Evaluation of Synthesis Method of Fe Loaded Amorphous Silica on the Adsorption of Glyphosate
Main Article Content
Abstract
Amorphous silica from sugarcane bagasse ash (Si-BA) was extracted and used as a support for iron (Fe). The FeSO4 was loaded onto the Si-BA by 3 different methods consisting of refluxing (RF), incipient wetness impregnation (IWI) and physical mixing (PM) methods. The prepared materials used as glyphosate adsorbents were Fe/Si-BA-RF, Fe/Si-BA-IWI and Fe/SI-BA-PM. All adsorbents were further studied by several techniques. There were X-ray diffraction (XRD), energy dispersive X-ray fluorescence (ED-XRF), N2 adsorption-desorption, diffused reflected UV-Visible (DR-UV-Vis) techniques and pH Drift method. The Fe was highly dispersed onto the Si-BA with Fe loading of approximately 2.36-2.55%wt. The Fe/Si-BA-IWI and Fe/Si-BA-PM exhibited a large amount of FexOy oligomer and Fe2O3 species as compared to the Fe/Si-BA-RF. Then, the glyphosate adsorption kinetic was further studied over the Si-BA and all Fe loaded Si-BA. The adsorption kinetic of glyphosate could be described by pseudo-second order kinetic model for all adsorbents. Moreover, the Langmuir and Freundlich isotherm models were applied to study the adsorption isotherms. All adsorbents were fitted well with the Freundlich isotherm model. Based on the Freundlich isotherm, the relative adsorption capacity of the adsorbents could be determined from the Freundlich isotherm constant (KF). The Fe/Si-BA-IWI provided a higher KF value than Fe/Si-BA-PM, Fe/Si-BA-RF and Si-BA, respectively. As the results, the synthesis method of Fe loaded amorphous silica affected the glyphosate adsorption capacity. The highest capacity of Fe/Si-BA-IWI was attributed to its predominately observed FexOy oligomer and Fe2O3 species.
Keywords: sugarcane bagasse ash; silica; iron; refluxing method; incipient wetness impregnation method; physical mixing method; glyphosate; adsorption
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E-mail: onsulang@buu.ac.th
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References
Benbrook, C.M., 2016. Trends in glyphosate herbicide use in the United States and globally. Environmental Sciences Europe, 28(3), 1-15, DOI: 10.1186/s12302-016-0070-0.
Sen, K. and Chattoraj, S., 2021. A comprehensive review of glyphosate adsorption with factors influencing mechanism:Kinetics, isotherms, thermodynamics study. In: S. Bhattacharyya, N.K. Mondal, J. Platos, V. Snášel and P. Krömer, eds. Intelligent Environmental Data Monitoring for Pollution Management. Cambridge: Academic Press, pp. 93-125.
Jia, D., Zhou, C. and Li, C., 2011. Adsorption of glyphosate on resin supported by hydrated iron oxide: equilibrium ad kinetic studies. Water Environment Research, 83(9), 784-790, DOI: 10.1002/j.1554-7531.2011.tb00268.x.
Ross, A.B., Junyapoon, S., Jones, J.M., Williams, A. and Bartle, K.D., 2005. A study of different soots using pyrolysis-GC-MS and comparison with solvent extractable material. Journal of Analytical and Applied Pyrolysis, 74(1-2), 494-501, DOI: 10.1016/j.jaap.2004.11.011.
Zhou, C., Jia, D., Liu, X. and Li, C., 2017. Removal of glyphosate from aqueous solution using nanosizes copper hydroxide modified resin: equilibrium isotherms and kinetics. Journal of Chemical and Engineering Data, 62(10), 3585-3592, DOI: 10.1021/acs.jced.7b00569.
Mojiri, A., Zhou, J.L., Robinson, B., Ohashi, A., Ozaki, N., Kinsaichi, T., Farraji, H. and Vakili, M., 2020. Pesticides in aquatic environments and their removal by adsorption methods. Chemosphere, 253, DOI: 10.1016/j.chemosphere.2020.126646.
Chindaprasirt, P. and Rattanasak, U., 2020. Eco-production of silica from sugarcane bagasse ash for use as a photochromic pigment filter. Scientific Reports, 10, DOI: 10.1038/s41598-020-66885-y.
Zhuravlev, LT., 2020. The surface chemistry of amorphous silica. Zhuravlev model. Colloids and Surfaces A: Physicochemical and Engineering Aspects, 173(1-3), 1-38, DOI: 10.1016/S0927-7757(00)00556-2.
Rovani, S., Santos, J.J., Corio, P. and Fungaro, D.A. 2018. Highly pure silica nanoparticles with high adsorption capacity obtained from sugarcane waste ash. ACS Omega, 3(3), 2618-2627, DOI: 10.1021/acsomega.8b00092.
Koner, S. and Adak, A., 2012. Fixed bed column study for adsolubilization of 2,4-D herbicide on surfactant modified silica gel waste. Journal of The Institution of Engineers (India): Series A, 93, 187-191, DOI: 10.1007/s40030-013-0021-3.
