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Adsorptive Removal of Zinc from Electroplating Effluent by Using Banana Peels as Bio-Sorbent
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1.
International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395-0056 p-ISSN: 2395-0072Volume: 04 Issue: 07 | July -2017 www.irjet.net Adsorptive Removal of Zinc from Electroplating Effluent by Using Banana Peels as Bio-Sorbent Mr. Vivek S. Damal1, Mrs. V. U. Khanapure2 1 Student, Department of Civil Engineering, SavitribaiPhule Pune University, India 2 Professor, Department of Civil Engineering, SavitribaiPhule Pune University, India ---------------------------------------------------------------------***--------------------------------------------------------------------- Abstract - Effluent of electroplating industry is a major contributor for heavy metal pollution in surface water. Pollution due to electroplating industry leads to eutrophication of surface water and bioaccumulation of heavy metals in aquatic animals. Zinc is the main heavy metal found in electroplating effluent which can be removed by various methods. Adsorption is effective and efficient method for removal of heavy metals from effluent. Banana peel is abundantly found material which can be used as bio-sorbent. The present study aims to investigate efficiency of banana peel as an absorbent for removal of zinc from effluent with the help of banana peels by batch study. This study focuses on optimization of contact time, pH and adsorbent dosage of banana peel for removal of heavy metal from effluent of electroplatingindustry. Key Words: Adsorption, Zinc, Banana Peel, Electroplating industry. 1. INTRODUCTION Removal of heavy metals from industrial waste water is important because they are not only contaminating water bodies but also toxic to human being and animals. Electroplating industrial waste water is one of the major contributors to heavy metal pollution in surface water. The traditional heavy metal treatment includes activated carbon adsorption, reverse osmosis, ion exchange, chemical precipitation and electro-dialysis. For the removal of heavy metals from industrial waste water streams the bi-sorption process is used with use of natural, alternative and cheaper adsorbents. The purpose of this study is to check feasibility of bio-sorbent for removal of zinc ion from electroplating industrial waste water. Problem Statement: At present scenario industries directly discharge their effluent into municipal waste water because there is lack of regulations regarding disposal of such effluent and also due to costlier treatment techniques available. Objective of the study is to suggest economical and environment friendly technique by use of banana peels which is easily available as bio-sorbent for removal of zinc from electroplating industrial effluent. 2. EXPERIMENTAL ANALYSIS Preparationof Adsorbent from Banana Peel: The banana peels used to prepare adsorbent in form of powder. This adsorbent used for removal of zinc from the electroplating effluent. These are collected from various fruit juice centers. Firstly Banana peels washed with distilled water 3-4 times to remove other soluble substances. Then banana peels dried in sun light for 5days. Then this banana peels dried in an oven at 900C for 10 hrs. Afterword’s this product again dried in an oven at 1000C for 5 hrs. This banana peel product cooled at room temperature and grinded to powder. Sampling: The effluent samples were collected from the Electroplating industry, Super Auto Plating Pvt. Ltd, Bhosari Pune, Maharashtra,India. Batch Adsorption: All experiments are carried out at room temperature (25- 30°C) in batch method. Batch method was selected because of its simplicity and reliability. The experiments were carried out by taking 100ml effluent sample in a flask and after pH adjustment a 1gm of dried adsorbent was added. The flask wasagitatedatnearabout 60to70rpmfor60minutesusing a mechanical stirrer. After shaking, the suspension was allowed to settle. The residual biomass adsorbed with metal ion was filtered using whatman-1 filter paper. Metal ion estimation using Atomic adsorption spectrophotometer. The percent removal of metals from the solution was calculated by the following equation. Percent removal of metals from the solutionwas calculatedby the followingequation. Where, Co= is the metal ion concentration(mg/l) Ce= is the final ion concentration(mg/l) © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 681
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International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395-0056 p-ISSN: 2395-0072Volume: 04 Issue: 07 | July -2017 www.irjet.net Where, M= mass of adsorbent Co= initial concentrationof metal ion in the solution Ce=Finalconcentrationofmetalioninthesolution(mg/lit) V= volumeof solution (lit), qe = amountof metal ion adsorbed per gram Characteristicsof Adsorbent(BananaPeel): 1. Energy-dispersive X-ray spectroscopy - Scanning Electron Microscopy(EDX-SEM) Table no.01 EDX-SEM analysis Fig. no.02: Before Adsorption Element Weight% Atomic% C K 51.04 59.70 O K 43.40 38.11 Mg K 0.18 0.10 Si K 0.68 0.34 P K 0.21 0.09 Cl K 1.00 0.40 K K 3.04 1.09 Ca K 0.46 0.16 Totals 100.00 Fig. no.03: After Adsorption ParametersaffectingAdsorptionProcess: 1. Effect of pH The effect of pH on percentage removal of zinc banana peel from effluent sample is shown in following figure. It is observed that the percentage removal of zinc increases slowly with increasing pH from 2 to 4 and thereafter drops slowly. The maximum percentage removal of zinc by banana peel was 97.15%. The optimum pH at which maximum removal of zinc is observedis to 4.0 Fig. no.01 EDX-SEM analysis Scanning ElectronSpectroscopy(SEM) © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 682
