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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 07 Issue: 03 | Mar 2020 www.irjet.net p-ISSN: 2395-0072
© 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 3000
Evaluation of Aluminium Removal Efficiency of Jackfruit Seed Powder
and Guava Leaf Powder
Rijimol.P.M1, Lubna.C.H2
1P.G Student, Department of Civil Engineering, Malabar College of Engineering and Technology, Desamangalam,
Thrissur, Kerala, India
2Assistant Professor, Department of Civil Engineering, Malabar College of Engineering and Technology,
Desamangalam, Thrissur, Kerala, India
---------------------------------------------------------------------***----------------------------------------------------------------------
Abstract - Water is the most essential resource for the
existence of life on earth. At the same time waste water
generation is increasing day by day. This has led to various
techniques for waste water treatment. Naturalcoagulantsare
very effective for the treatment of waste water. The present
study investigates removal of Aluminium ions from industrial
effluent by using jackfruitseed(Artocarpus heterophyllus) and
guava leaf (Psidium guajava) powder. TheparameterslikepH,
alkalinity, acidity, turbidity; TSS, TDS, Al ions, etc are tested.
Key Words: Jackfruit seed (Artocarpus Heterophyllus),
Guava leaf (Psidium guajava), pH, Alkalinity, Acidity,
Turbidity, TSS, TDS, Aluminium ion
1. INTRODUCTION
Most of the developing countries are facing the problem of
water scarcity. The availability of fresh water is limited on
earth compare to the demand. To meet the high demand of
water, different waste water treatment methods can be
adopted. Coagulation is one of the cheapest methodofwaste
water treatment. The most commonly used primary
coagulants are salts of aluminium and iron. The usage of
alum-based coagulants in drinking water treatment process
caused residues in completed drinking water treatment,
which eventually supplied to consumers. This cause risk to
their health. Furthermore, alum-based coagulants are
expensive.
Different industries discharge waste water containing high
aluminium concentration. This causes so many problems to
the environment and humans. Usage of aluminium based
coagulants, also increases the aluminium ion concentration
in the waste water.
Aluminium based coagulant such as alum (aluminium
sulphate (Al2 (SO4)3) or polyaluminium chloride (PACl) are
commonly used in drinking water treatment to enhance the
removal of particulate,collodial anddissolvedsubstancesvia
coagulation processes. The treatment of surface water with
aluminium sulphate has been in operation for over a
hundred years all over the world. The use of alum as a
coagulant for water treatment often leads to higher
concentrations of aluminium in the treatedwaterthaninthe
raw water itself (Srinivisan et al. 1999).
Chemical coagulants can be replaced by natural coagulants.
Natural coagulants are eco-friendly and cost effective.
Jackfruit (Artocarpus heterophyllus) trees belong to the
family Moraceae. They grow abundantly in India,
Bangladesh, and in many parts of Southeast Asia (Rahaman
and others 1999). It is one the most significant evergreen
trees in tropical areas and widely grown in Asia including
India. These jackfruit seed are very cost effective in nature.
Guava ( Psidium guajava) is a tropical andsemitropical plant.
The use of natural plants as natural coagulants in clarifying
turbidity of water has been a common practice since ancient
times. Concerning these practices, the extract of thisplantas
coagulant is believed to have high potential in drinking
water treatment to replace the current conventional
coagulants due to its ability in absorb excess water during
diarrhea. Moreover, this method seems to be inexpensive,
environmental friendly as well as an effective agent in
drinking water treatment, especially in removing heavy
metal and suspended solids (Yap, 2013).
Anu Sundaresan and Anu N (2016), conducted a study on
Feasibility of Natural Coagulant for the Treatment of Dairy
Wastewater. In this study using the two seeds an effective
removal of turbidity is obtained. Coagulating with jack fruit
seed attained 94% removal efficiency, while with the
Common Beans seed obtain a highly removal efficiency upto
99%.
