Preparation and investigation of M-MWCNT nanocomposite by hydrothermal method for Pb(II) ions adsorption

Document Type : Reasearch Paper

Authors

1 Department of Chemical Engineering, Neyshabur Branch, Islamic Azad University, Neyshabur, Iran.

2 Department of Chemistry, Neyshabur Branch, Islamic Azad University, Neyshabur, Iran.

3 Avdanced Research Center of Chemistry Biochemistry & Nanomaterial, Neyshabur Branch, Islamic Azad University, Neyshabur, Iran.

4 Department of Chemical Engineering, Quchan Branch, Islamic Azad University, Quchan, Iran.

5 New Materials Technology and Processing Research Center, Department of Chemistry, Neyshabur Branch,Islamic Azad University, Neyshabur, Iran.

6 Chemical Engineering Department, Hakim Sabzevari University, Sabzevar, Iran.

Abstract

In this present work, MWCNTs modified NiFe2O4 NPs (M-MWCNT) were successfully fabricated based on a hydrothermal route, and then utilized to Pb(II) sorption from an aqueous solution. The M-MWCNT was characterized and analyzed by SEM, TEM, FTIR, XRD, and VSM techniques. TEM image demonstrated that the size of NiFe2O4 nanoparticles in the structure of MWCNT was 20 nm. VSM results indicated that the M-MWCNT with saturation magnetization (Ms) value of  7 emu/g would have a fast magnetic response. According to X-ray data the average crystal sizes of the pure NiFe2O4 and M-MWCNT are 21.62 and 7.25 nm, respectively. The sorption kinetics, isotherms, thermodynamic and regeneration performance for lead ((Pb(II)) ions were evaluated. The M-MWCNT can effectively remove Pb(II) from aqueous solution at optimum pH of 5.5. Based on the Langmuir model, the maximum saturated adsorbed amount (qmax) of Pb(II) was up to 85.12 mg/g. The kinetic characteristic was appropriate for pseudo 1st order model expression, and the isothermal characteristic can be described via Longmuir model. The data obtained from the thermodynamic study show that the Pb(II) sorption using M-MWCNT nanocomposite was a spontaneous, exothermic and physisorption process with a good regeneration performance.

