International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 2997
EXPERIMENTAL STUDY ON REMOVAL OF TOXIC METALS FROM
LEACHATE USING RICE HUSK AND FLY ASH
C. Vaishnavi1, E. Vasumathi2, P. Visva Barathy3, M. Sathya4, Y. Sathya5
1,2,3,4UG Student, Department of Civil Engineering, Valliammai Engineering College, Tamil Nadu, India
5Assistant Professor(O.G),Department of Civil Engineering, Tamil Nadu, India
-------------------------------------------------------------------------***------------------------------------------------------------------------
ABSTRACT - Leachate is one of the major problems for Municipal Solid Waste (MSW) landfills and cause significant threat to
surface water and ground water. It may contain large amount of organic matter, chlorinated organic and inorganic salts and
heavy metals. Therefore in this study rice husk and fly ash are used for the removal of toxic metals from the leachate. Sorption
takes place due to rice husk. This study purposes to investigate the ability of rice husk to remove Cr, Cu, Ni and other traces.
Adsorption increases with increase in pH was studied. Results show that these low cost adsorbents canbe usedforremovalof toxic
metals.
Keywords: Leachate, toxic metals, Sorption, Adsorption, adsorbent.
1. INTRODUCTION
Leachate generation is a major problem for MSW landfills and causes threat to surface water and ground water due to the
presence of large amount of organic matter, heavy metals, chlorinated organic and inorganic salts. Leachate from landfill
depends on age and type of waste it contains. These substances cause major hazards to the world and can lastformanyyears.1
The dump yard contains all types of Municipal E-waste, agricultural etc. Electronics waste like batteries and television are
dumped in a landfill for many years. So the water that percolatesthroughthiswastecontainstoxicmetalswhicheventuallyend
up in our environment causing severe problem to human health. The heavy metals presentintheLeachatemaycontainatomic
density more than 5. Generally Landfill leachate contains Lead, Cobalt, Chromium, Nickel, Zinc, Iron that causes threat to the
environment.
There are many conventional methods for removing toxic heavy metals fromLandfill Leachate. Thusitisa challengetofindthe
proper treatment to remove the Toxic metals on Landfill Leachate.
Adsorption is an alternative method for economical treatment of Leachate. Compared to all other treatment method, the
adsorption process seems to be appropriate techniques due to its wide applications such as economic feasibility, Ease of
operation, simplicity in design etc.
Generally heavy metals are present in the Leachate at low concentrations and adsorption is suitable even when themetal ions
are present at concentrations as low as 1 mg/L. One of the conventional adsorbent is activated carbon that has been used in
many applications. But due to the high cost of activated carbon it is not much economical. Hence an alternative method of
adsorption technique is choosing low cost adsorbents for the treatment of Leachate.
In this study Rice husk and Fly ash are used as adsorbents for Adsorption method. Due to the increased production of
agricultural waste and waste generated from industries this kind of adsorbents are used. In this study the husk is converted
into Granular Activated Carbon (GAC) for increasing the adsorption process. Rice husk involves in Sorption process and GAC
undergoes Adsorption process.
The adsorption increases when the surface area increases due to the incineration method while treating Rice husk.
The Granular Activated Carbon has high carbon content that tends to increase the Adsorption. Fly ash is used for Absorption
process. Rice husk is used in the adsorption of metals like Chromium (Cr),Nickel (Ni),Copper(Cu) andLead(Pb).Flyashisused
for the removal of Lead (Pb). In this study, the maximum metal removal efficiency was attained at pH 6. The adsorption
increases with increase in contact time and pH were also studied.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 2998
2. MATERIALS AND METHODS
2.1 MATERIALS
2.1.1 ADSORBENT MATERIAL
In this study the leachate is treated using low cost adsorbent such as rice husk and fly ash. The rice husk has been collected
from the local rice mill. It was washed with distilled water for several times to remove the impurities and dirt
particles. To remove the remove moisture, it was dried at 100°C for 4hours.The fly ash has been collected from the paper
industry in Madurantakam.
