Magnetically Active GO-Fe3O4 Nanocomposite for Enhanced Rhodamine B Removal Efficiency
Alexander Souhuat(1), Henry Fonda Aritonang(2*), Harry Steven Julius Koleangan(3)
(1) Department of Chemistry, Faculty of Mathematics and Natural Sciences, Sam Ratulangi University, Jl. Kampus Unsrat Kleak, Manado 95115, Indonesia
(2) Department of Chemistry, Faculty of Mathematics and Natural Sciences, Sam Ratulangi University, Jl. Kampus Unsrat Kleak, Manado 95115, Indonesia
(3) Department of Chemistry, Faculty of Mathematics and Natural Sciences, Sam Ratulangi University, Jl. Kampus Unsrat Kleak, Manado 95115, Indonesia
(*) Corresponding Author
Abstract
According to the World Bank study, approximately 17–20% of water contamination is attributed to the textile industry. The quantity of waste produced increases as a result of increased productivity. Textile wastewater contains dyes such as rhodamine B (RhB), which are hazardous and challenging to remove using standard methods. Adsorption utilizing nano-adsorbents has been widely researched and developed to remove dyes from the environment because of its numerous advantages. Graphene oxide-magnetite (GO-Fe3O4) has been extensively explored as an adsorbent due to its large surface area, strong bonding, and ease of separation from water. In this study, GO-Fe3O4 was synthesized by combining GO from coconut shell with Fe3O4 from iron sand as an absorbent to lower the amount of RhB. Various analytical techniques, including XRD, SEM-EDS, TEM, FTIR, and UV-vis, were employed to examine the properties of the composites. The GO-Fe3O4 exhibited a maximum adsorption capacity of 34.590 mg/g under specific conditions, i.e., 0.5 g adsorbent dosage, pH 4, and a 2 h contact time. The adsorption followed the pseudo-second-order kinetics model with 0.00016 mg/g min adsorption rate while the adsorption isotherm followed the Langmuir model where adsorbent surfaces are spread homogeneously by forming a monolayer.
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[1] Chen, H., Yu, X., Wang, X., He, Y., Zhang, C., Xue, G., Liu, Z., Lao, H., Song, H., Chen, W., Qian, Y., Zhang, A., and Li, X., 2021, Dyeing and finishing wastewater treatment in China: State of the art and perspective, J. Cleaner Prod., 326, 129353.
[2] Yukseler, H., Uzal, N., Sahinkaya, E., Kitis, M., Delik, F.B., and Yetis, U, 2017, Analysis of the best available techniques for wastewaters from a denim manufacturing textile mill, J. Environ. Manage., 203, 1118–1125.
[3] Contreras, M., Grande-Tovar, C.D., Vallejo, W., and Chaves-López, C., 2019, Bio-removal of methylene blue from aqueous solution by Galactomyces geotrichum KL20A, Water, 11 (2), 282.
[4] Pervez, M.N., and Stylios, G.K., 2018, Investigating the synthesis and characterization of a novel “green” H2O2-assisted, water-soluble chitosan/polyvinyl alcohol nanofiber for environmental end uses, Nanomaterials, 8 (6), 395.
[5] Sherlala, A.I.A., Raman, A.A.A., Bello, M.M., and Buthiyappan, A., 2019, Adsorption of arsenic using chitosan magnetic graphene oxide nanocomposite, J. Environ. Manage., 246, 547–556.
[6] Albanio, I.I., Muraro, P.C.L., and da Silva, W.L., 2021, Rhodamine B dye adsorption onto biochar from olive biomass waste, Water, Air, Soil Pollut., 232 (5), 214.
[7] da Silva, W.L., Muraro, P.C.L., Pavoski, G., Espinosa, D.C.R., and dos Santos, J.H.Z., 2022, Preparation and characterization of biochar from cement waste for removal of rhodamine B dye, J. Mater. Cycles Waste Manage., 24 (4), 1333–1342.
[8] Sharma, J., Sharma, S., Bhatt, U., and Soni, V., 2022, Toxic effects of rhodamine B on antioxidant system and photosynthesis of Hydrilla verticillate, J. Hazard. Mater. Lett., 3, 100069.