1.1 Objectives of the Study
The main objective of the study is to determine the Al
removal efficiency of jackfruit seed powder and guava leaf
powder. Then comparing the results and identify either
jackfruit seed powder or guava leaf powderismoreeffective
as natural a coagulant.
1.2 Scope of the Study
This study is mainly deals with the usage of natural
coagulants for aluminium ion removal from waste water.
Usage of natural coagulants alone or in combination with
other chemical coagulants will reduce the cost of treatment
process. By conducting this study the optimum dosage of
coagulant is determined.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 07 Issue: 03 | Mar 2020 www.irjet.net p-ISSN: 2395-0072
© 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 3001
2. MATERIALS AND METHODS
The effluent was collected from an Aluminium powder
coating industry at Thrissur. The samples were collected in
sterilized bottles and were preserved in the refrigerator
during storage. Initial characterization of waste water like
pH, alkalinity, acidity, turbidity; TSS, TDS, Al ions, etc were
determined.
Fig -1 : Image of sample
Table -1: Effluent characteristics before treatment
Sl . no Parameter Value
1 pH 4.2
2
Total hardness
(mg/l)
550
3 BOD(mg/l) 280
4 COD(mg/l) 520
5 TSS(mg/l) 3
6 TDS(mg/l) 6955
7 Turbidity(NTU) 3
8
Aluminium
ion(mg/l)
71.67
3.1 Jackfruit Seed Powder Preparation
The jackfruit seed were collected from locality.Thecollected
seeds were thoroughly washed using distilled water and
dried for 48 hours in hot air oven. Then the seeds were
grained to fine powder. The powder was sieved using 0.45
mm mesh and stored in an airtight container to prevent the
entry of moisture into it and to avoid loss of its activity. This
fine powder was used as coagulant for this analysis.
Fig -2 : Jackfruit seed powder
3.2 Guava Leaf Powder Preparation
The guava leaves were collected from locality. The collected
leaves were thoroughly washed using distilled water and
dried for 48 hours in hot air oven. Then the leaves were
grained to fine powder. The powder was sieved using 0.45
mm mesh and stored in an airtight container to prevent the
entry of moisture into it and to avoid loss of its activity. This
fine powder was used as coagulant for this analysis.
Fig -3 : Guava leaf powder
3.3 Experimental Setup
The aluminium ion from the effluent is removed by
coagulation process. Coagulation studies were performed to
determine the optimum conditionandtostudythecoagulant
dosage and contact time. Eachcoagulantwith0.5g,1.5g,2.5g,
3.5g and 4.5 g are mixed with 1000ml of effluent to study its
effects. At the end of the desired contact time, the samples
were filtered using filter paper and the filtratewasanalysed.
Characteristics of effluent after and before treatingandafter
treating are also analysed. The parameters include pH,
turbidity, hardness, BOD, COD, TSS, TDS,andAl aretested.Al
removal efficiency can be determined by the following
formula:
Percentage removal of Al ion =
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 07 Issue: 03 | Mar 2020 www.irjet.net p-ISSN: 2395-0072
© 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 3002
Fig - 4 : Jar test apparatus
4. RESULTS AND DISCUSSIONS
Jackfruit seed powder is added into the waste water at
various concentrations of 0.5, 1.5, 2.5, 3.5, and 4.5 g. As the
jackfruit seed powder dosage increases, aluminiumremoval
efficiency also increases up to 3.5 g/l, beyond this limit it
reaches the equilibrium. There is no further increment in
aluminium removal efficiency. Optimumcoagulantdosageis
3.5 g/l. The maximum efficiency obtained is 92%.
Table -2 : Coagulant Dosage V/S Percentage Al Removal
Efficiency
Coagulant dosage
Percentage Al removal
efficiency of jackfruit seed
powder
0.5 62
1.5 74
2.5 91
3.5 92
4.5 92
Guava leaf powder is added into the waste water at various
concentrations of 0.5, 1.5, 2.5, 3.5, and 4.5 g. The aluminium
removal capacity of guava leaf powder is increases with the
dosage of coagulant. The plot is an ascending curve. The
optimum coagulant dosage is 4.5 g/l andobtainedmaximum
efficiency is 84%.