2.1.2 REAGENTS
Potassium hydroxide (KOH) was used for activation of the adsorbent distilled water for raisingthesolubilityandHydrochloric
acid (HCl) for adjustment of pH. Since the molecular weight of KOH is 56, the ions are more and hence adsorption increases.
2.1.3 EQUIPMENT
The following laboratory equipment were used in the study, Inductively Coupled Plasma Optical Emission Spectroscopy (ICP-
OES) for metal analysis like copper, chromium and nickel,ScanningElectronMicroscope(SEM)todeterminethe morphological
aspect of GAC, Energy Dispersive X-Ray Spectroscopy(EDAX) for elemental analysis of GAC.
2.2 METHODS
2.2.1 PREPARATION OF ADSORBENT
The rice husk is washed and dried off to remove the dust and adhered particles. Potassium hydroxide pellets were used as an
activating agent for preparing GAC. 8.2g of Potassium hydroxide pellets was weighed and soaked in 100ml of distilled water to
form a solution. Add 2g of rice huskand let it soak into a solution. 7 parts of Potassiumhydroxide,2partsofricehuskand1parts
of distilled water is taken to form 1 molar concentration of solution. After 24 hours the husk is filtered and dried in Muffle
furnace for about 3 hours at 600°C. Then the activated carbon is hydrolyzed and dried in oven for about 2 hours at 105°C and
further dried in muffle furnace to convert into Granular Activated Carbon.
The Rice husk is converted to Granular ActivatedCarbon for increasingtheadsorptionprocessbytheincinerationmethod.So to
increase the adsorption,
Potassium hydroxide is dissolved in the husk and is incinerated. Therefore surface areaof the husk increases.Whenthesurface
area of the husk increases the metal uptake also increases.
Fig -1: Granular Activated Carbon from rice husk
3. RESULTS AND DISCUSSION
3.1 LANDFILL LEACHATE SAMPLE
Leachate generated at landfill is collected from nearby dump yard at Pallikaranai. The characteristics of leachate such as COD,
BOD, Dissolved Oxygen, TDS,TSS, turbidity andhardnessisanalyzedandpreservedinrefrigeratorat2°C.InthisstudyCr,Cuand
Ni was analyzed by Inductively Coupled Plasma Optical Emission Spectroscopy (ICP-OES).
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 2999
Table -1 Characteristics of Leachate
PARAMETERS CONCENTRATION UNIT
pH 7.9 -
Turbidity 242 mg/L
BOD 90 mg/L
COD 235 mg/L
Hardness 541.05 mg/L
TDS 389 mg/L
TSS 400 mg/L
Dissolved Oxygen 7 mg/L
Cr 0.037 mg/L
Cu 0.458 mg/L
Ni 0.441 mg/L
3.1 CHARACTERISATION OF ADSORBENT
The adsorbent characteristics is determined by Scanning Electron Microscope (SEM) and Energy Dispersive X-Ray
Spectroscopy (EDAX) analysis. From SEM analysis it is found that the surface of the GAC adsorbent is non uniform. So the
adsorption increases. If the surface of the adsorbent is uniform the adsorption does not takes place.
Fig-2 Surface of Granular Activated Carbon
The Energy Dispersive X-Ray Spectroscopy (EDAX) analysis is made for GAC and it is found that carbon is present in GAC. Due
to increased mass percentage of carbon the adsorption is increased. So it is proved thattheGAChasmoreadsorptionthanRice
husk due to its surface characteristics.