[9] Zhou, Y., Li, Z., Ji, L., Wang, Z., Cai, L., Guo, J., Song, W., Wang, Y., and Piotrowski, A.M., 2022, Facile preparation of alveolate biochar derived from seaweed biomass with potential removal performance for cationic dye, J. Mol. Liq., 353, 118623.
[10] Kodama, K., Thao, N.T.T., and Saitoh, T., 2023, Effect of air bubbles on the membrane filtration of rhodamine B, Anal. Sci., 39 (9), 1601–1605.
[11] Wei, Z., Kang, X., Xu, S., Zhou, X., Jia, B., and Feng, Q., 2021, Electrochemical oxidation of rhodamine B with cerium and sodium dodecyl benzene sulfonate co-modified Ti/PbO2 electrodes: Preparation, characterization, optimization, application, Chin. J. Chem. Eng., 32, 191–202.
[12] Rahdar, S., Rahdar, A., Zafar, M.N., Shafqat, S.S., and Ahmadi, S., 2019, Synthesis and characterization of MgO supported Fe-Co-Mn nanoparticles with exceptionally high adsorption capacity for rhodamine B dye, J. Mater. Res. Technol., 8 (5), 3800–3810.
[13] Huang, Z., Wang, T., Shen, M., Huang, Z., Chong, Y., and Cui, L., 2019, Coagulation treatment of swine wastewater by the method of in-situ forming layered double hydroxides and sludge recycling for preparation of biochar composite catalyst, Chem. Eng. J., 369, 784–792.
[14] Nubail, A., Yusmaniar, Y., and Rahman, A., 2019, Adsorpsi pewarna eosin Y menggunakan komposit silika gel termodifikasi 3-aminopropiltrietoksisilan (APTES)-karbon aktif dari bahan alam, JRSKT, 8 (2), 1–8.
[15] Tatinting, G.D., Aritonang. H.F., and Wuntu, A.D., 2021, Sintesis nanopartikel Fe3O4-polietilen glikol (PEG) 6000 dari pasir besi pantai Hais sebagai adsorben logam kadmium (Cd), Chem. Prog., 14 (2), 131–137.
[16] Aritonang, H.F., Onggo, D., Ciptati, C., and Radiman, C.L., 2015, Insertion of platinum particles in bacterial cellulose membranes from PtCl4 and H2PtCl6 precursors, Macromol. Symp., 353 (1), 55–61.
[17] Oluwasina, O.O., Fahmi, M.Z., and Oluwasina, O.O., 2023, Performance assessment: Influence of sorbate-sorbent interphase using magnetite modified graphene oxide to improve wastewater treatment, Indones. J. Chem., 23 (4), 1077–1094.
[18] Heidarizadeh, M., Doustkhah, E., Rostamnia, S., Rezaei, P.F., Harzevili, F.D., and Zeynizadeh, B., 2017, Dithiocarbamate to modify magnetic graphene oxide nanocomposite (Fe3O4-GO): A new strategy for covalent enzyme (lipase) immobilization to fabrication a new nanobiocatalyst for enzymatic hydrolysis of PNPD, Int. J. Biol. Macromol., 101, 696–702.
[19] Al-Ruqeishi, M.S., Mohiuddin, T., Al-Moqbali, M., Al-Shukaili, H., Al-Mamari, S., Al-Rashdi, H., Al-Busaidi, R., Sreepal, V., and Nair, R.R., 2020, Graphene oxide synthesis: Optimizing the Hummers and Marcano methods, Nanosci. Nanotechnol. Lett., 12 (1), 88–95.
[20] Kabir Ahmad, R., Anwar Sulaiman, S., Yusup, S., Sham Dol, S., Inayat, M., and Aminu Umar, H., 2021, Exploring the potential of coconut shell biomass for charcoal production, Ain Shams Eng. J., 13 (1), 101499.
