StDev T Df P-value Decision
IT 6 420.00 0.00 3.04 5 0.029 Reject Ho IT 6 422.00 0.00 4.82 5 0.005 Reject Ho
FT 6 407.67 9.93 FT 6 407.50 6.35
Tamarindus indica root bark extract Tamarindus indica leave extract
N Mean StDev T Df P-value Decision N Mean StDev T Df P-value Decision
IT 6 420.00 0.00 18.41 5 0.000 Reject Ho IT 6 420.00 0.00 21.86 5 0.000 Reject Ho
FT 6 369.83 6.68 FT 6 353.83 7.41
Ho = There is no difference in turbidity removal of the extracts in the raw water
The Table indicated that the pre-determined significance values of all the extracts were less than
0.05.
The coagulation activities of the plant extracts were found to vary slightly at various dosages.
The highest percentage of turbidity and colour removal of 18.57 and 22.38 was demonstrated by
Tamarindus indica leaves extract while the lowest percentage removal of turbidity and colour of
0.71 and 1.17 respectively was demonstrated by Piliostigma reticulatum leaves extract.
Generally, it was observed that the coagulating effect of these plant materials were not
substantial. The patterns of floc-formation for all the plant extracts were observed to be of
smoky-like than aggregating into sizes that may have enough density to settle down in a short
period of time. This might be attributed to some factors such as the initial pH of the raw water
which stood at a value of 8.1.
The results of T-Test analysis for the coagulation property (colour removal) of the aqueous root
bark and leaves extracts of the plants are shown in table 4.
Arid Zone Journal of Engineering, Technology and Environment, April, 2017; Vol. 13(3):420-427
ISSN 1596-2490; e-ISSN 2545-5818; www.azojete.com.ng
425
Table 4: T-Test analysis for the coagulation property (colour removal) of the aqueous root bark
and leaves extracts
Diospyros mespiliformis root bark extract Diospyros mespiliformis leave extract
N Mean StDev T Df P-value Decision N Mean StDev T Df P-value Decision
IC 6 4361.00 0,0 12.09 5 0.000 Reject Ho IC 6 4361.00 0.0 35.34 5 0.000 Reject Ho
FC 6 3932.7 86.8 FC 6 3943.8 289
Mitragyna inermis root bark extract MItragyna inermis leave extract
N Mean StDev T Df P-value Decision N Mean StDev T Df P-value Decision
IC 6 4361.00 0.0 22.62 5 0.000 Reject Ho IC 6 4361.00 0.0 37.32 5 0.000 Reject Ho
FC 6 3971.5 42.2 FC 6 3978.0 25.1
Piliostigma reticulatum root bark extract Piliostigma reticulatum leave extract
N Mean StDev T Df P-value Decision N Mean StDev T Df P-value Decision
IC 6 4357.00 0.0 3.66 5 0.015 Reject Ho IC 6 4357.00 0.0 5.83 5 0.002 Reject Ho
FC 6 4202.2 103.6 FC 6 4161.0 82.4
Tamarindus indica root bark extract Tamarindus indica leave extract
N Mean StDev T Df P-value Decision N Mean StDev T Df P-value Decision
IC 6 4357.00 0.0 18.63 5 0.000 Reject Ho IC 6 4357.00 0.0 21.90 5 0.000 Reject Ho
FC 6 3725.5 83.0 FC 6 3529.7 92.5
Ho = There is no difference in colour removal of the extracts in the raw water
The Table indicated that the pre-determined significance values of all the extracts were less than
0.05.
It was often reported that the performance of natural coagulants improves at acidic pH of raw
water samples (Bodlund, 2013). Similarly, Marobhe, (2008b) observed that the net surface
charge of colloidal particles is reduced at low pH and hense the electrostatic repulsion between
the colloids and the thickness of the double layer is also reduced. This suggests that efficient
particles destabilization and optimal flocculation occur at lower pH. The floc-formation patterns
of these extracts could also be explained by the degree of their solubility or polarity in the water
(solvent). The best performance of a crude extract from a finely grinded seed powder could be
due to its large total surface area; whereby most of the water soluble proteins are at the solid-
liquid interface during the extraction process and this might increase the concentration of active
coagulation polymer in the extracts which improves the coagulation process (Hart, 2000).