Table -3 : Coagulant Dosage V/S Percentage Al Removal
Efficiency
Coagulant dosage
Percentage Al removal
efficiency of guava leaf
powder
0.5 54
1.5 60
2.5 72
3.5 76
4.5 84
This graph shows the alominium removal efficiency of
jackfruit seed powder and guava leaf powder. Both the
coagulants have high aluminiumremoval removal efficiency.
While jackfruit seed powder is obtain more efficiency than
guava leaf powder
Chart -1 : Coagulant dosage v/s % removal efficiency
Table -4 : Comparison of the Results
Parameters
Jackfruit seed
powder
Guava leaf
powder
Optimum
coagulant dosage
3.5 4.5
Percentage
aluminium
removal
efficiency
92 84
The optimum jackfruit seed powder dosage is 3.5 g/l and
the aluminium removal efficiency is 92%.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 07 Issue: 03 | Mar 2020 www.irjet.net p-ISSN: 2395-0072
© 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 3003
The optimum dosage of guava leaf powder is obtained as
4.5 mg/l and the aluminium removal efficiency is 84%.
5. CONCLUSIONS
In this study jackfruit seed powder and guava leaf powder
are used as coagulants. The optimum dosage for jackfruit
seed and guava leaf powder is 3.5 g/ l and 4.5 g/l
respectively. The aluminium removal efficiency of jackfruit
seed and guava leaf powder were obtained as 92% and 84%
respectively. From this comparison it can be concluded that
jackfruit seed powder is more efficient than guava leaf
powder as a natural coagulant. The usage of natural
coagulants in waste water treatment units will help to
reduce the cost of the process.
REFERENCES
[1] Anu Sundaresan and Anu N, “Feasibility of Natural
Coagulant for the Treatment of Dairy Wastewater”,
International Journal of Scientific and Engineering
Research, Vol. 7, Issue 4, April 2016, ISSN 2229-5518
[2] Mohd Faiz Muaz Ahmad Zamri, “Effectiveness of
Jackfruit Seed Star ch as Coagulant Aid in Landfill
Leachate Treatment Process”, International Journal of
GEOMAT
[3] Robert Natumanya and James Okot-okumu, “Evaluating
coagulant activity of locally availableUganda”, Int. J.Biol.
Chem. Sci., Vol. 9(6), Dec. 2015, pp. 2535-2547
[4] Selvaraj Raja, “Decolorisation of synthetic dye by guava
(psidiumguajava) leaf powder – A statistical approach”,
Journal of Chemical and Pharmaceutical Research,2012,
4(6):3239-3244
[5] Aneesu Rahman,Aswathy Ramesh, Ranjitha O R ,
Suranya T,and Jency Nadayil,“Efficiency ofjackfruitseed
powder as a natural coagulant”,International Research
Journal of Engineering and Technology, 2018, 5(3)
[6] Joseph, A; Salvato,P.E,DEE,,”Environmental Engineering
and sanitation”, John Wiley, & Sons, Inc, New York, 4th
Edition.; 1993.
[7] Rana. S.V.S., Environmental Pollution: Health and
Toxicology, Narosa Publishing House. New Delhi, 2006.
[8] S.kumarvermal; V.Khandegar,et.al. Removal of
chromium from electroplating industry effluent using
electro coagulation Journal of hazardous, toxic, and
radioactive waste ASCE/ APRIL 2013.
[9] Abhijit M. Deshpande Ramakant,et.al (2012),Treatment
of pharmaceutical Wastewater by Electrochemical
Method: Optimization of Operating parameters by
response surface methodology. J.Hazard. Toxic
radioactive. Waste, 16.316-326 Antony, S.P & Natesan,
B.(2012).