[21] Lestari, I., Kurniawan, E., Gusti, D.R., and Yusnelti, Y., 2020, Magnetite Fe3O4-activated carbon composite as adsorbent of rhodamine B dye, IOP Conf. Ser.: Earth Environ. Sci., 483 (1), 012046.
[22] Pauner, I.D.M., Senolinggi, G.P., Dullah, F.A., Laseduw, G.P.D., and Aritonang, H.F., 2023, Magnetic nanocomposite-chitosan based on North Sulawesi iron sand as heavy metal adsorbent and synthetic dyes in textile industry waste, AIP Conf. Proc., 2694 (1), 020001.
[23] Directorate General of Estate Crops, 2022, Statistical of National Leading Estate Crops Commodity 2020-2022, Ministry of Agriculture Republic of Indonesia, Jakarta, Indonesia.
[24] Fu, R., and Zhu, M., 2016, Synthesis and characterization of structure of Fe3O4@graphene oxide nanocomposite, Adv. compos. Let., 25 (6), 143–146.
[25] Tamuntuan, G., Tongkurut, H.J.S., and Pasau, G, 2017, Analisis suseptibilitas dan histeresis magnetik pada endapan pasir besi di Sulawesi Utara, J. MIPA, 6 (2), 105–108.
[26] Sujiono, E.H., Zurnansyah, Z., Zabrian, D., Dahlan, M.Y., Amin, B.D., Samnur, S., and Agus, J., 2020, Graphene oxide based coconut shell waste: synthesis by modified Hummers method and characterization, Heliyon, 6 (8), e04568.
[27] Sebayang, P., Kurniawan, C., Aryanto, D., Setiadi, E.A., Tamba, K., Djuhana, D., and Sudiro, T, 2018, Preparation of Fe3O4/bentonite nanocomposite from natural iron sand by co-precipitation method for adsorbents materials, IOP Conf. Ser.: Mater. Sci. Eng., 316 (1), 012053.
[28] Tanwar, S., and Mathur, D., 2020, Magnetite-graphene oxide nanocomposites: facile synthesis and characterization of optical and magnetic property, Mater. Today: Proc., 30, 17–22.
[29] Jahan, M., and Feni, F., 2022, Environmentally friendly bifunctional catalyst for OOR and OER from coconut shell particles, Adv. Mater. Phys. Chem., 12, 106–123.
[30] Bakti, I.A., and Gareso, P.L., 2018, Characterization of active carbon prepared from coconuts shells using FTIR, XRD and SEM techniques, JIPF Al-Biruni, 7 (1), 33–39.
[31] Liu, G., Wang, L., Wang, B., Gao, T., and Wang, D., 2015, A reduced graphene oxide modified metallic cobalt composite with superior electrochemical performance for supercapacitors, RSC Adv., 5 (78), 63553–63560.
[32] Gautam, D., Samal, R.R., Kumar, S., Hooda, S., and Dheer, N., 2023, One pot chemical co-precipitation preparation of magnetic graphene oxide-deltamethrin nanoformulations for management of Aedes aegypti, J. Appl. Nat. Sci., 15 (1), 194–202.
[33] Yan, J.C., Zeng, X.Q., Ren, T.H., and van der Heide, E., 2015, Exploring an alternative aqueous lubrication concept for biomedical applications: Hydration lubrication based on O/W emulsions combined with graphene oxide, Biosurf. Biotribol., 1 (2), 113–123.
[34] Abbas, R.F., Hami, H.K., Mahdi, N.I., and Waheb, A.A., 2020, Removal of Eriochrome Black T dye by using Al2O3 nanoparticles: Central composite design, isotherm and error analysis, Iran. J. Sci. Technol., Trans. A: Sci., 44 (4), 993–1000.
[35] Jiang, G., Chang, Q., Yang, F., Hu, X., and Tang, H., 2015, Sono-assisted preparation of magnetic ferroferric oxide/graphene oxide nanoparticles and application on dye removal, Chin. J. Chem. Eng., 23 (5), 510–515.
[36] Nuengmatcha, P., Mahachai, R., and Chanthai, S., 2016, Adsorption capacity of thr as-synthetic graphene oxide for the removal of alizarin red S dye from aqueous solution, Orient. J. Chem., 32 (3), 1399–1410.