Therefore, these extracts require substantial settling time before a significant turbidity and colour
removal can be achieved, hence they could be used with coagulant aid such as Non-ionic
polymer which may raise the pH as well as increase the alkalinity. The T-Test results of turbidity
and colour removal abilities of the plant extracts indicated that the pre-determined significance
values of all the extracts were less than 0.05. This signified that there were differences in the
removal of turbidity and colour at the varying dosages of the extracts.
Yadima et al.: Turbidity and colour reduction of pond water using extracts of diospyros mespiliformis,
mitragyna inermis, piliostigma reticulatum and tamarindus indica in northern Nigeria. AZOJETE,
13(3):420-427. ISSN 1596-2490; e-ISSN 2545-5818, www.azojete.com.ng
426
4. Conclusion
The highest percentage of performance for turbidity removal was 18.57% and for colour removal
was 22.38% and was established by Tamarindus indica leaves extract which was rather low. The
implication was that these plant materials could be used with the help of an aid (coagulation aid)
to improve their performances.
This investigation has opened up the possibility of using these plant materials as natural
coagulants in improving the quality of pond or surface water (on which most rural communities
in developing countries depend for drinking and other purposes) that are highly turbid.
Therefore, it is recommended that the use of these plant materials should be encouraged among
rural communities to improve the quality of pond or surface water. Toxicity test should be
carried out on these plant extracts so that safe application concentrations can then be determined,
and further diversification of these plant extracts towards treating some common chemicals
including heavy metals and pathogenic organisms and other related contaminants in pond or
surface water is also recommended.
References
Bodlund, I. 2013. Coagulant Protein from Plant Materials: Potential Water Treatment Agent. School of
Biotechnology, Royal Institute of Technology (KTH), Alba Nova University Center, Stockholm, Sweden.
Conte, M., Albert, F., Fucci, L. and Piscopo, M. 2007. Antibacterial Activity of Various Cationic
Molecules on Foodborne Pathogens. World Journal of Microbiology and Biotechnology, 23: 1679-1683.
Clasen, TF. and Bastable, A. 2003. Faecal Contamination of Drinking Water during Collection
and Household Storage. The need to Extend Protection to the Point of Use. Journal of Water and
Health, 1(3): 109-115.
Ebobganya, PRO., Ocholi, OJ. and Apejt, Y. 2013. A Review on the Use of Plants’ Seeds as
Biocoagulants in the Purification of Water. Continental Journal of Biological Sciences, 6(2): 26-32.
Ghabremichael, KA., Gunaratna,, KR., Hongbin, H., Brumer, H. and Dalhammer, G. 2005. A simple
Purification and Activity Assay of the Coagulant Protein from Moringa oleifera Seed. Water Research,
39(1): 2338-2344.
Ghabremichael, KA, Gunaratna, KR. and Dalhammar, G. 2006. Single-Step Ion Exchange Purification of
the Coagulant Protein from Moringa oleifera Seed. Applied Microbiology and Biotechnology, 70: 526-
532.
Gurcharan, S. and Jagdish, S. 2009. Water Supply and Sanitary Engineering, 6th
reprint edition, Nem
Chand Jain, Nai Sarak, Delhi India.
Hart, TL. 2000. Natural coagulants: An Investigation of Moringa oleifera and Tamarind Seeds. MSc
Thesis. The University of Texas, Austin, USA.