Matias, T., Marques, J., Quina, M.J., Gando-Ferreira, L., Valente, A.J.M., Portugal, A. and Durães, L, 2015. Silica-based aerogels as adsorbents for phenol-derivative compounds. Colloids and Surfaces A: Physicochemical and Engineering Aspects, 480, 260-269, DOI: 10.1016/j.colsurfa.2015.01.074.
Clusellas, A.S., Angelis, L. De, Beltramo, M., Bava, M., Frankenberg, J.D., Vigliarolo, J. Giovanni, N.J., Stripeikis, J.D., Herrera, J.A.R. and Cortalezzi, M.M.F.D., 2019. Glyphosate and AMPA removal from water by solar induced processes using low Fe(III) or Fe(II) concentrations. Environmental Science: Water Research and Technology, 5(11), 1932-1942, DOI: 10.1039/C9EW00442D.
Jiang, X., Ouyang, Z., Zhang, Z., Yang, C., Li, X., Dang, Z. and Wu, P., 2018. Mechanism of glyphosate removal by biochar supported nano-zero-valent iron in aqueous solutions. Colloids and Surfaces A: Physicochemical and Engineering Aspects, 547, 64-72, DOI: 10.1016/j.colsurfa.2018.03.041.
Samuel, L., Wang, R., Dubois, G., Allen, R., Wojtecki, R. and La, Y.-H., 2017. Aminefunctionalized, multi-arm star polymers: a novel platform for removing glyphosate from aqueous media. Chemosphere, 169, 437-442, DOI: 10.1016/j.chemosphere.2016.11.049.
Barja, B.C. and Afenso, M.D.S., 2005. Aminomethylphosphonic acid and glyphosate adsorption onto goethite: A comparative study. Environmental Science and Technology, 39(2), 585-592, DOI: 10.1021/es035055q.
Rivoira, L., Appendini, M., Fiorilli, S., Onida, B., Bubba, M.D. and Bruzzoniti, M.C., 2016. Functionalized iron oxide/SBA-15 sorbent: investigation of adsorption performance towards glyphosate herbicide. Environmental Science and Pollution Research, 23(21), 21682-21691, DOI: 10.1007/s11356-016-7384-8.
Decyk, P., Trejda, M., Ziolek, M., Kujawa, J., Glaszczka, K., Bettahar, M., Monteverdi, S. and Mercy, M., 2003. Physicochemical and catalytic properties of iron-doped silica – the effect of preparation and pretreatment methods. Journal of Catalysis, 219(1), 146-155, DOI:10.1016/S0021-9517(03)00186-6.
Tasfy, S.F.H., Zabidi, N.A.M. and Subbarao, D., 2011. Comparison of synthesis techniques for supported iron nanocatalysts. Journal of Applied Sciences, 11(7), 1150-1156, DOI: 10.3923/jas.2011.1150.1156.
Maldonado, S., Rosa, J.R.D.l., Ortiz, C.J.L., Ramírez, A.H., Barraza, F.F.C. and Valente, J.S., 2014. Low concentration Fe-doped alumina catalysts using sol-gel and impregnation methods: the synthesis, characterization and catalytic performance during the combustion of trichloroethylene. Materials, 7(3), 2062-2086, DOI: 10.3390/ma7032062.
Aguila, G., Valenzuela, A., Guerrero, S and Araya, P., 2013. WGS activity of a novel Cu-ZrO2 catalyst prepared by a reflux method. Comparison with a conventional impregnation method. Catalysis Communications, 39, 82-85, DOI: 10.1016/j.catcom.2013.05.007.
Sophiphun, O., Föttinger, K., Loiha, S., Neramittagapong, A., Prayoonpokarach, S., Rupprechter, G. and Wittayakun, J., 2015. Properties and catalytic performance in phenol hydroxylation of iron on zeolite beta prepared by different methods. Reaction Kinetics, Mechanisms and Catalysis, 116(2), 549-561, DOI: 10.1007/s11144-015-0908-2.
Rakmae, S. and Wittayakun, J., 2015. The effect of gel volume in autoclave on the synthesis of mordenite from rice husk silica by hydrothermal method. Suranaree Journal of Science and Technology, 22(1), 83-91.
Il’ves, V.G., Zuev, M.G. and Sokovnin, S.Y., 2015. Properties of silicon dioxide amorphous nanopowder produced by pulsed electron beam evaporation. Journal of Nanotechnology, 57(12), 2512-2518, DOI: 10.1155/2015/417817.
Ghaffari, Y., Gupta, N.K., Bae, J. and Kim, K.S., 2019. Heterogeneous catalytic performance and stability of iron-loaded ZSM-5, zeolite-A, and silica for phenol degradation: a microscopic and spectroscopic approach. Catalysts, 9(10), 859-873, DOI: 10.3390/catal9100859.
Pereira, R.C., Anizelli, P.R., Mauro, E.D., Valezi, D.F., Costa, A.C.S., Zaia, C.T.B.V. and Zaia, D.A.M., 2019. The effect of pH and ionic strength on the adsorption of glyphosate onto ferrihydrite. Geochemical Transactions, 20(3), 1-14, DOI: 10.1186/s12932-019-0063-1.