Table-2 Elements present in GAC
Element At.no Mass Norm Atom Abs. Error Rel. Error
% % % % %
C 6 49.77 55.85 13.25 26.6
O 8 34.97 24.96 13.06 37.3
N 7 15.26 14.68 10.84 71.0
S 16 0.00 0.00 0.00 1.69
100 100
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 3000
Fig-3 Elemental Analysis
3.2 ICP-OES ANALYSIS
Inductively Coupled Plasma Optical Emission Spectroscopy (ICP-OES) is a multi-element analytical technique used for the
detection of chemical elements. In this study the metals present in the sample were analyzed by Perkin Elmer, Model: Optima
5300 DV ICP-OES.
Table-3 Percentage of metal removal for Cu
S.no Name of the sample Dilution Factor % of removal (mg/L)
1 Raw Leachate
10
0.458
2 Rice Husk 0.215
3 GAC 0.091
Chart-1 Percentage of metal removal for Cu
Table-4 Percentage of metal removal for Cr
S.no Name of the sample Dilution Factor % of removal (mg/L)
1 Raw Leachate
10
0.037
2 Rice Husk 0.020
3 GAC 0.009
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 3001
Chart -2 Percentage of metal removal for Cr
Table-5 Percentage of metal removal for Ni
S.no Name of the sample Dilution Factor % of removal (mg/L)
1 Raw Leachate
10
0.441
2 Rice Husk 0.305
3 GAC 0.157
Chart-3 Percentage of metal removal for Ni
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 3002
Table -6 Effect of pH
S.no Metals Identified Range of pH Dilution Factor % of removal (mg/L)
1
Cu
2
10
0.075
Cr 0.027
Ni 0.289
2
Cu
4
0.126
Cr 0.035
Ni 0.300
3
Cu
6
0.001
Cr 0.013
Ni 0.164
Chart-4 Effect of pH towards removal of Cr
Chart-5 Effect of pH towards removal of Cu
Chart-6 Effect of pH towards removal of Ni
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 3003
4. CONCLUSION
A number of methods are used for the removal of toxic metals from Leachate water, but it has several disadvantages like high
cost and input of chemicals. So in this study the rice husk and fly ash were used for the removal of toxic metals. The use of GAC
prepared from Rice husk is proved to be the best and economic adsorbent for removing the toxicity from the Leachate water.
From the above experimental procedureand testresultitisprovedthatthemaximummetalremovingcapacityisachievedatpH
6 at which heavy metals like Ni, Cu and Cr were removed from the Leachate by 100th parts upto 80%. Odour and Color were
removed by this treatment process. `
5. REFERENCES
1) Monik Kasman and Shaliza Ibrahim (2016) The Removal of Iron from Landfill Leachate by Rice Husk Packed Bed
Column. “Journal of Chemical and Pharmaceutical Research”,1255-1262.
2) Ying Zhang, Jiaying Zhao, Zhao Jiang, Dexin Shan and Yan Lu (2014) Biosorption of Fe and Mn ions from Aqueous
solutions by Rice husk ash. “Biomed Research International”.
3) Zahir Hussain A and Mohamed Sheriff K.M (2014) Removal of Heavy Metals from wastewater using low cost
adsorbents “ Archives of Applied Science Research” 52-54.
4) Hala Ahmed Hegazi (2013) Removal of Heavy metals from wastewater using agricultural and industrial wastes as
adsorbents “HBRC Journal” Vol 9-Issue 3. 276-282.
5) Motling Sanjay, Dutta Amit and Mukherjee S.N (2013) Applications of Adsorption process for treatment of Landfill
Leachate “ Journal of Environmental Research and Development” Vol 8 No2.
6) Satya Vani Yadla, V. Sridhevi and M.V.V Chandana Lakshmi (2012) Adsorption Performance of Fly ash for the
removal of lead “International Journal of Engineering Research and Technology” Vol 1-Issue 7.2278-0181.
7) Munaf E and Zein R (2010) The use of Rice husk for removal of toxic metals from wastewater “Journal of
Environment Technology”, Vol 18, 1997-Issue 3.
8) Sumra Naeem, Naseem Zahra and Uzma Zafar (2010) Adsorption Studies of Copper on Rice Husk Ash (RHA)
“Bangladesh Journal of Scientific and Industrial Research”,367-370.