[10] Budiyono, I N Widiasa, and S.M. Hassani, M.R.
Khoshchereh (2012); “treatment of dairy Industry
Wastewater using electrocogulation process”
[11] E.N Vaikosen, et.al (2011); “Evaluation of
pharmacognostical parameters and hea vy metal in
some locally manufactured herbal drugs,”
[12] N. M salem, A. M. Awwad (2011); “Biosorption of Ni(II)
from electroplating wastewater bymodified(Eriobotrya
Japonica) loquat bark”
[13] Katal, R.; pahlavanzadesh, H. (2011), Influence of
different combinations of aluminum and iron electrode
on electrocogulation efficiency: Application to the
treatment of paper mill wastewater.
[14] O. E. Abdel Salam N.A. Reiad b. M.M. Elshafei (2011); A
study of the removal characteristics ofheavymetal from
wastewater by low-cost adsorbent
[15] Dermentzis, K., Chistoforidis, et.al (2011) Removal of
Hexavaent Chromium from electroplating wastewater
by electrocogulation
[16] Heidmann, I.; Calmano, W. (2010),Removal ofNi,Cuand
Cr from a galvanic wastewater in an electrocogulation
system with Fe-and Al- electrodes.
[17] O. Apaydin u. Kurt, m.t. Gonullu, (2009) “An
investigation on thetreatmentoftannerywastewaterby
electrocogulation”
[18] IS- 3306 (2003): Indian standard for industrial
wastewater- specification, secondrevisionIS10500,ICS
No. 13.060.20, January 2
[19] Pallavi N, Dr. S. Mahesh,“Feasibility Study of
MoringaOleifera as a Natural Coagulant for the
TreatmentofDairyWastewater”,International Journal of
Engineering Research, Vol 2, pp: 200-202, July 2013.
[20] KokilaParmar, YogeshDabhi, Rinku
Patel,SarjuPrajapati,“Effectiveness ofMoringaoleifera as
natural coagulant aid for waste watertreatment ofdairy
industry”,AsianJournal OfEnvironmental Science,Vol.7,
pp167-171, December 2012.

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IRJET - Evaluation of Aluminium Removal Efficiency of Jackfruit Seed Powder and Guava Leaf Powder

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 07 Issue: 03 | Mar 2020 www.irjet.net p-ISSN: 2395-0072 © 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 3000 Evaluation of Aluminium Removal Efficiency of Jackfruit Seed Powder and Guava Leaf Powder Rijimol.P.M1, Lubna.C.H2 1P.G Student, Department of Civil Engineering, Malabar College of Engineering and Technology, Desamangalam, Thrissur, Kerala, India 2Assistant Professor, Department of Civil Engineering, Malabar College of Engineering and Technology, Desamangalam, Thrissur, Kerala, India ---------------------------------------------------------------------***---------------------------------------------------------------------- Abstract - Water is the most essential resource for the existence of life on earth. At the same time waste water generation is increasing day by day. This has led to various techniques for waste water treatment. Naturalcoagulantsare very effective for the treatment of waste water. The present study investigates removal of Aluminium ions from industrial effluent by using jackfruitseed(Artocarpus heterophyllus) and guava leaf (Psidium guajava) powder. TheparameterslikepH, alkalinity, acidity, turbidity; TSS, TDS, Al ions, etc are tested. Key Words: Jackfruit seed (Artocarpus Heterophyllus), Guava leaf (Psidium guajava), pH, Alkalinity, Acidity, Turbidity, TSS, TDS, Aluminium ion 1. INTRODUCTION Most of the developing countries are facing the problem of water scarcity. The availability of fresh water is limited on earth compare to the demand. To meet the high demand of water, different waste water treatment methods can be adopted. Coagulation is one of the cheapest methodofwaste water treatment. The most commonly used primary coagulants are salts of aluminium and