Arid Zone Journal of Engineering, Technology and Environment, April, 2017; Vol. 13(3):420-427
ISSN 1596-2490; e-ISSN 2545-5818; www.azojete.com.ng
427
Marobhe, JN. 2008. Water Supply in Tanzania and Performance of Local Plant Materials in Purification
of Turbid Water. Trita LWR PhD Thesis 1042. Department of Land and Water Resources Engineering,
Royal Institute of Technology (KTH), SE-100 44 Stockholm, Sweden.
Marobhe, NJ. and Gunaratna, RK. 2012. Effect of Coagulant Protein from Parkinsonia aculeate Seed and
Citrus Juice on Bacteria Isolated from Ruvu River in Tanzania. International Journal of Applied
Science and Engineering Research, 1(5): 714-724.
Muhammad, M. 2016. Turbid water Clarification using Natural Plant Materials as Coagulants.
Unpublished M. Eng. Thesis. Department of Civil and Water Resources Engineering, University of
Maiduguri, Nigeria.
Phani Madhavi, T. and Rajkumar, R. 2013. Utilisation of Natural Coagulants for Reduction of Turbidity
from Waste Water. International Journal of Chem. Tech. Research, 5(3): 1119-1123.
Renuka, AB. and Jadhav, MV. 2012. Assessment of Purification of Water by using Natural Herbs.
Lokavishkar International E-Journal, 1(4): 2-22.
Saritha, V. 2012. Screening and Evaluation of Innate Coagulants for Water Treatment: a Sustainable
Approach. Vara International Journal of Energy and Environmental Engineering, 3(29): 1-11.

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Phyto-Chemical Screening and Antibacterial Activities of Aqueous Extracts of Diospyros mespiliformis, Mitragyna inermis, Piliostigma reticulatum and Tamarindus indica in Northern Nigeria

  • 1. Arid Zone Journal of Engineering, Technology and Environment, April, 2017; Vol. 13(3):420-427 Copyright © Faculty of Engineering, University of Maiduguri, Maiduguri, Nigeria. Print ISSN: 1596-2490, Electronic ISSN: 2545-5818, www.azojete.com.ng 420 Turbidity and Colour Reduction of Pond Water Using Extracts of Diospyros mespiliformis, Mitragyna inermis, Piliostigma reticulatum and Tamarindus indica in Northern Nigeria S. G. Yadima*, M. Muhammad and B. Usman (Department of Civil and Water Resources Engineering, University of Maiduguri, P.M.B.1069, Borno State, Nigeria) *Corresponding author’s E-mail: sunday.yadima@gmail.com Abstract The study examined the coagulation performance of leaves and root bark extracts of Diospyros mespiliformis, Mitragyna inermis, Piliostigma reticulatum and Tamarindus indica. The plant materials were collected along River Kubwa in Damboa local Government area of Borno State, Nigeria. The crude extracts of these plant materials were prepared based on soxhlet method using soxhlet solvent extractor. About 400mg of each pulverized sample was used for the extraction process. Three (3) liters of distilled water was used for the extraction process. The extracts were each added to highly turbid (422 NTU) pond water samples at various dosages of 60, 75, 90, 105, 120, and 135mg/l and a conventional coagulation-flocculation jar tests were conducted. The nature of the flocs formation for all the plant extracts were observed to be smoky rather than aggregating into denser masses and resulted in turbidity and colour removal efficiencies of 0.71-18.57% and 1.17-22.38% respectively. The coagulation activities were subjected to T-Test Analysis and it indicated that there was statistically (P< 0.05) significance difference at different concentrations. The results also revealed slight decrease in pH in the range of 8.1-7.55 exhibited by all the extracts. From the results of the turbidity and colour removal efficiencies, it can be concluded that these plant materials have the potential of improving the quality of pond or surface water (which most rural communities in developing countries depend for many purposes) that are heavily turbid; However, for them to perform effectively, a coagulant aid is required. Keywords: Extracts, Coagulation, Flocculation, Leaves, Root