IRJET- Experimental Study on Removal of Toxic Metals from Leachate using Rice Husk and Fly Ash

  • 1.
    International Research Journalof Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 2997 EXPERIMENTAL STUDY ON REMOVAL OF TOXIC METALS FROM LEACHATE USING RICE HUSK AND FLY ASH C. Vaishnavi1, E. Vasumathi2, P. Visva Barathy3, M. Sathya4, Y. Sathya5 1,2,3,4UG Student, Department of Civil Engineering, Valliammai Engineering College, Tamil Nadu, India 5Assistant Professor(O.G),Department of Civil Engineering, Tamil Nadu, India -------------------------------------------------------------------------***------------------------------------------------------------------------ ABSTRACT - Leachate is one of the major problems for Municipal Solid Waste (MSW) landfills and cause significant threat to surface water and ground water. It may contain large amount of organic matter, chlorinated organic and inorganic salts and heavy metals. Therefore in this study rice husk and fly ash are used for the removal of toxic metals from the leachate. Sorption takes place due to rice husk. This study purposes to investigate the ability of rice husk to remove Cr, Cu, Ni and other traces. Adsorption increases with increase in pH was studied. Results show that these low cost adsorbents canbe usedforremovalof toxic metals. Keywords: Leachate, toxic metals, Sorption, Adsorption, adsorbent. 1. INTRODUCTION Leachate generation is a major problem for MSW landfills and causes threat to surface water and ground water due to the presence of large amount of organic matter, heavy metals, chlorinated organic and inorganic salts. Leachate from landfill depends on age and type of waste it contains. These substances cause major hazards to the world and can lastformanyyears.1 The dump yard contains all types of Municipal E-waste, agricultural etc. Electronics waste like batteries and television are dumped in a landfill for many years. So the water that percolatesthroughthiswastecontainstoxicmetalswhicheventuallyend up in our environment causing severe problem to human health. The heavy metals presentintheLeachatemaycontainatomic density more than 5. Generally Landfill leachate contains Lead, Cobalt, Chromium, Nickel, Zinc, Iron that causes threat to the environment. There are many conventional methods for removing toxic heavy metals fromLandfill Leachate. Thusitisa challengetofindthe proper treatment to remove the Toxic metals on Landfill Leachate. Adsorption is an alternative method for economical treatment of Leachate. Compared to all other treatment method, the adsorption process seems to be appropriate techniques due to its wide applications such as economic feasibility, Ease of operation, simplicity in design etc. Generally heavy metals are present in the Leachate at low concentrations and adsorption is suitable even when themetal ions are present at concentrations as low as 1 mg/L. One of the conventional adsorbent is activated carbon that has been used in many applications. But due to the high cost of activated carbon it is not much economical. Hence an alternative method of adsorption technique is choosing low cost adsorbents for the treatment of Leachate. In this study Rice husk and Fly ash are used as adsorbents for Adsorption method. Due to the increased production of agricultural waste and waste generated from industries this kind of adsorbents are used. In this study the husk is converted into Granular Activated Carbon (GAC) for increasing the adsorption process. Rice husk involves in Sorption process and GAC undergoes Adsorption process. The adsorption increases when the surface area increases due to the incineration method while treating Rice husk. The Granular Activated Carbon has high carbon content that tends to increase the Adsorption. Fly ash is used for Absorption process. Rice husk is used in the adsorption of metals like Chromium (Cr),Nickel (Ni),Copper(Cu) andLead(Pb).Flyashisused for the removal of Lead (Pb). In this study, the maximum metal removal efficiency was attained at pH 6. The adsorption increases with increase in contact time and pH were also studied.
  • 2.
