Journal of Environment Protection and Sustainable Development
Articles Information
Journal of Environment Protection and Sustainable Development, Vol.5, No.3, Sep. 2019, Pub. Date: Oct. 11, 2019
Biosorption of Mercury (II) Ions, Congo Red Dye and Their Binary Mixture Using Chemically Activated Mango Leaves Powder
Pages: 107-117 Views: 1369 Downloads: 497
Authors
[01] Mayowa Ezekiel Oladipo, Department of Chemistry, Federal University of Technology, Akure, Nigeria.
[02] Oluwaseun Adekoya Adelaja, Department of Chemistry, Federal University of Technology, Akure, Nigeria.
Abstract
The investigation of the potential of mango leaves powder activated with potassium persulphate (K2S2O8) solution for the removal of mercury (II) ions, Congo red (CR) dye and their binary mixture (BM) was carried out by characterizing the adsorbent (TMLP) using FTIR and conducting batch adsorption studies. The various adsorption parameters were optimized by comparing each adsorption’s standard error of mean, in which the adsorption having the least SEM value with relative maximum removal efficiency was selected i.e. pH 7 (0.7325, 83.11%), contact time 30minutes (0.857, 63.82%), adsorbent dose 0.1g (1.5412, 50.46%), initial concentration 120mg/L (1.7388, 43%) and temperature 333K (0.248, 75%). The experimental equilibrium adsorption data of Hg (II) ions, CR dye and BM fitted best and well to Freundlich, Brunaer-Emmett-Teller and Langmuir respectively having 29.41, 21.28, 23.81mg/g as their respective maximum adsorption capacities. The kinetic data of all the adsorption conformed to the pseudo-second-order kinetic model due to low difference in qexp and qcal values, regression coefficient R2>0.95, high initial sorption rate and lower values of validity models. The rate limiting step of each adsorption may be chemisorptions in this increasing order (binary mixture>Hg2+>CR dye). The thermodynamic adsorption process of Hg (II) ions was spontaneous with the decrease in the degree of randomness and endothermic in nature, the adsorption of CR dye indicated non-spontaneous, increased randomness and endothermic process. At 323K, the adsorption of binary mixture became spontaneous with more random solid-solution interface and it was endothermic in nature.
Keywords
Adsorption, Treated Mango Leaves Powder (TMLP), Mercury (II) Ions, Congo Red Dye, Binary Mixture
References
[01] Kadirvelu, K., Thamaraiselvi, K., &Namasivayam, C. (2001). Removal of heavy metal from industrial wastewaters by adsorption onto activated carbon prepared from an agricultural solid waste. Bioresour. Technol., 76, 63-65.
[02] Williams, C. J., Aderhold, D., &Edyvean, G. J. (1998). Comparison between biosorbents for the removal of metal ions from aqueous solutions. Water Res. 32, 216-224.
[03] WHO Environmental Health Criteria 101, Methyl Mercury, Geneva, World Health Organization (1990) 68.
[04] Reddad, Z., Gerente C., Andres, I., & Le Cloirec, P. (2002). Adsorption of several Metal Ions onto a Low-Cost Biosorbent: Kinetic and Equilibrium Studies. Environmental Science & Technology, 36, 2067-2073.
[05] Uddin, M. T., Rukanuzzaman, M., Khan, M. M. R., & Islam, M. A. (2009). Adsorption of methylene blue from aqueous solution by jackfruit (Artocarpusheteropyllus) leaf powder: A fixed-bed column study. Journal of Environment Management, 90, 3443-3450.
[06] Bhattacharyya, K. G., & Sharma, A. (2003). Adsorption Characteristic of the dye, Brilliant Green, on Neem leaf powder. Dyes and Pigments, 57, 211-222.
[07] Ong, P. S., Ong, S. T., & Hung, Y. T.(2013). Utilization of mango leaf as a low-cost adsorbent for the removal of Cu(II) ions from aqueous solution. Asian Journal of Chemistry, 25 (11), 6141-6145.
[08] Ahmed, M. J., & Alam, M. S. (2003). A rapid spectrophotometric method for the determination of mercury in environmental, biological, soil and plant samples using diphenylthiocarbazone. Spectroscopy 17, 45–52.
[09] Langmuir, I. (1916). The constitutional and fundamental properties of solids and liquids, J. Am. Chem. Soc. 38, pp. 2221-2295.
[10] Freundlich, H. M. F. (1906). Over the adsorption in solution, Z. Phys. Chem. 57, pp. 385-470.
[11] Brunaer, S., Emmett, P. H., & Teller E. (1938). Adsorption of gases in multi molecular layers. Journal of the American Chemical Society, 60 (2), 309-319.
[12] Ho, Y. S., & Mckay, G. (1998). Kinetic model for Pb(II) sorption onto peat. Adsorpt. Sci., Technol., 16, 943-955.
[13] Birtukan, A., Khalid, S., &Nathan, M. (2015). Kinetic, equilibrium and thermodynamic study of 2-Chlorophenol adsorption onto RicinusCommunis pericarp activated carbon from aqueous solutions. Green chemistry Letters and Reviews, 8, 1-12. DOI: 10.1080/17518253.2015.1065348.
[14] Adewumi O. D., Folahan A. A., & Ezekiel O. O. (2017). Kinetics, mechanism, isotherm and thermodynamic studies of liquid-phase adsorption of Pb2+ onto wood activated carbon supported zerovalent iron (WAC-ZVI) nanocomposite. Cogent Chemistry, 3, 1351653.
