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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 4046
COMPARATIVE STUDY OF EFFICIENCY OF LOCAL PLANTS IN WATER
TREATMENT
Akhila Jinna1, Anu M R2, Nijesh Krishnan3, Vyshnavy Sanal4, Litty Das5
1UG student, Department of civil engineering, UKF College of engineering and technology, Kollam, Kerala
2UG student, Department of civil engineering, UKF College of engineering and technology, Kollam, Kerala
3UG student, Department of civil engineering, UKF College of engineering and technology, Kollam, Kerala
4UG student, Department of civil engineering, UKF College of engineering and technology, Kollam, Kerala
5Assistant Professor, Department of civil engineering, UKF College of engineering and technology,
Kollam, Kerala
---------------------------------------------------------------------***---------------------------------------------------------------------
Abstract -
Coagulation is one of the main processes in water
treatment systems. It is mainly done to remove colloidal as
well as suspended particles that will not settle under plain
sedimentation. Usually chemical coagulants like Alum and
Ferric chloride are used for this purpose. Recent studies
emphasis that these chemical coagulants are associated with
Neurotoxicity and other polluting effects on environments. So
here we were analyzed the efficiency of some locally available
plants like Moringa, Cactus and Aloevera for its coagulation
efficiency. The improvement of water quality parameters like
PH, Chloride, BOD, DO, and COD after treating with natural
coagulants were also assessed. Moringa powder gave a
removal efficiency of 97.5% with a dosage of 70mg/l and
Cactus have 87.6% removal with 60 mg/l.Aloevera could not
give an efficient result that is necessary for an independent
coagulant. It could give only 67% of removal efficiency in its
optimum dosage. Coagulation is highly dependent on many
physio chemical parameters like initial turbidity, PH,
temperature, contact time. For the complete analysis of
natural coagulant as a substitute for conventional synthetic
coagulants, all these factors should be considered in deep. So
an optimisation study was done to find the optimumcondition
for getting economical and efficient results from natural
coagulants. Optimisationstudyincludedtheanalysisofchange
in turbity removal with initial turbidity, PH, temperature,
contact time. For that initial turbidity is varied artificiallyand
it is tested for low (40 NTU), Medium (100NTU) and
High(180NTU) turbidities. PH is varied between 4and
9.Temperature ranges of study was 10, 20, 35, 40°c.The
contact time was varied as 0.5 to 1.5 hours. Optimisationstudy
could improve the efficiency of natural coagulant to a very
high extend.
Key Words:Chemical coagulant,AlumNeurotoxicity,Natural
coagulant, Moringa, Cactus, Aloevera, Sustainability
1. INTRODUCTION
Water, the elixir of life, is also the most abundant material in
the nature, second to air. It has a paramount importance in
almost all the natural and anthropogenic activities. For the
development of human life as well as the ecosystems water
carries a vital role. In the past times water is considered to
be infinite good, but currently misuse coupled with the
drastic increase in demand has made this resource to shrink
and lead to water scarcity. Only less than 1% of the whole
water on earth is accessibletohumanand otherliving beings
in the form of fresh water found in lakes, rivers and
underground aquifers. About 97% is saltwater that fills the
oceans and nearly 2% lies frozen in the PolarRegions. Water
that exist on the earth can be in gaseous, liquid or solidstate.
As water has the ability to act as universal solvent, pure
water is hard to found in nature. The major part of water
contaminates due to inadequate treatment and disposal of
wastes from human and also livestock, discharges from
industries and over exploitation of these scarce resource.
Water is having a unique property of self-cleansing and
self-purification by allowing pollutants to settle out through
sedimentation and flocculation process. But very fine
suspended particles present in the water which cannot be
removed in plain sedimentation, may sometimes be settled
by increasing their size by changing them into flocculated
particles. For this purpose, a chemical compound (likealum,
Ferric chloride and ferric sulphate) called coagulant is used.
When these coagulant is added to the water to be treated,
which on thorough mixing forms a gelatinous precipitate,
called flocs. Fine mud particles and other colloidal particles
get absorbed to this flocs, forming bigger size flocculated
particles. The process of addition and mixing of coagulant
called coagulation.
Chemical coagulants have superiority in clarifying the
turbid water, still it lacking in terms of green chemistry and
sustainability. Many studies pointed out the worse effects of
chemical coagulants but all these studies are in its childish
ages. Major problem is nothing but the increased amount of
residual aluminium in treated water and is linked to serious
health issues like Alzheimer’s disease and Dementia.
Presence of residual Al in treated water also reported to be
concerned with reduced disinfecting efficiency. Increased
volume of sludge produced is also make it difficult to handle
and dispose it. These all factors are the background of these
experimental study regarding natural coagulants and its
optimum conditions. Here we have done the analysis of
Moringa oleifera, Aloevera and Cactus as natural coagulants
in river water treatment. Also its efficiency in improving
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 4047
other water quality parameters were also studied in this
work.
1.1 Coagulation and Chemical coagulants
In water treatment, coagulation isa processthatoccurs
when a coagulant is added to water to "destabilize" colloidal
suspensions. Conversely, flocculation involves the addition
of polymers that clump the small, destabilized particles
together into larger aggregates so that they can be more
easily separated from the water. Coagulation is a chemical
process that involves neutralization of charge whereas
flocculation is a physical process and does not involve
neutralization of charge.
Coagulationitselfcannotreduceturbidity.Infactturbidity
may increase during coagulation process due to additional
insoluble compounds that are generated by coagulant
addition. The coagulation-flocculationprocesscanbeusedas
a preliminary or intermediary step between other water or
wastewater treatment processes like filtration and
sedimentation. Since therecentstudiesemphasistherelation
of chemical coagulant with Neurotoxicity, and is no
biodegradability arises threat on sustainable future. So it the
farthest timetomovetowardsnaturalcoagulants.Thefactors
influence coagulation is the type of coagulant used, its dose
and mass; pH and initial turbidity of the water that is being
treated; and properties of the pollutants present. The
effectiveness of the coagulation process is also affected by
pretreatments like oxidation.