iron. The usage of alum-based coagulants in drinking water treatment process caused residues in completed drinking water treatment, which eventually supplied to consumers. This cause risk to their health. Furthermore, alum-based coagulants are expensive. Different industries discharge waste water containing high aluminium concentration. This causes so many problems to the environment and humans. Usage of aluminium based coagulants, also increases the aluminium ion concentration in the waste water. Aluminium based coagulant such as alum (aluminium sulphate (Al2 (SO4)3) or polyaluminium chloride (PACl) are commonly used in drinking water treatment to enhance the removal of particulate,collodial anddissolvedsubstancesvia coagulation processes. The treatment of surface water with aluminium sulphate has been in operation for over a hundred years all over the world. The use of alum as a coagulant for water treatment often leads to higher concentrations of aluminium in the treatedwaterthaninthe raw water itself (Srinivisan et al. 1999). Chemical coagulants can be replaced by natural coagulants. Natural coagulants are eco-friendly and cost effective. Jackfruit (Artocarpus heterophyllus) trees belong to the family Moraceae. They grow abundantly in India, Bangladesh, and in many parts of Southeast Asia (Rahaman and others 1999). It is one the most significant evergreen trees in tropical areas and widely grown in Asia including India. These jackfruit seed are very cost effective in nature. Guava ( Psidium guajava) is a tropical andsemitropical plant. The use of natural plants as natural coagulants in clarifying turbidity of water has been a common practice since ancient times. Concerning these practices, the extract of thisplantas coagulant is believed to have high potential in drinking water treatment to replace the current conventional coagulants due to its ability in absorb excess water during diarrhea. Moreover, this method seems to be inexpensive, environmental friendly as well as an effective agent in drinking water treatment, especially in removing heavy metal and suspended solids (Yap, 2013). Anu Sundaresan and Anu N (2016), conducted a study on Feasibility of Natural Coagulant for the Treatment of Dairy Wastewater. In this study using the two seeds an effective removal of turbidity is obtained. Coagulating with jack fruit seed attained 94% removal efficiency, while with the Common Beans seed obtain a highly removal efficiency upto 99%. 1.1 Objectives of the Study The main objective of the study is to determine the Al removal efficiency of jackfruit seed powder and guava leaf powder. Then comparing the results and identify either jackfruit seed powder or guava leaf powderismoreeffective as natural a coagulant. 1.2 Scope of the Study This study is mainly deals with the usage of natural coagulants for aluminium ion removal from waste water. Usage of natural coagulants alone or in combination with other chemical coagulants will reduce the cost of treatment process. By conducting this study the optimum dosage of coagulant is determined.
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 07 Issue: 03 | Mar 2020 www.irjet.net p-ISSN: 2395-0072 © 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 3001 2. MATERIALS AND METHODS The effluent was collected from an Aluminium powder coating industry at Thrissur. The samples were collected in sterilized bottles and were preserved in the refrigerator during storage. Initial characterization of waste water like pH, alkalinity, acidity, turbidity; TSS, TDS, Al ions, etc were determined. Fig -1 : Image of sample Table -1: Effluent characteristics before treatment