bark, Materials, Turbidity 1. Introduction Access to safe drinking water is as important as a health and development issues at National, Regional and Local government levels. In some regions of the world, it has been shown that investment in water supply and sanitation can yield a net economic benefit, since the reduction in adverse health effect and health care costs over weight the cost of undertaking the intervention (Saritha et al., 2012). Globally, the Middle East and parts of Africa are the continents with the most limited water resources and critical resource issues, which is a greatly limiting input to food security, economic and social development. In regions of Africa, Asia and Latin America; people living in extreme poverty in rural and sub- urban communities are often forced to rely on polluted surface water sources for their domestic uses and this poses a great risk to human health (Marobhe and Gunaratna, 2012). It is true that water related infections are responsible for more than 80% of diseases in all over the world (Reuka and Jadhav, 2012). In an attempt to treat these infections, lack of adequate finances to purchase the necessary antibiotics has led to abuse and poor compliance to treatment, thus the increasing prevalence of antibiotic helicobacter pylori infections and many others have rather compounded the pathogenicity and epidemiological pattern in the water. Given the time and cost of developing or rehabilitating the improved communal water supply sources, it can be cheaper in certain circumstances to rely on the existing traditional sources (Clasen and Bastable,
  • 2. Arid Zone Journal of Engineering, Technology and Environment, April, 2017; Vol. 13(3):420-427 ISSN 1596-2490; e-ISSN 2545-5818; www.azojete.com.ng 421 2003). This is possible if traditional water sources can be treated using water purification methods, which are inexpensive and suitable under local conditions. One area that holds a lot of prospect for the future is the plant kingdom and particularly the use of these plant seeds, leaves, root barks, stem barks and fruits as natural coagulants to remove turbidity and bacteria in surface water (Ebobganya et al., 2013, Ghebremichael et al., 2005). It has also been observed by many researchers that reduction in turbidity is associated with significant improvements in bacteriological quality (Ghebremichael et al., 2006; Marobhe, 2008b; Conte et al., 2007; Phani and Rajkumar, 2013). The present study examined the performance of natural plant materials that are locally available in North East Nigeria as renewable sources of natural coagulants using their leaves and root barks aqueous extracts in pond water treatment. 2. Materials and Methods 2.1 Collection of Plant Materials The fresh root barks and matured leaves of Diospyros mespiliformis, Mitragyna inermis, Piliostigma reticulatum and Tamarindus indica were collected from bush along Kubwa riverside in Damboa local Government area of Borno State, Nigeria in the month of April, 2013, when the leaves of these trees were green. The root barks and matured leaves of these plants were removed, chopped into pieces using mortar and pestle and shade dried at room temperature. Each dried sample was subjected to a size reduction using mechanical grinding machine. 2.2 Preparation of Plant Extracts The extraction process was conducted based on soxhlet method using soxhlet solvent extractor. About 400mg of each pulverized sample was used for the extraction process. Three liters of distilled water was added to cover the sample into solution. The heating mantle on the extractor was switched on and allowed to reflux the mixture for 2hrs. The solution was removed and filtered to remove debris. The aqueous extracts were evaporated to dryness on rotary evaporator. 