1.2 Draw backs of chemical coagulant
Previousstudiesshowsthatchemicalcoagulantscanhave
worse effect on human and environments. Major problem
concerning chemical coagulant is increased residual
aluminium in the treated water which is likely to serious
healthissueslikeAlzheimer’sdiseaseanddementia.Presence
of residual Al in treated water also reported to be concerned
with reduced disinfecting efficiency. Chemical coagulant in
majority consist of syntheticorganicpolymerlikeacrylamide
have neurotoxicity and carcinogenic effects. Untreated
chemical monomer and the byproducts of polymer in water
canalso cause detrimental effects onhumanhealth.Incaseof
Iron salts, negligence in process controls will lead to highly
visible rust or stains caused by hydrolysis of iron salts.
Other major drawback of hydrolyzing type of metal
coagulant is generation voluminousoxidesludge.About99%
of Alum sludge contain water and is hard to dewater these
sludge. Alum sludge also cause phosphorous uptake from
plants due to inorganic phosphorous absorption whichleads
to aluminium phytotoxicity. All their drawbacks of chemical
coagulants demands other potential alternatives for water
purification to diminish the environmental damages and to
protect human life. So here we were studied about natural
coagulants.
1.3 Natural coagulant
In the current scenario majority of waterclarificationis
done by using chemical or synthetic coagulants. Some of
them are Aluminum based and some others are Iron based.
Coagulation flocculation process can also be done with
natural coagulants. Natural coagulant can be a plant part
which is safe for life and having the efficiency of forming
flocs in coagulation flocculation process and thereby
removing the colloidal and suspended impurities naturally.
Natural coagulants are safe, ecofriendly and generally
nontoxic in contrast to chemical coagulants. Primarily the
volume of sludge generated by the natural coagulants are
about five times lower than that generated by chemical
based coagulants and these sludge will have a high
nutritional value. More over all the sludge produced by the
natural coagulants are freeof toxicresidualswhichmayhave
polluting effects on environment also linked to Alzheimer’s
disease in human beings. Thus the sludge treatment and
handling cost are lowered and making it a more sustainable
option. The plant extract used as natural coagulant are
locally available, hence it can be considered as a low cost
alternative to chemical and synthetic coagulants.
2.Materials and Methodology
2.1 Materials
2.1.1 Moringa
Moringa oleifera is a fast growing multipurposetropical tree.
It can grow up to 10-12m and trunk diameter 45 cm. The
bark has a whitish grey colour and is surrounded by thick
cork. The tree has open crown of drooping, fragile branches
and leaves built up of feathery foliage of tripinnatte leaves.
Mainly it is used as food and has a wide usage for medicinal,
industrial and animal feeding purpose. Recently emerging
studies emphasize the coagulative efficiency of Moringa
oleifera.
It is a drought tolerant and nutritious tree. In
Asia and Africa the cultivation of MO become increasingly
popular and it also an economically valuable crop. The
antibacterial properties of MO powder make it useful as a
natural clarifier for water purification systems and fish
ponds. . Earlier studieshavefoundtheMoringaoleiferaseeds
are non-toxic, and recommended its use as coagulant in
water treatment.
2.1.2 Aloevera
Aloe Vera specifically refers to the Aloe barbadensis Miller
plant. AloeVera is the oldest medicinal plant everknownand
the most applied medicinal plant Worldwide. This is a
perennial tropical plant that can be cultivated in drought
prone areas. In India, it is scattered in the wild, along the
coast of southern India. It is a stem less or very short
stemmed succulent plant growing to 60–100 cm (24–39 in)
tall, spreading by offsets. The leaves are thick and fleshy,
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 4048
green to grey-green, with some varieties showing white
flecks on their upper and lower stem surfaces .Aloe Vera
plant requires very less water for its growth as it contains
98% of water in its leaves. It contains around 75 nutrients
and 200 active compounds including minerals, amino acids,
enzymes and vitamins. Here the study is based on aloe leave
extract is compared as natural coagulant with other natural
coagulant plant parts.
2.1.3 Cactus
Opuntia ficus-indica is found in the plant family
Cactaceae. This family comprising about 127 genera with
some 1750 known species of the order Caryophyllales. In
extremely hot and dry habitats and in most arid regions
Cactus plant that can store large amounts of water and
survive. There are around 2000 different species of cactus
that differ in size, shape, color and type of habitat. Arid
regions of South and North America consisting of almost all
cacti species. Cacti can be seen in all over the world
because of its attractive physiology. Over exploitation and
habitat loss are major threats to the survival of cacti in the
wild. Cactus Opuntia contains carbohydrates such as d-
galactose, d-xylose and galacturonic acid. Galacturonic acid
is the active ingredient that affords coagulation capability
of Opuntiasap. It is highly possible that Galacturonic acid
exist predominantly in polymeric form that provides a
bridge for particles to adsorb on. Thepoly-galacturonic acid
structure evidently indicates that it is anionic due to partial
deprotonating of carboxylic functional group in aqueous
solution.
2.2 Methodology
2.2.1 Coagulant preparation
Collectedseed pods of Moringaoleiferaareairdried
for three to four days. Matured Pod shells were removed
manually by using a knife; kernels were grounded in a
domestic blender and sieved through 600 micron stainless
steel sieve. This powdered form of moringa with varying
dosage can be used as coagulant for water treatment.
Prepared coagulantscanbepreservedinarefrigeratortillthe
usage. At the timeof experiment stock solutionwasprepared
with different concentrationsofmoringapowder.Thiscanbe
used as coagulant for water treatment.20-100mg/l is taken
for surface water samples.
Succulent Aloe Vera leaves were collected from some
areas of paravur. The leaves were washed under the tap
water to remove the dirt. Thick green cover or epidermis
was carefully separated from the gel part. Then the gel part
was blended in domestic mixer to form liquid andpreserved
in glass bottles in refrigerator. 1% dilution of aloe vera was
made by using 1ml aloe vera gel in 100 ml distilled water
similarly different percentage of aloe vera solutions were
made to use as coagulant.