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International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395-0056 p-ISSN: 2395-0072Volume: 04 Issue: 07 | July -2017 www.irjet.net Fig. no.04: Relation between pH and percentage removal of zinc. 2. Effect of Adsorbent Dose The effect of adsorbent dosage on percentage removal of zinc from effluent sample is shown in following figure no.2. It is observed that initially the percentage removal of zinc increased rapidly with an increase in adsorbent dosage, but after certain adsorbent dosage the removal efficiency did not increase. Fig. no.05: Relation between adsorbent dose and percentageremoval of zinc. 3. Effect of Temperature The effect of temperature on percentage removal of zinc from effluent sample is shown in following figure no.3. With the increase in temperature percentage removal of zinc decreased. For banana peel, zinc removal decreases from 85.05 % to 79.35 % due to the increase in temperature from 30o to 50°C. Fig. no.06: Relation between adsorbent dose and percentageremoval of zinc. The percentage removal is decreased with increase of temperature, so it was concluded that the adsorption reactions are exothermic. Bio sorption capacity also increased with decrease in temperature. The decrease of bio- sorption capacity at higher temperature may be due to the damage of active binding sites in the biomass. The maximum zinc removal is observedat 30°C. 4. Effect of ContactTime The effect of contact time on batch adsorption of zinc at 30°C and at pH 4.0 by banana peel is shown in following figure. During the experiment contact time was varied from 0 to 270min.Theresults showedthat thepercentageremoval of metal ion by adsorbent increased by increasing contact time. The maximum removal of zinc is observedat 270 min. Fig. no. 07: Relation between Contact Time and percentage removal of zinc. © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 683
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International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395-0056 p-ISSN: 2395-0072Volume: 04 Issue: 07 | July -2017 www.irjet.net 3. ADSORPTION ISOTHERMS Adsorption isotherms i.e. Langmuir and Freundlich isothermsare used to characterizethe bio sorption. LangmuirIsotherm: The Langmuir model makes assumptions such as monolayer adsorption and constant adsorption energy. Langmuir equation of adsorptionisotherm is: 1⁄q = 1⁄ qmax + 1⁄ ȋb* qmax) (Cf) Where, qmax and b are the Langmuir constants. The graph of isotherm is plotted below: Graph no.01: Langmuir Isotherm plots for removal of zinc for bananapeel. Freundlich Isotherm Freundlich modeldeals withheterogeneous adsorptionThe Freundlich equationof adsorptionisotherm is: log q = log K + ȋ1⁄nȌ log Cf Where q is the amount adsorbed per unit mass of adsorbent and Cf is equilibrium concentration. The graphs of isotherms are plotted below: Graph no. 02: FreundlichIsothermplots for removal of zinc 4. CONCLUSION 1. The experimental data on batch study showed the maximum removal of 90.49 % was obtained at 4gm of adsorbent for 100ml of effluent. 2. Values of correlation coefficient for Langmuir isotherms are 0.951 and for Freundlich is 0.943. It clearly indicates that Langmuir isotherms fit well for adsorption equilibrium. 3. The removal of zinc from solution strongly depends on pH of the solution, adsorbent dosage, and temperature and contact time. The maximum adsorption zinc was obtained at pH 4.0, adsorbent dosage of 4 gm, contact time 270 min and temperatureat 30°C. Acknowledgements I would like to express the deepest gratitude to my project advisor and mentor Mrs. V. U. Khanapure for her supervision,advice and guidance. I am highly grateful to Professor Dr. S. S. Shastri, Head, Department of Civil Engineering, (SCOE Pune) for providing necessary facilities and encouragement. I express my sincere thanks to all faculty members of the Department of Civil EngineeringSCOE, Pune, for their help. References 1. Madhukar J. Phadtare, S.T. Patil,DzThe Removal heavy metals from industrial waste waterdz,InternationalJournalAdvanced Engineering and ResearchStudies,April-June2015. 2. SunilRajoriya,Balpreetkaur,DzAbsorptiveRemoval of Zinc from Waste Water by Natural Bio-sorbentsdz, International Journal of Engineering ScienceInvention, Volume 3 Issue 6,June 2014,PP.60-80. 3. Ali S.M., Khalid A.R., MajidR.M.,DzThe Removal of Zinc,ChromiumandNickelfromindustrial wastewater © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 684
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International Research Journal
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