    International Research Journalof Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 2998 2. MATERIALS AND METHODS 2.1 MATERIALS 2.1.1 ADSORBENT MATERIAL In this study the leachate is treated using low cost adsorbent such as rice husk and fly ash. The rice husk has been collected from the local rice mill. It was washed with distilled water for several times to remove the impurities and dirt particles. To remove the remove moisture, it was dried at 100°C for 4hours.The fly ash has been collected from the paper industry in Madurantakam. 2.1.2 REAGENTS Potassium hydroxide (KOH) was used for activation of the adsorbent distilled water for raisingthesolubilityandHydrochloric acid (HCl) for adjustment of pH. Since the molecular weight of KOH is 56, the ions are more and hence adsorption increases. 2.1.3 EQUIPMENT The following laboratory equipment were used in the study, Inductively Coupled Plasma Optical Emission Spectroscopy (ICP- OES) for metal analysis like copper, chromium and nickel,ScanningElectronMicroscope(SEM)todeterminethe morphological aspect of GAC, Energy Dispersive X-Ray Spectroscopy(EDAX) for elemental analysis of GAC. 2.2 METHODS 2.2.1 PREPARATION OF ADSORBENT The rice husk is washed and dried off to remove the dust and adhered particles. Potassium hydroxide pellets were used as an activating agent for preparing GAC. 8.2g of Potassium hydroxide pellets was weighed and soaked in 100ml of distilled water to form a solution. Add 2g of rice huskand let it soak into a solution. 7 parts of Potassiumhydroxide,2partsofricehuskand1parts of distilled water is taken to form 1 molar concentration of solution. After 24 hours the husk is filtered and dried in Muffle furnace for about 3 hours at 600°C. Then the activated carbon is hydrolyzed and dried in oven for about 2 hours at 105°C and further dried in muffle furnace to convert into Granular Activated Carbon. The Rice husk is converted to Granular ActivatedCarbon for increasingtheadsorptionprocessbytheincinerationmethod.So to increase the adsorption, Potassium hydroxide is dissolved in the husk and is incinerated. Therefore surface areaof the husk increases.Whenthesurface area of the husk increases the metal uptake also increases. Fig -1: Granular Activated Carbon from rice husk 3. RESULTS AND DISCUSSION 3.1 LANDFILL LEACHATE SAMPLE Leachate generated at landfill is collected from nearby dump yard at Pallikaranai. The characteristics of leachate such as COD, BOD, Dissolved Oxygen, TDS,TSS, turbidity andhardnessisanalyzedandpreservedinrefrigeratorat2°C.InthisstudyCr,Cuand Ni was analyzed by Inductively Coupled Plasma Optical Emission Spectroscopy (ICP-OES).
  • 3.
    International Research Journalof Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 2999 Table -1 Characteristics of Leachate PARAMETERS CONCENTRATION UNIT pH 7.9 - Turbidity 242 mg/L BOD 90 mg/L COD 235 mg/L Hardness 541.05 mg/L TDS 389 mg/L TSS 400 mg/L Dissolved Oxygen 7 mg/L Cr 0.037 mg/L Cu 0.458 mg/L Ni 0.441 mg/L 3.1 CHARACTERISATION OF ADSORBENT The adsorbent characteristics is determined by Scanning Electron Microscope (SEM) and Energy Dispersive X-Ray Spectroscopy (EDAX) analysis. From SEM analysis it is found that the surface of the GAC adsorbent is non uniform. So the adsorption increases. If the surface of the adsorbent is uniform the adsorption does not takes place. Fig-2 Surface of Granular Activated Carbon The Energy Dispersive X-Ray Spectroscopy (EDAX) analysis is made for GAC and it is found that carbon is present in GAC. Due to increased mass percentage of carbon the adsorption is increased. So it is proved thattheGAChasmoreadsorptionthanRice husk due to its surface characteristics. Table-2 Elements present in GAC Element At.no Mass Norm Atom Abs. Error Rel. Error % % % % % C 6 49.77 55.85 13.25 26.6 O 8 34.97 24.96 13.06 37.3 N 7 15.26 14.68 10.84 71.0 S 16 0.00 0.00 0.00 1.69 100 100
  • 4.