Fresh cladodes of opuntia ficus was collected and
washed.They were first dried to 80 degree Celsius and
ground to powder.Sieved to obtain solids with diameter of
0.45 – 1.25 mm.The solids are then usedasrawcoagulantfor
surface water treatment.
2.2.2 Sample collection
Surface water was collected from Ithikkara River.
Ithikkara River is a 56Km long river in kerala, India. It
originates in the Kulathupuzha hills in the Western Ghats
and flows through the kollam district, finally emptying into
Paravur Lake. The village of Ithikkara is located on the river,
15Km from the port of Kollam. The river also flows through
the settlements of Chathannoor and Pooyappally.
Surface water sample should be collected as per the
standard procedures. Samples should be collected. as far as
possible, from midstream at mid depths. Sampling too near
the bank provide fictitious results. Sites should be selected
preferably where marked quality changes occur and where
there are important river uses such as confluences, major
river discharges or abstractions. Sampling locations can be
fixed by reference to significant features. In this connection
use of reference maps may be helpful. The site should be
reasonably accessible all the year round. Taking of samples
from over the bridges is appropriate. Samples can also be
taken from boats wherever feasible for rivers and lakes.
Unsafe banks should be avoided. Wherever necessary,
sampling should be made by a team using safety jackets.
Sampling by wading, where the rivers are shallow, care
being taken to collect samples upstream of the wader, who
can disturb the bottom sediments.
2.2.3 Initial quality parameters
The physico chemical quality of sample water is first
studied to determine the variations regarding this before
after the commencementofexperiments. Fortheassessment
of quality of collected sample water parameter like initial
turbidity, PH, Total hardness, Chloride, BOD, DO, COD are
studied.
Table -1: Initial quality of water
PARAMETER INITIAL VALUE
Initial turbidity 50NTU
PH 5.6
Total Hardness 140
Chloride 567.5mg/l
DO 2.2mg/l
BOD 1.4
COD 25ppm
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 4049
2.2.4 Optimum dosage by jar test
Coagulationandflocculationareimportantunitprocesses
in water and wastewater treatment plants. The purpose of
coagulation/flocculation is to remove suspended matter,
turbidity, color, microorganisms, and odor producing
substances. Coagulationinvolvestheadditionofchemicalsto
destabilize the suspended particles, colloidal materials, and
macromolecules. Some common coagulants used are
aluminum sulfate (alum) and ferric sulfate. Here we had
analyzed the various dosages of natural coagulants and its
optimum dosages. Flocculation is usually defined as the
aggregation of destabilized particles into larger flocs under
slow mixing conditions. The flocs formed are subsequently
removed by sedimentation and/or filtration. A useful
laboratory experiment for the evaluation of
coagulation/flocculation of an untreatedwateristhejartest.
This test provides information on the effects of the
concentrations of the coagulants, mixing of the raw water,
and the water quality parameters such as pH and alkalinity
on the coagulation process. The jar test is often used for the
design of treatment facilities and in the routine operation of
treatment plants.
Most extensively used method of coagulation-
flocculation process is jar test analysis. The experiments
were carried out batch wise in six number of beakers
together with six number of rotating paddles.Sample was
homogenously mixed before conducting jar test
experiments.Here the surface water sample that collected
from ittikkara river was used .Initial turbidity and other
prominent physico chemical characteristics of water is
assessed prior to this experiments. Natural coagulants like
Moringa oleifera,Cactus opuntia and Aloevera wasprepared
and the different concentrations added to the beaker.The
rotating speeds for rapid mixing for one minute at 120 rpm
and after that 20 minute of slow mixing at 40rpm were
allowed. After that a settling time of 30 minutesis permitted.
After all these steps the supernatant is collected using a
pippete and final turbidity is measured in Nephelometer
Turbidity Unit. Optimum dosage of a coagulant is that
minimum dosage which corresponding to lowest residual
turbidity.
2.2.5 Change in parameter after treatment
Table -2: Quality of water after treatment
Parameter Change parameters after
treatment
MO Cactus Aloe
Turbidity
NTU
2 6 25
PH 6.8 7.2 6.6
Hardness
mg/l
98 112 141
Chloride
mg/l
201 556 567
DO
mg/l
5.8 4.5 3.8
BOD
ppm
nil 0.98 1.8
COD
ppm
19 15 25
2.2.6 Optimisation study
Coagulation flocculation is highly dependent on many
phyco chemical parameters like initial turbidity, PH,
temperature, contact time. The efficiency of a coagulant in
removing the turbidity will depend on these characteristics.
So the assessment of variations in result duetothechange in
the above mentioned parameters were incorporated with
these project work. Thus to find the optimum conditions for
the coagulation process so that we can have the most
efficient result from natural coagulant. For the complete
analysis of natural coagulant as a substitute forconventional
synthetic coagulants, all these factors should be considered
in deep. Optimisation study is refers to determine the most
efficient natural coagulant that works economically and
effectively.
3.Result and discussion
3.1 Optimum dosage
0
10
20
30
40
50
60
0 20 40 60 80 100 120
FinalTurbidittyinNTU
Dosage of Moringa oleifera in mg/L
Chart -1: Turbidity variation with dosage of MO
0
10
20
30
40
50
60
70
0 20 40 60 80 100 120
FinalturbidityNTU
Cactus dosage in mg/L
Chart -2: Turbidity variation with dosage of Cactus
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 4050
0
20
40
60
80
100
0% 1% 2% 3% 4% 5% 6%
Finalturbidity
Aloe vera dosage ml/l
Chart -3: Turbidity variation with dosage of Aloevera
For jar test analysis, water sample was collected from
Ittikkara River. The initial turbidity of the collected sample
in 82 NTU. This sample is taken for optimum dosage
study.MO gave the most efficient removal of turbidity. The
optimum dosage of MO was determined as 70mg/l with a
maximum removal of 97.5%.Cactus also gave a comparable
result with MO. The showed optimum dosage was 60mg/l
with a maximum efficiency of 87.6%. Aloe vera is less
efficient compared to the other two natural coagulants.4%
solution gave the maximum removal efficiency. The
efficiency of removal is only 67%.So in short MO and Cactus
were showed a comparable result with conventional
chemical coagulants. But Aloe could not give an appreciable
result in this surface water sample. So it cannot give a
satisfactory result as an independent coagulant.