2.3 Source of Raw Water The raw water having turbidity strength of 422 NTU was collected from a pond along Molai Road, Maiduguri, Nigeria. Maiduguri the capital of Borno State lies within the latitude 11° 51’ N and 13° 40’ N and longitude 10° 0’ E and 13° E. The water sample was collected towards the middle of the pond to serve as representative sample of the whole pond water and a laboratory test was carried out each day the sample was collected. 2.4 Coagulation Tests The coagulation activities of the aqueous crude root bark and leave extracts of the plant materials on highly turbid water (422 NTU) were evaluated using an experimental jar tester of Phipps and Birds fitted with six (1000ml) beakers. The coagulation tests (jar test experiments) were carried out at varying dosages of the aqueous crude extracts using standard procedure described by Gurchran and Jagdish (2009). 2.5 Statistical Analysis
  • 3. Yadima et al.: Turbidity and colour reduction of pond water using extracts of diospyros mespiliformis, mitragyna inermis, piliostigma reticulatum and tamarindus indica in northern Nigeria. AZOJETE, 13(3):420-427. ISSN 1596-2490; e-ISSN 2545-5818, www.azojete.com.ng 422 T-Test analysis was used to compare the significant differences of turbidity and colour removals of the aqueous leaves and root bark extracts of the plant materials on the raw water 3. Results and Discussions The Percentage of turbidity and colour removal using aqueous root bark extracts of the plants are shown in table 1. Table 1: Percentage of turbidity and colour removal using aqueous root bark extracts Number of Jars Concentrations of extracts (mg/l) Settling time (min) Plant extracts Percent turbidity removal (%) Percent colour removal (%) J1 60 20 DR 9.00 8.71 MR 8.53 8.25 PR 0.95 1.24 MR 10.24 12.35 J2 75 23 DR 9.48 9.17 MR 8.77 8.48 PR 1.9 2.25 MR 12.38 14.92 J3 90 24 DR 9.95 9.62 MR 10.09 9.77 PR 2.38 3.19 MR 11.9 14.64 J4 105 26 DR 9.72 9.4 MR 9.86 9.54 PR 7.62 8.03 MR 14.76 17.79 J5 120 28 DR 8.53 8.25 MR 7.82 7.57 PR 2.62 3.99 MR 10.71 12.92 J6 135 30 DR 14.22 13.76 MR 10.31 9.97 PR 2.14 2.59 MR 11.67 14.34 Key: DR = Diospyros mespiliformis root bark MR = Mitragyna inermis root bark PR = Piliostigma reticulatum root bark TR=Tamarindus indica root bark The percentage of turbidity and colour removal using root bark extracts of the plant materials are presented in Table 1. From the Table, it can be seen that the highest turbidity removal of Diosppyros mespiliformis extract was 14.22% at the dosage of 135mg/l, for Mitragyna inermis, it was 10.31% at a dose concentration of 135mg/l, for Piliostigma reticulatum, it was 7.62% at a dosage of 105mg/l and for Tamarindus indica, it was 14.76% at a dose concentration of 105mg/l. Diosppyros mespiliformis had colour removal efficiency in the range of 8.25% to 13.76% and the highest removal was achieved at dose concentration of 135mg/l. For mitragyna inermis extract, is from 7.54% to 9.97% and had the highest colour removal ability at the dose concentration of 135mg/l. The percentage of colour removal for Piliostigma reticulatum and Tamarindus indica
  • 4. Arid Zone Journal of Engineering, Technology and Environment, April, 2017; Vol. 13(3):420-427 ISSN 1596-2490; e-ISSN 2545-5818; www.azojete.com.ng 423 ranged from 1.24% to 8.03% and 12.35% to 17.79% respectively and the highest efficiencies were achieved at dose concentration of 105mg/l for the extracts. The Percentage of turbidity and colour removal using aqueous leaves bark extracts of the plants are shown in table 2. Table 2: Percentage of turbidity and colour removal using aqueous leaves extracts Number of Jars Concentrations of extracts (mg/l) Settling time (min) Plant extracts Percent turbidity removal (%) Percent colour removal (%) J1 60 20 DL 9.00 8.71 ML 8.77 8.64 PL 0.71 1.17 TL 14.05 16.94 J2 75 23 DL 10.19 9.86 ML 9.24 8.94 PL 3.1 5.1 TL 15.48 18.66 J3 90 24 DL 9.9 9.58 ML 8.59 8.58 PL 5.24 6.22 TL 15 18.09 J4 105 26 DL 9.72 9.4 ML 10.19 9.86 PL 2.62 4.31 TL 14.29 17.21 J5 120 28 DL 9.48 9.17 ML 8.91 8.62 PL 2.38 3.92 TL 17.14 20.66 J6 135 30 DL 11.02 10.66 ML 8.53 8.23 