[15] Khan, T. A., Sharma, S., & Ali, I. (2011). Adsorption of Rhodamine B dye from aqueous solution onto acid activated mango (Magniferaindica) leaf powder: Equilibrium, kinetic and thermodynamic studies. Journal of Toxicology and Environmental Health Sciences Vol. 3 (10), pp. 286-297.
[16] http://www.peroxychem.com/media/90826/AOD_Brochure_Persulfate.pdf&ved=2ahUKEwjC0uWrlJrdAhVCAsAKHa1bAg4QFjABegQICBAB&usg=AOvVaw38bEPGaMNHsd00nN9LanBt.
[17] Yang, H., & Feng, Q.(2010). Characterization of pore-expanded amino-functionalized mesoporoussilicas directly synthesized with dimethyldecylamine and its application for decolorization of sulphonatedazo dyes. J Hazard Mater 180, 106-114.
[18] Gupta, S., Kumar, D., & Gaur, J. P. (2008). Kinetics and isotherm modeling of lead (II) sorption onto some waste plant materials. Chem. Eng. J. 148 (2-3), 226-233.
[19] Aslam, M., Rais, S., Alam, M.,&Pugazhenzi, A. (2013). Adsorption of Hg (II) from Aqueous Solution Using Adulsa (Justiciaadhatoda) Leaves Powder: Kinetic and Equilibrium Studies. Journal of Chemistry, Volume 2013, Article ID 174807, 11 pages.http://dx.doi.org/10.1155/2013/174807.
[20] Umpuch, C., & Jutarat, B. (2013). Adsorption of organic dyes from aqueous solution by surfactant modified corn straw. Inter. J. Chem. Eng. Applications, 4 (3), 134-139.
[21] Wu, C. H.(2007). Adsorption or reactive dyes onto carbon nanotubes: Equilibrium, kinetics and thermodynamics. J. Hazard, Mater. 144, 96-98.
[22] Iscen, C. F., Krian, I., &Iihan, S. (2007). Biosorption of reactive blacks dyes by Fenicilliumrestrictum: the kinetic study. J. Hazard Mater. 143, 335-338.
[23] Enenebeaku, K. C., Okorocha, J. N., Enenebeaku, E. U., Anukan, B., Onyeocha, O. V., Ogukwe, E. C., & Oguzie, E. E. (2016). Adsorption of Congo Red Dye from Aqueous solution using Agricultural Waste. IOSR Journal of Applied Chemistry (IOSR-JAC), Volume 9, 39-51.
[24] Deepak, P., & Pardeep S. (2017). Removal of methylene blue by adsorption onto activated carbon developed from FicusCaricabast. Arabian journal of chemistry, 10, 51445-51451.
[25] Gebremedhin G. (2016). Removal of Chromium (VI) Ions from Aqueous Solution Using Leaves of CordiaAfricana and Sawdust of Acacia Albida. International Journal of Modern Chemistry and Applied Science, 3 (2), 369-377.
[26] Hassanein, T. F., & Koumanova, B. (2010). Evaluation of adsorption potential of the agricultural waste wheat straw on basic yellowish 21. Journal of the University Chemical Technology and Metallurgy, 45 (4), 407-414.
[27] Gupta, S. S., & Bhattacharyya, K. G. (2008). Immobilization of Pb(II), Cd(II) and Ni(II) ions on kaolinite and montmorillonite surfaces from aqueous medium. Journal of Environmental Management 87, 46–58.
[28] Viera, M. G. A., Neto, A. F. A., & Gimenes, M. I. (2010). Sorption kinetics and equilibrium for the removal of nickel ions from aqueous phase on calcinedBofebentonite clay. Journal Hazardous Materials 177, 362-371.
[29] Muhammad, A. A., Maah, M. J., & Yusoff, I. (2010). Study of mango biomass (Mangiferaindica L) as a cationic biosorbent. International Journal of Environment Science & Technology 7 (3), 581-590.
[30] Bouhamed, F., Elouear, Z., & Bouzid, J. (2012). Adsorptive removal of copper (II) from aqueous solutions on activated carbon prepared from Tunisian date stones: Equilibrium, kinetics and thermodynamics. Journal of the Taiwan Institute of Chemical Engineers 43, 741-749.
[31] Kalavathy, M. H., &Miranda, L. R. (2012). Comparison of copper adsorption from aqueous solution using modified and unmodified Heveabrasiliensis saw dust. Desalination 255, 1-7.
[32] Muhammad, H. R., Aqsa, S., Umar, F., Makshoof, A., Tajamal, H., Adnan, M., &Muhammad, S. (2015). PhragmitesKarka as a Biosorbent for the Removal of Mercury Metal ions from aqueous solution: Effect of Modification. Hindawi Publishing Corporation Journal of Chemistry Volume 2015, Article ID 293054, 12 pages.
[33] Yu, L., & Ya-juan, L. (2008). Biosorption isotherms, kinetics and thermodynamics. Separation and Purification Technology 61 (3), 229-242.
[34] Ayla, Ö., Görkem, G., Ayla, Ç., & Bahadır, K. K. (2009). Biosorption of copper (II) ions on Enteromorphaprolifera: application of response surface methodology (RSM). Chemical Engineering Journal 146 (3), 377-387.
[35] Sathya, M., Kumarand, P. E., & Santhi M. (2017). Equilibrium Studies and Kinetics Mechanism for the Removal of Congo red by PassifloraFoetida Activated Carbon–Mno2- Nano Composite. IOSR Journal of Applied Chemistry, 10 (01), 8-14.
[36] Yu, Y., Zhuang, Y. Y., Wang, Z. H., & Qiu, M. Q. (2004) Chemosphere, 54, 425-430.
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