3.2Optimisation study
Coagulation flocculation is highly dependent on many
physio chemical parameters like initial turbidity, PH,
temperature, contact time. For the complete analysis of
natural coagulant as a substitute for conventional synthetic
coagulants, all these factors should be considered in deep.
Optimisation study is refers to determine the most efficient
natural coagulant that works economically and effectively.
0
10
20
30
40
50
60
0 20 40 60 80 100 120
FinalTurbiityNTU
Moriga dosagein mg/L
100 NTU 180 NTU 40NTU
Chart -4: Variation of turbidity reduction with initial
turbidity for MO
0
20
40
60
0 2 4 6 8 10 12
FinalturbidityNTU
Alovera Dosage in ml/L
40 NTU 100NTU 180 NTU
Chart -5: Variation of turbidity reduction with initial
turbidity for Aloevera
Chart -6: Variation of turbidity reduction with initial
turbidity for Cactus
Turbidity removal efficiency variation for low, medium
and high turbidity was studied. A turbidity range of 40-180
NTU were considered in analysis. Low turbidity 40 NTU,
Medium turbidity 100 NTU and High turbidity 180 NTU
water samples were considered. Ithikkara river water show
wide range of turbidity throughout the seasonal variations.
So it became necessary to study the influence of turbidity
removal of natural coagulant. For low turbidity, removal
efficiency of all natural coagulants were found to be low. As
initial turbidity increases removal efficiency also increases.
In low turbid ware MO show maximum of 75% of removal
and for high turbidity it show 97.2% of efficiency in
removing turbidity. In case of Aloe, similar to MO, it is less
efficient in removing turbidity from low turbid water.
Removal efficiency of Aloe in low turbid water is 50% and
medium turbidity is 60%.It could give removal efficiency of
65% in high turbid water. Cactus gave 95% of removal
efficiency in high turbid water and in low turbidity, it can
gave only 70% of result. All the graph show an increase in
final turbidity after optimum point, it was because excess
amount of coagulant also could decrease removal efficiency.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 4051
0
20
40
60
80
0 50 100 150
Finalturbidity
contact time in minute
moringa cactus aloevera
Chart -7: Variation of turbidity reduction with contact time
Contact time is an important factor that affect the
removal of turbidity. Normally all coagulants will show
increasing efficiency as contact time increases. But the rate
of removal would go on decreasing as time passes. All the
natural coagulants follow similar profilesinthisexperiment.
As contact time increasesremoval ofturbidityalsoincreases.
But too much contact time did not increase the overall
efficiency of treatment system.
0
10
20
30
0 2 4 6 8 10 12
Finalturbidity
PH
moringa cactus Aloevera
Chart -8: Variation of turbidity reduction with PH
PH is another vital factor in coagulation process. The
data show a low degree of turbidity reduction at extreme
temperatures. All the chemical coagulant have itsownrange
of PH for efficient performance during coagulation. Alum is
having a very narrow range of PH for good floc formation.
The effective range of PH for Alum is 6.5 to 8.3.So PH
adjustments should be done before the coagulation process
commences. It also add to the overall cost of treatment and
treated water quality. Ferric sulphate have a p range of 4to7
and above 9. Performance of natural coagulants arefound to
be good for a wide range of PH. So adjustment is not
necessary in n natural coagulants.
Chart -9: Variation of turbidity reduction with
temperature
All natural coagulant that we considered in this study
show low removal efficiency in low temperatures. We had
studied 10oC, 20 oC, 35 oC and 40 oC .Efficiency of turbidity
removal increase with increase in temperature. The best
result obtained at 35 oC then coagulation activity get
retarded. It may be because of the disintegration of flocs at
higher temperature .Lower temperatures can also cause
breakage of flocs that formed during coagulation. Buthigher
temperatures are also not suitable for natural coagulants. It
is because natural coagulants are basically proteins. High
temperature can hamper the activityofproteins.Alumisless
efficient in low temperatures. But natural coagulants could
give much improved results than Alum.
4. Conclusion
 From these studies MO is found to be the most
efficient natural coagulant with a removal
efficiency of 97.5 % with an optimum dosage of 70
mg/l, cactus with an optimum dosage of 60mg/l,
show 87.6% of removal. These two arecomparable
result with the alum. But aloe vera is less efficient
and gave only 67% of removal efficiency.
 Natural coagulant work well in 350 C and which is
normal temperature of surface water. Extremely
high and low temperature was also got affectedthe
coagulation of chemical as well as natural
coagulant.
 The optimum PH in case of alum is 6.5 – 8 which is a
very narrow range. The PH showed have to be
adjusted before coagulation process. But natural
coagulation are efficient in wide range of PH. The
experiment showed a low degree of removal at
extreme PH.
 Increase in contact time also increases efficiency.
Maximum removal was found at 120 minutes. As
time increased, rate of removal decreased. But too
much increase in contact time cannot contribute to
the removal efficiency.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 4052
 So natural coagulant like MO and Cactus can
independently use as in coagulation procedure. It
can give better results in all conditions. But
Aloevera can only be used as coagulant aid. It can
give a sustainable solution for the problems
associated with chemical coagulants.
 Further study is required in this field for analyzing
parameters like mixingspeed,methodofextraction
of coagulant and influence of these parameters in
coagulation efficiency.