PL 3.81 6.27 TL 18.57 22.38 Key: DL=Diospyros mespiliformis leave ML=Mitragyna inermis leave PL=Piliostigma reticulatum leave TL=Tamarindus indica leave The percentage of turbidity and colour removal using leave extracts of the plant materials are presented in Table 2. The percentage of turbidity removal efficiency by Diosppyros mespiliformis leaves extract varied from 9.00% to 11.02%, for mitragyna inermis, it varied from 8.53% to 10.19%, for Piliostigma reticulatum, it varied from 0.71% to 5.14% and for Tamarindus indica, it varied from 14.05% to 18.57%. The highest percentage turbidity removal for Diosppyros mespiliformis, Mitragyna inermis, Piliostigma reticulatum and Tamarindus indica were achieved at dose concentrations of 135mg/l, 105mg/l, 90mg/l and 135mg/l respectively. The percentage of colour removal using the leave extracts (table 2) indicated that for Diosppyros mespiliformis, it varied from 6.71% to 10.66%, for Mitragyna inermis, it was from 8.23% to 9.86% with the lowest percentage removal of 8.23% at the dosage of 135mg/l. Piliostigma
  • 5. Yadima et al.: Turbidity and colour reduction of pond water using extracts of diospyros mespiliformis, mitragyna inermis, piliostigma reticulatum and tamarindus indica in northern Nigeria. AZOJETE, 13(3):420-427. ISSN 1596-2490; e-ISSN 2545-5818, www.azojete.com.ng 424 reticulatum extract had percentage of colour removal which varied from 1.17% to 6.27% and Tamarindus indica extract had percentage removal of colour which varied from 16.94% to 22.38%. TheT-Test analysis for the coagulation property (turbidity removal) of the aqueous root bark and leaves extracts of the plants are shown in table 3 Table 3: T-Test analysis for the coagulation property (turbidity removal) of the aqueous root bark and leaves extracts Diospyros mespiliformis root extract Diospyros mespiliformis leave extract N Mean StDev T Df P-value Decision N Mean StDev T Df P-value Decision IT 6 422.00 0.00 12.09 5 0.000 Reject Ho IT 6 422.00 0.00 35.30 5 0.000 Reject. Ho FT 6 397.17 8.68 FT 6 380.29 2.89 Mitragyna inermis root bark extract Mitragyna inermis leave extract N Mean StDev T Df P-value Decision N Mean StDevT T Df P-value Decision IT FT 6 6 422.00 383.05 0.00 4.22 22.62 5 0.000 Reject Ho IT FT 6 6 422.00 383.07 0.00 2.62 35.72 5 0.000 Reject Ho Piliostigma reticulatum root bark extract Piliostigma reticulatum leave extract N Mean StDev T Df P-value Decision N Mean StDev T Df P-value Decision IT 6 420.00 0.00 3.04 5 0.029 Reject Ho IT 6 422.00 0.00 4.82 5 0.005 Reject Ho FT 6 407.67 9.93 FT 6 407.50 6.35 Tamarindus indica root bark extract Tamarindus indica leave extract N Mean StDev T Df P-value Decision N Mean StDev T Df P-value Decision IT 6 420.00 0.00 18.41 5 0.000 Reject Ho IT 6 420.00 0.00 21.86 5 0.000 Reject Ho FT 6 369.83 6.68 FT 6 353.83 7.41 Ho = There is no difference in turbidity removal of the extracts in the raw water The Table indicated that the pre-determined significance values of all the extracts were less than 0.05. The coagulation activities of the plant extracts were found to vary slightly at various dosages. The highest percentage of turbidity and colour removal of 18.57 and 22.38 was demonstrated by Tamarindus indica leaves extract while the lowest percentage removal of turbidity and colour of 0.71 and 1.17 respectively was demonstrated by Piliostigma reticulatum leaves extract. Generally, it was observed that the coagulating effect of these plant materials were not substantial. The patterns of floc-formation for all the plant extracts were observed to be of smoky-like than aggregating into sizes that may have enough density to settle down in a short period of time. This might be attributed to some factors such as the initial pH of the raw water which stood at a value of 8.1. The results of T-Test analysis for the coagulation property (colour removal) of the aqueous root bark and leaves extracts of the plants are shown in table 4.