    International Research Journalof Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 3000 Fig-3 Elemental Analysis 3.2 ICP-OES ANALYSIS Inductively Coupled Plasma Optical Emission Spectroscopy (ICP-OES) is a multi-element analytical technique used for the detection of chemical elements. In this study the metals present in the sample were analyzed by Perkin Elmer, Model: Optima 5300 DV ICP-OES. Table-3 Percentage of metal removal for Cu S.no Name of the sample Dilution Factor % of removal (mg/L) 1 Raw Leachate 10 0.458 2 Rice Husk 0.215 3 GAC 0.091 Chart-1 Percentage of metal removal for Cu Table-4 Percentage of metal removal for Cr S.no Name of the sample Dilution Factor % of removal (mg/L) 1 Raw Leachate 10 0.037 2 Rice Husk 0.020 3 GAC 0.009
  • 5.
    International Research Journalof Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 3001 Chart -2 Percentage of metal removal for Cr Table-5 Percentage of metal removal for Ni S.no Name of the sample Dilution Factor % of removal (mg/L) 1 Raw Leachate 10 0.441 2 Rice Husk 0.305 3 GAC 0.157 Chart-3 Percentage of metal removal for Ni
  • 6.
    International Research Journalof Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 3002 Table -6 Effect of pH S.no Metals Identified Range of pH Dilution Factor % of removal (mg/L) 1 Cu 2 10 0.075 Cr 0.027 Ni 0.289 2 Cu 4 0.126 Cr 0.035 Ni 0.300 3 Cu 6 0.001 Cr 0.013 Ni 0.164 Chart-4 Effect of pH towards removal of Cr Chart-5 Effect of pH towards removal of Cu Chart-6 Effect of pH towards removal of Ni
  • 7.
    International Research Journalof Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 3003 4. CONCLUSION A number of methods are used for the removal of toxic metals from Leachate water, but it has several disadvantages like high cost and input of chemicals. So in this study the rice husk and fly ash were used for the removal of toxic metals. The use of GAC prepared from Rice husk is proved to be the best and economic adsorbent for removing the toxicity from the Leachate water. From the above experimental procedureand testresultitisprovedthatthemaximummetalremovingcapacityisachievedatpH 6 at which heavy metals like Ni, Cu and Cr were removed from the Leachate by 100th parts upto 80%. Odour and Color were removed by this treatment process. ` 5. REFERENCES 1) Monik Kasman and Shaliza Ibrahim (2016) The Removal of Iron from Landfill Leachate by Rice Husk Packed Bed Column. “Journal of Chemical and Pharmaceutical Research”,1255-1262. 2) Ying Zhang, Jiaying Zhao, Zhao Jiang, Dexin Shan and Yan Lu (2014) Biosorption of Fe and Mn ions from Aqueous solutions by Rice husk ash. “Biomed Research International”. 3) Zahir Hussain A and Mohamed Sheriff K.M (2014) Removal of Heavy Metals from wastewater using low cost adsorbents “ Archives of Applied Science Research” 52-54. 4) Hala Ahmed Hegazi (2013) Removal of Heavy metals from wastewater using agricultural and industrial wastes as adsorbents “HBRC Journal” Vol 9-Issue 3. 276-282. 5) Motling Sanjay, Dutta Amit and Mukherjee S.N (2013) Applications of Adsorption process for treatment of Landfill Leachate “ Journal of Environmental Research and Development” Vol 8 No2. 6) Satya Vani Yadla, V. Sridhevi and M.V.V Chandana Lakshmi (2012) Adsorption Performance of Fly ash for the removal of lead “International Journal of Engineering Research and Technology” Vol 1-Issue 7.2278-0181. 7) Munaf E and Zein R (2010) The use of Rice husk for removal of toxic metals from wastewater “Journal of Environment Technology”, Vol 18, 1997-Issue 3. 8) Sumra Naeem, Naseem Zahra and Uzma Zafar (2010) Adsorption Studies of Copper on Rice Husk Ash (RHA) “Bangladesh Journal of Scientific and Industrial Research”,367-370.