[37] Jara, A.D., and Kim, J.Y., 2020, Chemical purification processes of the natural crystalline flake graphite for Li-ion battery anodes, Mater. Today Commun., 25, 101437.
[38] Kırbıyık, Ç., Pütün, A.E., and Pütün, E., 2017, Equilibrium, kinetic, and thermodynamic studies of the adsorption of Fe(III) metal ions and 2,4-dichlorophenoxyacetic acid onto biomass-based activated carbon by ZnCl2 activation, Surf. Interfaces, 8, 182–192.
[39] Barale, M., Lefèvre, G., Carrette, F., Catalette, H., Fédoroff, M., and Cote, G., 2008, Effect of the adsorption of lithium and borate species on the zeta potential of particles of cobalt ferrite, nickel ferrite, and magnetite, J. Colloid Interface Sci., 328 (1), 34–40.
[40] Güneş, K., 2023, Isotherm and kinetic modeling of the adsorption of methylene blue, a cationic dye, on pumice, Int. J. Chem. Technol., 7 (1), 67–74.
[41] Chen, L., Li, Y., Du, Q., Wang, Z., Xia, Y., Yedinak, E., Lou, J., and Ci, L., 2017, High performance agar/graphene oxide composite aerogel for methylene blue removal, Carbohydr. Polym., 155, 345–353.
[42] Inyinbor, A.A., Adekola, F.A., and Olatunji, G.A., 2015, Adsorption of rhodamine B dye from aqueous solution on Irvingia gabonensis biomass: Kinetics and thermodynamics studies, S. Afr. J. Chem., 68, 115–125.
[43] Kuśmierek, K., Fronczyk, J., and Świątkowski, A., 2023, Adsorptive removal of rhodamine B dye from aqueous solutions using mineral materials as low-cost adsorbents, Water, Air, Soil Pollut., 234 (8), 531.
[44] Khan, M.I., Almanassra, I.W., Shanableh, A., Atieh, M.A., Manzoor, S., Hayat, M., Besbes, M., Elgharbi, S., Alimi, F., and Jemmali, M., 2024, Utilization of palm leaves powder for removal of rhodamine-B from an aqueous solution, Desalin. Water Treat., 317, 100159.
[45] Matias, C.A., de Oliveira, L.J.G.G., Geremias, R., and Stolberg, J., 2020, Biosorption of rhodamine B from aqueous solution using Araucaria angustifolia sterile bracts, Rev. Int. Contam. Ambiental, 36 (1), 97–104.
[46] Khan, M.I., and Shanableh, A., 2022, Adsorption of rhodamine B from an aqueous solution onto NaOH-treated rice husk, Desalin. Water Treat., 254, 104–115.
[47] Vigneshwaran, S., Sirajudheen, P., Karthikeyan, P., and Meenakshi, S., 2021, Fabrication of sulfur-doped biochar derived from tapioca peel waste with superior adsorption performance for the removal of malachite green and rhodamine B dyes, Surf. Interfaces, 23, 100920.
[48] Li, X., Shi, J., and Luo, X., 2022, Enhanced adsorption of rhodamine B from water by Fe-N co-modified biochar: Preparation, performance, mechanism and reusability, Bioresour. Technol., 343, 126103.
[49] Li, P., Zhao, T., Zhao, Z., Tang, H., Feng, W., and Zhang, Z., 2023, Biochar derived from Chinese herb medicine residues for rhodamine B dye adsorption, ACS Omega, 8 (5), 4813–4825.
[50] Azeez, L., Adefunke, O., Oyedeji, A.O., Agbaogun, B.K., Busari, H.K., Adejumo, A.L., Agbaje, W.B., Adeleke, A.E., and Samuel, A.O., 2024, Facile removal of rhodamine B and metronidazole with mesoporous biochar prepared from palm tree biomass: Adsorption studies, reusability, and mechanisms, Water Pract. Technol., 19 (3), 730–744.
DOI: https://doi.org/10.22146/ijc.96383
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