REFERENCES
[1] Franciele Pereira Camacho et al, “The use of Moringa
oleifera as a natural coagulant in surface water
treatment”, Journal of chemical engineering
[2] Chun-yang yin et al(2010) ,”Emerginguseofplantbased
coagulant for water andwastewater treatment”,Journal
of process chemistry ,45-1437-1444
[3] Jing Dong Zhang et.al(2006) ,”Preliminary study of
cactus as coagulant in water treatment”, Journal of
Process biochemistry 41,730-733
[4] Pritchard et.al(2010) , “Comparison between Moringa
oleifera and chemical coagulants in purification of
water-An alternate sustainable solution for developing
countries”, Journal of Physics andChemistryofthe earth
,38,798-805
[5] G. Muthuraman et al (2007) , “Removal ofturbidityfrom
drinking water using natural coagulants”, Journal of
Industrial and Engineering chemistry,51,502-521
[6] Sook Yan Choy et.al(2014) , “Utilization of plant based
coagulants as future alternative towards sustainable
water clarification”, Journal of Environmental sciences
,28,2178-2189

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Comparative Study of Efficiency of Local Plants in Water Treatment

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 4046 COMPARATIVE STUDY OF EFFICIENCY OF LOCAL PLANTS IN WATER TREATMENT Akhila Jinna1, Anu M R2, Nijesh Krishnan3, Vyshnavy Sanal4, Litty Das5 1UG student, Department of civil engineering, UKF College of engineering and technology, Kollam, Kerala 2UG student, Department of civil engineering, UKF College of engineering and technology, Kollam, Kerala 3UG student, Department of civil engineering, UKF College of engineering and technology, Kollam, Kerala 4UG student, Department of civil engineering, UKF College of engineering and technology, Kollam, Kerala 5Assistant Professor, Department of civil engineering, UKF College of engineering and technology, Kollam, Kerala ---------------------------------------------------------------------***--------------------------------------------------------------------- Abstract - Coagulation is one of the main processes in water treatment systems. It is mainly done to remove colloidal as well as suspended particles that will not settle under plain sedimentation. Usually chemical coagulants like Alum and Ferric chloride are used for this purpose. Recent studies emphasis that these chemical coagulants are associated with Neurotoxicity and other polluting effects on environments. So here we were analyzed the efficiency of some locally available plants like Moringa, Cactus and Aloevera for its coagulation efficiency. The improvement of water quality parameters like PH, Chloride, BOD, DO, and COD after treating with natural coagulants were also assessed. Moringa powder gave a removal efficiency of 97.5% with a dosage of 70mg/l and Cactus have 87.6% removal with 60 mg/l.Aloevera could not give an efficient result that is necessary for an independent coagulant. It could give only 67% of removal efficiency in its optimum dosage. Coagulation is highly dependent on many physio chemical parameters like initial turbidity, PH, temperature, contact time. For the complete analysis of natural coagulant as a substitute for conventional synthetic coagulants, all these factors should be considered in deep. So an optimisation study was done to find the optimumcondition for getting economical and efficient results from natural coagulants. Optimisationstudyincludedtheanalysisofchange in turbity removal with initial turbidity, PH, temperature, contact time. For that initial turbidity is varied artificiallyand it is tested for low (40 NTU), Medium (100NTU) and High(180NTU) turbidities. PH is varied between 4and 9.Temperature ranges of study was 10, 20, 35, 40°c.The contact time was varied as 0.5 to 1.5 hours. Optimisationstudy could improve the efficiency of natural coagulant to a very high extend. Key Words:Chemical coagulant,AlumNeurotoxicity,Natural coagulant, Moringa, Cactus, Aloevera, Sustainability 1. INTRODUCTION Water, the elixir of life, is also the most abundant material in the nature, second to air. It has a paramount importance in almost all the natural and anthropogenic activities. For the development of human life as well as the ecosystems water carries a vital role. In the past times water is considered to be infinite good, but currently misuse coupled with the drastic increase in demand has made this resource to shrink and lead to water scarcity. Only less than 1% of the whole water on earth is accessibletohumanand otherliving beings in the form of fresh water found in lakes, rivers and underground aquifers. About 97% is saltwater that fills the oceans and nearly 2% lies frozen in the PolarRegions. Water that exist on the earth can be in gaseous, liquid or solidstate. As water has the ability to act as universal solvent, pure water is hard to found in nature. The major part of water contaminates due to inadequate treatment and disposal of wastes from human and also livestock, discharges from industries and over exploitation of these scarce resource. Water is having a unique property of self-cleansing and self-purification by allowing pollutants to settle out through sedimentation and flocculation process. But very fine suspended particles present in the water which cannot be removed in plain sedimentation, may sometimes be settled by increasing their size by changing them into flocculated particles. For this purpose, a chemical compound (likealum, Ferric chloride and ferric sulphate) called coagulant is used. When these coagulant is added to the water to be treated, which on thorough mixing forms a gelatinous precipitate, called flocs. Fine mud particles and other colloidal particles get absorbed to this flocs, forming bigger size flocculated particles. The process of addition and mixing of coagulant called coagulation. Chemical coagulants have superiority in clarifying the turbid water, still it lacking in terms of green chemistry and sustainability. Many studies pointed out the worse effects of chemical coagulants but all these studies are in its childish ages. Major problem is nothing but the increased amount of residual aluminium in treated water and is linked to serious health issues like Alzheimer’s disease and Dementia. Presence of residual Al in treated water also reported to be concerned with reduced disinfecting efficiency. Increased volume of sludge produced is also make it difficult to handle and dispose it. These all factors are the background of these experimental study regarding natural coagulants and its optimum conditions. Here we have done the analysis of Moringa oleifera, Aloevera and Cactus as natural coagulants in river water treatment. Also its efficiency in improving