  • 6. Arid Zone Journal of Engineering, Technology and Environment, April, 2017; Vol. 13(3):420-427 ISSN 1596-2490; e-ISSN 2545-5818; www.azojete.com.ng 425 Table 4: T-Test analysis for the coagulation property (colour removal) of the aqueous root bark and leaves extracts Diospyros mespiliformis root bark extract Diospyros mespiliformis leave extract N Mean StDev T Df P-value Decision N Mean StDev T Df P-value Decision IC 6 4361.00 0,0 12.09 5 0.000 Reject Ho IC 6 4361.00 0.0 35.34 5 0.000 Reject Ho FC 6 3932.7 86.8 FC 6 3943.8 289 Mitragyna inermis root bark extract MItragyna inermis leave extract N Mean StDev T Df P-value Decision N Mean StDev T Df P-value Decision IC 6 4361.00 0.0 22.62 5 0.000 Reject Ho IC 6 4361.00 0.0 37.32 5 0.000 Reject Ho FC 6 3971.5 42.2 FC 6 3978.0 25.1 Piliostigma reticulatum root bark extract Piliostigma reticulatum leave extract N Mean StDev T Df P-value Decision N Mean StDev T Df P-value Decision IC 6 4357.00 0.0 3.66 5 0.015 Reject Ho IC 6 4357.00 0.0 5.83 5 0.002 Reject Ho FC 6 4202.2 103.6 FC 6 4161.0 82.4 Tamarindus indica root bark extract Tamarindus indica leave extract N Mean StDev T Df P-value Decision N Mean StDev T Df P-value Decision IC 6 4357.00 0.0 18.63 5 0.000 Reject Ho IC 6 4357.00 0.0 21.90 5 0.000 Reject Ho FC 6 3725.5 83.0 FC 6 3529.7 92.5 Ho = There is no difference in colour removal of the extracts in the raw water The Table indicated that the pre-determined significance values of all the extracts were less than 0.05. It was often reported that the performance of natural coagulants improves at acidic pH of raw water samples (Bodlund, 2013). Similarly, Marobhe, (2008b) observed that the net surface charge of colloidal particles is reduced at low pH and hense the electrostatic repulsion between the colloids and the thickness of the double layer is also reduced. This suggests that efficient particles destabilization and optimal flocculation occur at lower pH. The floc-formation patterns of these extracts could also be explained by the degree of their solubility or polarity in the water (solvent). The best performance of a crude extract from a finely grinded seed powder could be due to its large total surface area; whereby most of the water soluble proteins are at the solid- liquid interface during the extraction process and this might increase the concentration of active coagulation polymer in the extracts which improves the coagulation process (Hart, 2000). Therefore, these extracts require substantial settling time before a significant turbidity and colour removal can be achieved, hence they could be used with coagulant aid such as Non-ionic polymer which may raise the pH as well as increase the alkalinity. The T-Test results of turbidity and colour removal abilities of the plant extracts indicated that the pre-determined significance values of all the extracts were less than 0.05. This signified that there were differences in the removal of turbidity and colour at the varying dosages of the extracts.