Sl . no Parameter Value 1 pH 4.2 2 Total hardness (mg/l) 550 3 BOD(mg/l) 280 4 COD(mg/l) 520 5 TSS(mg/l) 3 6 TDS(mg/l) 6955 7 Turbidity(NTU) 3 8 Aluminium ion(mg/l) 71.67 3.1 Jackfruit Seed Powder Preparation The jackfruit seed were collected from locality.Thecollected seeds were thoroughly washed using distilled water and dried for 48 hours in hot air oven. Then the seeds were grained to fine powder. The powder was sieved using 0.45 mm mesh and stored in an airtight container to prevent the entry of moisture into it and to avoid loss of its activity. This fine powder was used as coagulant for this analysis. Fig -2 : Jackfruit seed powder 3.2 Guava Leaf Powder Preparation The guava leaves were collected from locality. The collected leaves were thoroughly washed using distilled water and dried for 48 hours in hot air oven. Then the leaves were grained to fine powder. The powder was sieved using 0.45 mm mesh and stored in an airtight container to prevent the entry of moisture into it and to avoid loss of its activity. This fine powder was used as coagulant for this analysis. Fig -3 : Guava leaf powder 3.3 Experimental Setup The aluminium ion from the effluent is removed by coagulation process. Coagulation studies were performed to determine the optimum conditionandtostudythecoagulant dosage and contact time. Eachcoagulantwith0.5g,1.5g,2.5g, 3.5g and 4.5 g are mixed with 1000ml of effluent to study its effects. At the end of the desired contact time, the samples were filtered using filter paper and the filtratewasanalysed. Characteristics of effluent after and before treatingandafter treating are also analysed. The parameters include pH, turbidity, hardness, BOD, COD, TSS, TDS,andAl aretested.Al removal efficiency can be determined by the following formula: Percentage removal of Al ion =
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 07 Issue: 03 | Mar 2020 www.irjet.net p-ISSN: 2395-0072 © 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 3002 Fig - 4 : Jar test apparatus 4. RESULTS AND DISCUSSIONS Jackfruit seed powder is added into the waste water at various concentrations of 0.5, 1.5, 2.5, 3.5, and 4.5 g. As the jackfruit seed powder dosage increases, aluminiumremoval efficiency also increases up to 3.5 g/l, beyond this limit it reaches the equilibrium. There is no further increment in aluminium removal efficiency. Optimumcoagulantdosageis 3.5 g/l. The maximum efficiency obtained is 92%. Table -2 : Coagulant Dosage V/S Percentage Al Removal Efficiency Coagulant dosage Percentage Al removal efficiency of jackfruit seed powder 0.5 62 1.5 74 2.5 91 3.5 92 4.5 92 Guava leaf powder is added into the waste water at various concentrations of 0.5, 1.5, 2.5, 3.5, and 4.5 g. The aluminium removal capacity of guava leaf powder is increases with the dosage of coagulant. The plot is an ascending curve. The optimum coagulant dosage is 4.5 g/l andobtainedmaximum efficiency is 84%. Table -3 : Coagulant Dosage V/S Percentage Al Removal Efficiency Coagulant dosage Percentage Al removal efficiency of guava leaf powder 0.5 54 1.5 60 2.5 72 3.5 76 4.5 84 This graph shows the alominium removal efficiency of jackfruit seed powder and guava leaf powder. Both the coagulants have high aluminiumremoval removal efficiency. While jackfruit seed powder is obtain more efficiency than guava leaf powder Chart -1 : Coagulant dosage v/s % removal efficiency Table -4 : Comparison of the Results Parameters Jackfruit seed powder Guava leaf powder Optimum coagulant dosage 3.5 4.5 Percentage aluminium removal efficiency 92 84 The optimum jackfruit seed powder dosage is 3.5 g/l and the aluminium removal efficiency is 92%.