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 4047 other water quality parameters were also studied in this work. 1.1 Coagulation and Chemical coagulants In water treatment, coagulation isa processthatoccurs when a coagulant is added to water to "destabilize" colloidal suspensions. Conversely, flocculation involves the addition of polymers that clump the small, destabilized particles together into larger aggregates so that they can be more easily separated from the water. Coagulation is a chemical process that involves neutralization of charge whereas flocculation is a physical process and does not involve neutralization of charge. Coagulationitselfcannotreduceturbidity.Infactturbidity may increase during coagulation process due to additional insoluble compounds that are generated by coagulant addition. The coagulation-flocculationprocesscanbeusedas a preliminary or intermediary step between other water or wastewater treatment processes like filtration and sedimentation. Since therecentstudiesemphasistherelation of chemical coagulant with Neurotoxicity, and is no biodegradability arises threat on sustainable future. So it the farthest timetomovetowardsnaturalcoagulants.Thefactors influence coagulation is the type of coagulant used, its dose and mass; pH and initial turbidity of the water that is being treated; and properties of the pollutants present. The effectiveness of the coagulation process is also affected by pretreatments like oxidation. 1.2 Draw backs of chemical coagulant Previousstudiesshowsthatchemicalcoagulantscanhave worse effect on human and environments. Major problem concerning chemical coagulant is increased residual aluminium in the treated water which is likely to serious healthissueslikeAlzheimer’sdiseaseanddementia.Presence of residual Al in treated water also reported to be concerned with reduced disinfecting efficiency. Chemical coagulant in majority consist of syntheticorganicpolymerlikeacrylamide have neurotoxicity and carcinogenic effects. Untreated chemical monomer and the byproducts of polymer in water canalso cause detrimental effects onhumanhealth.Incaseof Iron salts, negligence in process controls will lead to highly visible rust or stains caused by hydrolysis of iron salts. Other major drawback of hydrolyzing type of metal coagulant is generation voluminousoxidesludge.About99% of Alum sludge contain water and is hard to dewater these sludge. Alum sludge also cause phosphorous uptake from plants due to inorganic phosphorous absorption whichleads to aluminium phytotoxicity. All their drawbacks of chemical coagulants demands other potential alternatives for water purification to diminish the environmental damages and to protect human life. So here we were studied about natural coagulants. 1.3 Natural coagulant In the current scenario majority of waterclarificationis done by using chemical or synthetic coagulants. Some of them are Aluminum based and some others are Iron based. Coagulation flocculation process can also be done with natural coagulants. Natural coagulant can be a plant part which is safe for life and having the efficiency of forming flocs in coagulation flocculation process and thereby removing the colloidal and suspended impurities naturally. Natural coagulants are safe, ecofriendly and generally nontoxic in contrast to chemical coagulants. Primarily the volume of sludge generated by the natural coagulants are about five times lower than that generated by chemical based coagulants and these sludge will have a high nutritional value. More over all the sludge produced by the natural coagulants are freeof toxicresidualswhichmayhave polluting effects on environment also linked to Alzheimer’s disease in human beings. Thus the sludge treatment and handling cost are lowered and making it a more sustainable option. The plant extract used as natural coagulant are locally available, hence it can be considered as a low cost alternative to chemical and synthetic coagulants. 2.Materials and Methodology 2.1 Materials 2.1.1 Moringa Moringa oleifera is a fast growing multipurposetropical tree. It can grow up to 10-12m and trunk diameter 45 cm. The bark has a whitish grey colour and is surrounded by thick cork. The tree has open crown of drooping, fragile branches and leaves built up of feathery foliage of tripinnatte leaves. Mainly it is used as food and has a wide usage for medicinal, industrial and animal feeding purpose. Recently emerging studies emphasize the coagulative efficiency of Moringa oleifera. It is a drought tolerant and nutritious tree. In Asia and Africa the cultivation of MO become increasingly popular and it also an economically valuable crop. The antibacterial properties of MO powder make it useful as a natural clarifier for water purification systems and fish ponds. . Earlier studieshavefoundtheMoringaoleiferaseeds are non-toxic, and recommended its use as coagulant in water treatment. 2.1.2 Aloevera Aloe Vera specifically refers to the Aloe barbadensis Miller plant. AloeVera is the oldest medicinal plant everknownand the most applied medicinal plant Worldwide. This is a perennial tropical plant that can be cultivated in drought prone areas. In India, it is scattered in the wild, along the coast of southern India. It is a stem less or very short stemmed succulent plant growing to 60–100 cm (24–39 in) tall, spreading by offsets. The leaves are thick and fleshy,
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 4048 green to grey-green, with some varieties showing white flecks on their upper and lower stem surfaces .Aloe Vera plant requires very less water for its growth as it contains 98% of water in its leaves. It contains around 75 nutrients and 200 active compounds including minerals, amino acids, enzymes and vitamins. Here the study is based on aloe leave extract is compared as natural coagulant with other natural coagulant plant parts. 2.1.3 Cactus Opuntia ficus-indica is found in the plant family Cactaceae. This family comprising about 127 genera with some 1750 known species of the order Caryophyllales. In extremely hot and dry habitats and in most arid regions Cactus plant that can store large amounts of water and survive. There are around 2000 different species of cactus that differ in size, shape, color and type of habitat. Arid regions of South and North America consisting of almost all cacti species. Cacti can be seen in all over the world because of its attractive physiology. Over exploitation and habitat loss are major threats to the survival of cacti in the wild. Cactus Opuntia contains carbohydrates such as d- galactose, d-xylose and galacturonic acid. Galacturonic acid is the active ingredient that affords coagulation capability of Opuntiasap. It is highly possible that Galacturonic acid exist predominantly in polymeric form that provides a bridge for particles to adsorb on. Thepoly-galacturonic acid structure evidently indicates that it is anionic due to partial deprotonating of carboxylic functional group in aqueous solution. 2.2 Methodology 2.2.1 Coagulant preparation Collectedseed pods of Moringaoleiferaareairdried for three to four days. Matured Pod shells were removed manually by using a knife; kernels were grounded in a domestic blender and sieved through 600 micron stainless steel sieve. This powdered form of moringa with varying dosage can be used as coagulant for water treatment. Prepared coagulantscanbepreservedinarefrigeratortillthe usage. At the timeof experiment stock solutionwasprepared with different concentrationsofmoringapowder.Thiscanbe used as coagulant for water treatment.20-100mg/l is taken for surface water samples. Succulent Aloe Vera leaves were collected from some areas of paravur. The leaves were washed under the tap water to remove the dirt. Thick green cover or epidermis was carefully separated from the gel part. Then the gel part was blended in domestic mixer to form liquid andpreserved in glass bottles in refrigerator. 