  • 7. Yadima et al.: Turbidity and colour reduction of pond water using extracts of diospyros mespiliformis, mitragyna inermis, piliostigma reticulatum and tamarindus indica in northern Nigeria. AZOJETE, 13(3):420-427. ISSN 1596-2490; e-ISSN 2545-5818, www.azojete.com.ng 426 4. Conclusion The highest percentage of performance for turbidity removal was 18.57% and for colour removal was 22.38% and was established by Tamarindus indica leaves extract which was rather low. The implication was that these plant materials could be used with the help of an aid (coagulation aid) to improve their performances. This investigation has opened up the possibility of using these plant materials as natural coagulants in improving the quality of pond or surface water (on which most rural communities in developing countries depend for drinking and other purposes) that are highly turbid. Therefore, it is recommended that the use of these plant materials should be encouraged among rural communities to improve the quality of pond or surface water. Toxicity test should be carried out on these plant extracts so that safe application concentrations can then be determined, and further diversification of these plant extracts towards treating some common chemicals including heavy metals and pathogenic organisms and other related contaminants in pond or surface water is also recommended. References Bodlund, I. 2013. Coagulant Protein from Plant Materials: Potential Water Treatment Agent. School of Biotechnology, Royal Institute of Technology (KTH), Alba Nova University Center, Stockholm, Sweden. Conte, M., Albert, F., Fucci, L. and Piscopo, M. 2007. Antibacterial Activity of Various Cationic Molecules on Foodborne Pathogens. World Journal of Microbiology and Biotechnology, 23: 1679-1683. Clasen, TF. and Bastable, A. 2003. Faecal Contamination of Drinking Water during Collection and Household Storage. The need to Extend Protection to the Point of Use. Journal of Water and Health, 1(3): 109-115. Ebobganya, PRO., Ocholi, OJ. and Apejt, Y. 2013. A Review on the Use of Plants’ Seeds as Biocoagulants in the Purification of Water. Continental Journal of Biological Sciences, 6(2): 26-32. Ghabremichael, KA., Gunaratna,, KR., Hongbin, H., Brumer, H. and Dalhammer, G. 2005. A simple Purification and Activity Assay of the Coagulant Protein from Moringa oleifera Seed. Water Research, 39(1): 2338-2344. Ghabremichael, KA, Gunaratna, KR. and Dalhammar, G. 2006. Single-Step Ion Exchange Purification of the Coagulant Protein from Moringa oleifera Seed. Applied Microbiology and Biotechnology, 70: 526- 532. Gurcharan, S. and Jagdish, S. 2009. Water Supply and Sanitary Engineering, 6th reprint edition, Nem Chand Jain, Nai Sarak, Delhi India. Hart, TL. 2000. Natural coagulants: An Investigation of Moringa oleifera and Tamarind Seeds. MSc Thesis. The University of Texas, Austin, USA.
  • 8. Arid Zone Journal of Engineering, Technology and Environment, April, 2017; Vol. 13(3):420-427 ISSN 1596-2490; e-ISSN 2545-5818; www.azojete.com.ng 427 Marobhe, JN. 2008. Water Supply in Tanzania and Performance of Local Plant Materials in Purification of Turbid Water. Trita LWR PhD Thesis 1042. Department of Land and Water Resources Engineering, Royal Institute of Technology (KTH), SE-100 44 Stockholm, Sweden. Marobhe, NJ. and Gunaratna, RK. 2012. Effect of Coagulant Protein from Parkinsonia aculeate Seed and Citrus Juice on Bacteria Isolated from Ruvu River in Tanzania. International Journal of Applied Science and Engineering Research, 1(5): 714-724. Muhammad, M. 2016. Turbid water Clarification using Natural Plant Materials as Coagulants. Unpublished M. Eng. Thesis. Department of Civil and Water Resources Engineering, University of Maiduguri, Nigeria. Phani Madhavi, T. and Rajkumar, R. 2013. Utilisation of Natural Coagulants for Reduction of Turbidity from Waste Water. International Journal of Chem. Tech. Research, 5(3): 1119-1123. Renuka, AB. and Jadhav, MV. 2012. Assessment of Purification of Water by using Natural Herbs. Lokavishkar International E-Journal, 1(4): 2-22. Saritha, V. 2012. Screening and Evaluation of Innate Coagulants for Water Treatment: a Sustainable Approach. Vara International Journal of Energy and Environmental Engineering, 3(29): 1-11.