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 07 Issue: 03 | Mar 2020 www.irjet.net p-ISSN: 2395-0072 © 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 3003 The optimum dosage of guava leaf powder is obtained as 4.5 mg/l and the aluminium removal efficiency is 84%. 5. CONCLUSIONS In this study jackfruit seed powder and guava leaf powder are used as coagulants. The optimum dosage for jackfruit seed and guava leaf powder is 3.5 g/ l and 4.5 g/l respectively. The aluminium removal efficiency of jackfruit seed and guava leaf powder were obtained as 92% and 84% respectively. From this comparison it can be concluded that jackfruit seed powder is more efficient than guava leaf powder as a natural coagulant. The usage of natural coagulants in waste water treatment units will help to reduce the cost of the process. REFERENCES [1] Anu Sundaresan and Anu N, “Feasibility of Natural Coagulant for the Treatment of Dairy Wastewater”, International Journal of Scientific and Engineering Research, Vol. 7, Issue 4, April 2016, ISSN 2229-5518 [2] Mohd Faiz Muaz Ahmad Zamri, “Effectiveness of Jackfruit Seed Star ch as Coagulant Aid in Landfill Leachate Treatment Process”, International Journal of GEOMAT [3] Robert Natumanya and James Okot-okumu, “Evaluating coagulant activity of locally availableUganda”, Int. J.Biol. Chem. Sci., Vol. 9(6), Dec. 2015, pp. 2535-2547 [4] Selvaraj Raja, “Decolorisation of synthetic dye by guava (psidiumguajava) leaf powder – A statistical approach”, Journal of Chemical and Pharmaceutical Research,2012, 4(6):3239-3244 [5] Aneesu Rahman,Aswathy Ramesh, Ranjitha O R , Suranya T,and Jency Nadayil,“Efficiency ofjackfruitseed powder as a natural coagulant”,International Research Journal of Engineering and Technology, 2018, 5(3) [6] Joseph, A; Salvato,P.E,DEE,,”Environmental Engineering and sanitation”, John Wiley, & Sons, Inc, New York, 4th Edition.; 1993. [7] Rana. S.V.S., Environmental Pollution: Health and Toxicology, Narosa Publishing House. New Delhi, 2006. [8] S.kumarvermal; V.Khandegar,et.al. Removal of chromium from electroplating industry effluent using electro coagulation Journal of hazardous, toxic, and radioactive waste ASCE/ APRIL 2013. [9] Abhijit M. Deshpande Ramakant,et.al (2012),Treatment of pharmaceutical Wastewater by Electrochemical Method: Optimization of Operating parameters by response surface methodology. J.Hazard. Toxic radioactive. Waste, 16.316-326 Antony, S.P & Natesan, B.(2012). [10] Budiyono, I N Widiasa, and S.M. Hassani, M.R. Khoshchereh (2012); “treatment of dairy Industry Wastewater using electrocogulation process” [11] E.N Vaikosen, et.al (2011); “Evaluation of pharmacognostical parameters and hea vy metal in some locally manufactured herbal drugs,” [12] N. M salem, A. M. Awwad (2011); “Biosorption of Ni(II) from electroplating wastewater bymodified(Eriobotrya Japonica) loquat bark” [13] Katal, R.; pahlavanzadesh, H. (2011), Influence of different combinations of aluminum and iron electrode on electrocogulation efficiency: Application to the treatment of paper mill wastewater. [14] O. E. Abdel Salam N.A. Reiad b. M.M. Elshafei (2011); A study of the removal characteristics ofheavymetal from wastewater by low-cost adsorbent [15] Dermentzis, K., Chistoforidis, et.al (2011) Removal of Hexavaent Chromium from electroplating wastewater by electrocogulation [16] Heidmann, I.; Calmano, W. (2010),Removal ofNi,Cuand Cr from a galvanic wastewater in an electrocogulation system with Fe-and Al- electrodes. [17] O. Apaydin u. Kurt, m.t. Gonullu, (2009) “An investigation on thetreatmentoftannerywastewaterby electrocogulation” [18] IS- 3306 (2003): Indian standard for industrial wastewater- specification, secondrevisionIS10500,ICS No. 13.060.20, January 2 [19] Pallavi N, Dr. S. Mahesh,“Feasibility Study of MoringaOleifera as a Natural Coagulant for the TreatmentofDairyWastewater”,International Journal of Engineering Research, Vol 2, pp: 200-202, July 2013. [20] KokilaParmar, YogeshDabhi, Rinku Patel,SarjuPrajapati,“Effectiveness ofMoringaoleifera as natural coagulant aid for waste watertreatment ofdairy industry”,AsianJournal OfEnvironmental Science,Vol.7, pp167-171, December 2012.