1% dilution of aloe vera was made by using 1ml aloe vera gel in 100 ml distilled water similarly different percentage of aloe vera solutions were made to use as coagulant. Fresh cladodes of opuntia ficus was collected and washed.They were first dried to 80 degree Celsius and ground to powder.Sieved to obtain solids with diameter of 0.45 – 1.25 mm.The solids are then usedasrawcoagulantfor surface water treatment. 2.2.2 Sample collection Surface water was collected from Ithikkara River. Ithikkara River is a 56Km long river in kerala, India. It originates in the Kulathupuzha hills in the Western Ghats and flows through the kollam district, finally emptying into Paravur Lake. The village of Ithikkara is located on the river, 15Km from the port of Kollam. The river also flows through the settlements of Chathannoor and Pooyappally. Surface water sample should be collected as per the standard procedures. Samples should be collected. as far as possible, from midstream at mid depths. Sampling too near the bank provide fictitious results. Sites should be selected preferably where marked quality changes occur and where there are important river uses such as confluences, major river discharges or abstractions. Sampling locations can be fixed by reference to significant features. In this connection use of reference maps may be helpful. The site should be reasonably accessible all the year round. Taking of samples from over the bridges is appropriate. Samples can also be taken from boats wherever feasible for rivers and lakes. Unsafe banks should be avoided. Wherever necessary, sampling should be made by a team using safety jackets. Sampling by wading, where the rivers are shallow, care being taken to collect samples upstream of the wader, who can disturb the bottom sediments. 2.2.3 Initial quality parameters The physico chemical quality of sample water is first studied to determine the variations regarding this before after the commencementofexperiments. Fortheassessment of quality of collected sample water parameter like initial turbidity, PH, Total hardness, Chloride, BOD, DO, COD are studied. Table -1: Initial quality of water PARAMETER INITIAL VALUE Initial turbidity 50NTU PH 5.6 Total Hardness 140 Chloride 567.5mg/l DO 2.2mg/l BOD 1.4 COD 25ppm
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 4049 2.2.4 Optimum dosage by jar test Coagulationandflocculationareimportantunitprocesses in water and wastewater treatment plants. The purpose of coagulation/flocculation is to remove suspended matter, turbidity, color, microorganisms, and odor producing substances. Coagulationinvolvestheadditionofchemicalsto destabilize the suspended particles, colloidal materials, and macromolecules. Some common coagulants used are aluminum sulfate (alum) and ferric sulfate. Here we had analyzed the various dosages of natural coagulants and its optimum dosages. Flocculation is usually defined as the aggregation of destabilized particles into larger flocs under slow mixing conditions. The flocs formed are subsequently removed by sedimentation and/or filtration. A useful laboratory experiment for the evaluation of coagulation/flocculation of an untreatedwateristhejartest. This test provides information on the effects of the concentrations of the coagulants, mixing of the raw water, and the water quality parameters such as pH and alkalinity on the coagulation process. The jar test is often used for the design of treatment facilities and in the routine operation of treatment plants. Most extensively used method of coagulation- flocculation process is jar test analysis. The experiments were carried out batch wise in six number of beakers together with six number of rotating paddles.Sample was homogenously mixed before conducting jar test experiments.Here the surface water sample that collected from ittikkara river was used .Initial turbidity and other prominent physico chemical characteristics of water is assessed prior to this experiments. Natural coagulants like Moringa oleifera,Cactus opuntia and Aloevera wasprepared and the different concentrations added to the beaker.The rotating speeds for rapid mixing for one minute at 120 rpm and after that 20 minute of slow mixing at 40rpm were allowed. After that a settling time of 30 minutesis permitted. After all these steps the supernatant is collected using a pippete and final turbidity is measured in Nephelometer Turbidity Unit. Optimum dosage of a coagulant is that minimum dosage which corresponding to lowest residual turbidity. 2.2.5 Change in parameter after treatment Table -2: Quality of water after treatment Parameter Change parameters after treatment MO Cactus Aloe Turbidity NTU 2 6 25 PH 6.8 7.2 6.6 Hardness mg/l 98 112 141 Chloride mg/l 201 556 567 DO mg/l 5.8 4.5 3.8 BOD ppm nil 0.98 1.8 COD ppm 19 15 25 2.2.6 Optimisation study Coagulation flocculation is highly dependent on many phyco chemical parameters like initial turbidity, PH, temperature, contact time. The efficiency of a coagulant in removing the turbidity will depend on these characteristics. So the assessment of variations in result duetothechange in the above mentioned parameters were incorporated with these project work. Thus to find the optimum conditions for the coagulation process so that we can have the most efficient result from natural coagulant. For the complete analysis of natural coagulant as a substitute forconventional synthetic coagulants, all these factors should be considered in deep. Optimisation study is refers to determine the most efficient natural coagulant that works economically and effectively. 3.Result and discussion 3.1 Optimum dosage 0 10 20 30 40 50 60 0 20 40 60 80 100 120 FinalTurbidittyinNTU Dosage of Moringa oleifera in mg/L Chart -1: Turbidity variation with dosage of MO 0 10 20 30 40 50 60 70 0 20 40 60 80 100 120 FinalturbidityNTU Cactus dosage in mg/L Chart -2: Turbidity variation with dosage of Cactus