Alves, R.H., Reis, T.V.S., Rovani, S. and Fungaro, D.A., 2017. Green synthesis and characterization of biosilica produced from sugarcane waste ash. Journal of Chemistry, 2017, 1-9, DOI: 10.1155/2017/6129035.
Munnik, P., Jongh, P.E. and Jong, K.P., 2015. Recent developments in the synthesis of supported catalysts. Chemical Reviews, 115(14), 6687-6718, DOI: 10.1021/cr500486u.
Busca, G., 2020. Silica-alumina catalytic materials: a critical review. Catalysis Today, 357, 621-629, DOI: 10.1016/j.cattod.2019.05.011.
Ramirez, J.P., 2004. Active iron sites associated with the reaction mechanism of N2O conversions over steam-activated FeMFI zeolites. Journal of Catalysis, 227(2), 512-522, DOI: 10.1016/j.jcat.2004.08.005.
Nechita, M.T., Berlier, G., Martra, G., Coluccia, S., Arena, F., Italiano, G., Teunfio, G. and Parmaliana, A., 2008. Iron ions supported on oxides: Fe/Al2O3 vs. Fe/SiO2. IL NUOVO CIMENTO, 123 (10-11),1541-1551, DOI: 10.1393/ncb/i2008-10726-0.
Kessouri, A., Boukoussa, B., Bengueddach, A. and Hamacha, R., 2018. Synthesis of iron-MFI zeolite and its photocatalytic application for hydroxylation of phenol. Research on Chemical Intermediates, 44(4), 2475-2487, DOI: 10.1007/s11164-017-3241-8.
Ramirez, J.P., Kumar, M.S. and Brückner, A., 2004. Reduction of N2O with CO over FeMFI zeolites: influence of the preparation method on the iron species and catalytic behavior. Journal of Catalysis, 223(1), 13-27, DOI: 10.1016/j.jcat.2004.01.007.
Rutkowska, M., Jankowska, A., Dudek, E.R., Dubiel, W., Kowalczyk, A., Piwowarska, Z., Llopis, S., Díaz, U. and Chmielarz, L., 2020. Modification of MCM-22 zeolite and its derivatives with iron for the application in N2O decomposition. Catalysts, 10(10), 1139-1155, DOI: 10.3390/catal10101139.
Borba, L.L., Cuba, R.M.F., Terán, F.J.C., Castro, M.N. and Mendes., T.A., 2019. Use of adsorbent biochar from Pequi (Caryocar brasiliense) husks for the removal of commercial formulation of glyphosate from aqueous media. Brazilian Archives of Biology and Technology, 62(10), 1-16, DOI: 10.1590/1678-4324-2019180450.
McConnell, J.S. and Hossner, L.R., 1985. pH-dependent adsorption isotherms of glyphosate. Journal of Agricultural and Food Chemistry, 33(6), 1075-1078, DOI: 10.1021/jf00004a043.
Jia, D., Zhou, C. and Li, C., 2011. Adsorption of glyphosate on resin supported by hydrated iron oxide: equilibrium ad kinetic studies. Water Environment Research, 83(9), 784-790, DOI: 10.1002/j.1554-7531.2011.tb00268.x.
Gimsing, A.L. and Borggaard, O.K., 2007. Phosphate and glyphosate adsorption by hematite and ferrihydrite and comparison with other variable-charge minerals. Clay and Clay Minerals, 5(1), 108-114, DOI: 10.1346/CCMN.2007.0550109.
Pathak, S., Saini, S., Kondamudi, K., Upadhyayula, S. and Bhattacharya, S., 2021. Insights into enhanced stability and activity of silica modified SiC supported iron oxide catalyst in sulfuric acid decomposition. Applied Catalysis B: Environmental, 284, DOI: 10.1016/j.apcatb.2020.119613.
Chen, F.-X., Zhou, C.-R., Li, G.-P. and Peng, F.-F., 2016. Thermodynamics and kinetics of glyphosate adsorption on resin D301. Arabian Journal of Chemistry, 9(2), 1665-1669.
Sahoo, T.R. and Prelot, B., 2020. Adsorption processes for the removal of contaminants from wastewater: the perspective role of nanomaterials and nanotechnology. In: B. Bonelli, F.S. Freyria, I. Rossetti and R. Sethi, eds. Nanomaterials for the Detection and Removal of Wastewater Pollutants. Amsterdam: Elsevier, pp. 161-222.
Yan, D., Gang, D.D., Zhang, N. and Lin, L.S., 2013. Adsorptive selenite removal using iron-coated GAC: Modeling selenite breakthrough with the pore surface diffusion model. Journal of Environmental Engineering, 139(2), 213-219, DOI: 10.1061/(ASCE)EE.1943-7870.0000633.
Krstić, V., 2021. Role of zeolite adsorbent in water treatment. In: B. Bhanvase, S. Sonawane, V. Pawade and A. Pandit, eds. Handbook of Nanomaterials for Wastewater Treatment. Amsterdam: Elsevier, pp. 417-481.