  • 5. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 4050 0 20 40 60 80 100 0% 1% 2% 3% 4% 5% 6% Finalturbidity Aloe vera dosage ml/l Chart -3: Turbidity variation with dosage of Aloevera For jar test analysis, water sample was collected from Ittikkara River. The initial turbidity of the collected sample in 82 NTU. This sample is taken for optimum dosage study.MO gave the most efficient removal of turbidity. The optimum dosage of MO was determined as 70mg/l with a maximum removal of 97.5%.Cactus also gave a comparable result with MO. The showed optimum dosage was 60mg/l with a maximum efficiency of 87.6%. Aloe vera is less efficient compared to the other two natural coagulants.4% solution gave the maximum removal efficiency. The efficiency of removal is only 67%.So in short MO and Cactus were showed a comparable result with conventional chemical coagulants. But Aloe could not give an appreciable result in this surface water sample. So it cannot give a satisfactory result as an independent coagulant. 3.2Optimisation study Coagulation flocculation is highly dependent on many physio chemical parameters like initial turbidity, PH, temperature, contact time. For the complete analysis of natural coagulant as a substitute for conventional synthetic coagulants, all these factors should be considered in deep. Optimisation study is refers to determine the most efficient natural coagulant that works economically and effectively. 0 10 20 30 40 50 60 0 20 40 60 80 100 120 FinalTurbiityNTU Moriga dosagein mg/L 100 NTU 180 NTU 40NTU Chart -4: Variation of turbidity reduction with initial turbidity for MO 0 20 40 60 0 2 4 6 8 10 12 FinalturbidityNTU Alovera Dosage in ml/L 40 NTU 100NTU 180 NTU Chart -5: Variation of turbidity reduction with initial turbidity for Aloevera Chart -6: Variation of turbidity reduction with initial turbidity for Cactus Turbidity removal efficiency variation for low, medium and high turbidity was studied. A turbidity range of 40-180 NTU were considered in analysis. Low turbidity 40 NTU, Medium turbidity 100 NTU and High turbidity 180 NTU water samples were considered. Ithikkara river water show wide range of turbidity throughout the seasonal variations. So it became necessary to study the influence of turbidity removal of natural coagulant. For low turbidity, removal efficiency of all natural coagulants were found to be low. As initial turbidity increases removal efficiency also increases. In low turbid ware MO show maximum of 75% of removal and for high turbidity it show 97.2% of efficiency in removing turbidity. In case of Aloe, similar to MO, it is less efficient in removing turbidity from low turbid water. Removal efficiency of Aloe in low turbid water is 50% and medium turbidity is 60%.It could give removal efficiency of 65% in high turbid water. Cactus gave 95% of removal efficiency in high turbid water and in low turbidity, it can gave only 70% of result. All the graph show an increase in final turbidity after optimum point, it was because excess amount of coagulant also could decrease removal efficiency.
  • 6. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 4051 0 20 40 60 80 0 50 100 150 Finalturbidity contact time in minute moringa cactus aloevera Chart -7: Variation of turbidity reduction with contact time Contact time is an important factor that affect the removal of turbidity. Normally all coagulants will show increasing efficiency as contact time increases. But the rate of removal would go on decreasing as time passes. All the natural coagulants follow similar profilesinthisexperiment. As contact time increasesremoval ofturbidityalsoincreases. But too much contact time did not increase the overall efficiency of treatment system. 0 10 20 30 0 2 4 6 8 10 12 Finalturbidity PH moringa cactus Aloevera Chart -8: Variation of turbidity reduction with PH PH is another vital factor in coagulation process. The data show a low degree of turbidity reduction at extreme temperatures. All the chemical coagulant have itsownrange of PH for efficient performance during coagulation. Alum is having a very narrow range of PH for good floc formation. The effective range of PH for Alum is 6.5 to 8.3.So PH adjustments should be done before the coagulation process commences. It also add to the overall cost of treatment and treated water quality. Ferric sulphate have a p range of 4to7 and above 9. Performance of natural coagulants arefound to be good for a wide range of PH. So adjustment is not necessary in n natural coagulants. Chart -9: Variation of turbidity reduction with temperature All natural coagulant that we considered in this study show low removal efficiency in low temperatures. We had studied 10oC, 20 oC, 35 oC and 40 oC .Efficiency of turbidity removal increase with increase in temperature. The best result obtained at 35 oC then coagulation activity get retarded. It may be because of the disintegration of flocs at higher temperature .Lower temperatures can also cause breakage of flocs that formed during coagulation. Buthigher temperatures are also not suitable for natural coagulants. It is because natural coagulants are basically proteins. High temperature can hamper the activityofproteins.Alumisless efficient in low temperatures. But natural coagulants could give much improved results than Alum. 4. Conclusion  From these studies MO is found to be the most efficient natural coagulant with a removal efficiency of 97.5 % with an optimum dosage of 70 mg/l, cactus with an optimum dosage of 60mg/l, show 87.6% of removal. These two arecomparable result with the alum. But aloe vera is less efficient and gave only 67% of removal efficiency.  Natural coagulant work well in 350 C and which is normal temperature of surface water. Extremely high and low temperature was also got affectedthe coagulation of chemical as well as natural coagulant.  The optimum PH in case of alum is 6.5 – 8 which is a very narrow range. The PH showed have to be adjusted before coagulation process. But natural coagulation are efficient in wide range of PH. The experiment showed a low degree of removal at extreme PH.  Increase in contact time also increases efficiency. Maximum removal was found at 120 minutes. As time increased, rate of removal decreased. But too much increase in contact time cannot contribute to the removal efficiency.
  • 7. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 4052  So natural coagulant like MO and Cactus can independently use as in coagulation procedure. It can give better results in all conditions. But Aloevera can only be used as coagulant aid. It can give a sustainable solution for the problems associated with chemical coagulants.  Further study is required in this field for analyzing parameters like mixingspeed,methodofextraction of coagulant and influence of these parameters in coagulation efficiency. REFERENCES [1] Franciele Pereira Camacho et al, “The use of Moringa oleifera as a natural coagulant in surface water treatment”, Journal of chemical engineering [2] Chun-yang yin et al(2010) ,”Emerginguseofplantbased coagulant for water andwastewater treatment”,Journal of process chemistry ,45-1437-1444 [3] Jing Dong Zhang et.al(2006) ,”Preliminary study of cactus as coagulant in water treatment”, Journal of Process biochemistry 41,730-733 [4] Pritchard et.al(2010) , “Comparison between Moringa oleifera and chemical coagulants in purification of water-An alternate sustainable solution for developing countries”, Journal of Physics andChemistryofthe earth ,38,798-805 [5] G. Muthuraman et al (2007) , “Removal ofturbidityfrom drinking water using natural coagulants”, Journal of Industrial and Engineering chemistry,51,502-521 [6] Sook Yan Choy et.al(2014) , “Utilization of plant based coagulants as future alternative towards sustainable water clarification”, Journal of Environmental sciences ,28,2178-2189