Keywords


[1] Abdollahi B., Salari D., Zarei M., (2022), Synthesis and characterization of magnetic Fe3O4@ SiO2-MIL-53 (Fe) metal-organic framework and its application for efficient removal of arsenate from surface and groundwater. J. Env. Chem. Eng. 10: 107144-107148.
[2] Kończyk J., Żarska S., Ciesielski W., (2019), Adsorptive removal of Pb (II) ions from aqueous solutions by multi-walled carbon nanotubes functionalised by selenophosphoryl groups: Kinetic, mechanism, and thermodynamic studies. Colloids and Surf. A: Physicochem. Eng. Asp. 575: 271-282.
[3] Awual M. R., Hasan M. M., Islam A., Rahman M. M., Asiri A. M., Khaleque M. A., Sheikh M. C., (2019), Offering an innovative composited material for effective lead (II) monitoring and removal from polluted water. J. Cleaner Prod. 231: 214-223.
[4] Abdel-Ghani N., Hefny M., El-Chaghaby G. A., (2007), Removal of lead from aqueous solution using low cost abundantly available adsorbents. Int. J. Env. Sci. Technol. 4: 67-73.
[5] Zhang K., Gao X., Zhang Q., Li T., Chen H., Chen X., (2017), Synthesis, characterization and electromagnetic wave absorption properties of asphalt carbon coated graphene/magnetic NiFe2O4 modified multi-wall carbon nanotube composites. J. Alloys & Comp. 721: 268-275.
[6] Zhao W., Tian Y., Chu X., Cui L., Zhang H., Li M., Zhao P., (2021), Preparation and characteristics of a magnetic carbon nanotube adsorbent: Its efficient adsorption and recoverable performances. Separ. Purif. Technol. 257: 117917-117921.
[7] Zhou L., Ji L., Ma P.-C., Shao Y., Zhang H., Gao W., Li Y., (2014), Development of carbon nanotubes/CoFe2O4 magnetic hybrid material for removal of tetrabromobisphenol A and Pb (II). J.  Hazard. Mater. 265: 104-114.
[8] Jiang R., Zhu H.-Y., Fu Y.-Q., Zong E.-M., Jiang S.-T., Li J.-B., Zhu J.-Q., Zhu Y.-Y., (2021), Magnetic NiFe2O4/MWCNTs functionalized cellulose bioadsorbent with enhanced adsorption property and rapid separation. Carbohyd. Polym. 252: 117158-117162.
[9] Luo X., Lei X., Cai N., Xie X., Xue Y., Yu F., (2016), Removal of heavy metal ions from water by magnetic cellulose-based beads with embedded chemically modified magnetite nanoparticles and activated carbon. ACS Sustain. Chem. Eng. 4: 3960-3969.
[10] Ren L., Lin H., Meng F., Zhang F., (2019), One-step solvothermal synthesis of Fe3O4@ Carbon composites and their application in removing of Cr (VI) and Congo red. Ceram. Int. 45: 9646-9652.
[11] Wang N., Ouyang X.-K., Yang L.-Y., Omer A. M., (2017), Fabrication of a magnetic cellulose nanocrystal/metal–organic framework composite for removal of Pb (II) from water. ACS Sustain. Chem. Eng. 5: 10447-10458.
[12] Aslibeiki B., Eskandarzadeh N., Jalili H., Varzaneh A. G., Kameli P., Orue I., Chernenko V., Hajalilou A., Ferreira L., Cruz M., (2022), Magnetic hyperthermia properties of CoFe2O4 nanoparticles: Effect of polymer coating and interparticle interactions. Ceram. Int. In Press.
[13] Hakimyfard A., Khademinia S., (2022), Hirshfeld surface analysis of solid-state synthesized NiFe2O4 nanocomposite and application of it for photocatalytic degradation of Water pollutant dye. Int. J. Nano Dimens. 13: 155-167.
[14] Bagheri Gh. A., Ashayeri V., Mahanpoor K., (2013), Photocatalytic efficiency of CuFe2O4 for photodegradation of acid red 206. Int. J. Nano Dimens. 4: 111-115.
[15] Abideen Idowu A., Sarafadeen Olateju K., Oluwatobi Samson A., (2019), Synthesis of MnFe2O4 nanoparticles for adsorption of digestive enzymes: Kinetics, isothermal and thermodynamics studies. Int. J. Nano Dimens. 10: 330-339.
[16] Ensafi A. A., Allafchian A. R., Rezaei B., Mohammadzadeh R., (2013), Characterization of carbon nanotubes decorated with NiFe2O4 magnetic nanoparticles as a novel electrochemical sensor: Application for highly selective determination of sotalol using voltammetry. Mater. Sci. Eng.: C. 33: 202-208.
[17] Kafshgari L. A., Ghorbani M., Azizi A., (2017), Fabrication and investigation of MnFe2O4/MWCNTs nanocomposite by hydrothermal technique and adsorption of cationic and anionic dyes. Appl. Surf. Sci. 419: 70-83.
[18] Foroutan R., Peighambardoust S. J., Esvandi Z., Khatooni H., Ramavandi B., (2021), Evaluation of two cationic dyes removal from aqueous environments using CNT/MgO/CuFe2O4 magnetic composite powder: A comparative study. J. Env. Chem. Eng. 9: 104752-104757.
[19] Sadegh H. R., Shahriary Ghoshehkandi R., Masjedi A., Mahmoodi Z., Kazemi M., (2016), A review on Carbon nanotubes adsorbents for the removal of pollutants from aqueous solutions. Int. J. Nano Dimens. 7: 109-120.
[20] Hazarika M., Chinnamuthu P., Borah J., (2022), Enhanced photocatalytic efficiency of MWCNT/NiFe2O4 nanocomposites. Phys. E: Low-dimens. Sys. Nanostruc. 139: 115177-115182.
[21] Forghani M., Azizi A., Livani M. J., Kafshgari L. A., (2020), Adsorption of lead (II) and chromium (VI) from aqueous environment onto metal-organic framework MIL-100 (Fe): Synthesis, kinetics, equilibrium and thermodynamics. J. Solid State Chem. 291: 121636-121641.
[22] Powell K. J., Brown P. L., Byrne R. H., Gajda T., Hefter G., Leuz A.-K., Sjöberg S., Wanner H., (2009), Chemical speciation of environmentally significant metals with inorganic ligands. Part 3: The Pb2+ , OH, Cl, CO32–, SO42–, and PO43–systems (IUPAC Technical Report). Pure and Appl. Chem. 81: 2425-2476.
[23] Sylva R. N., Brown P. L., (1980), The hydrolysis of metal ions. Part 3. Lead (II). J. Chem. Soc. Dalton Transactions. 1577-1581.
[24] Breza M., Manová A., (2002), On the structure of Lead (II) complexes in aqueous solutions. III. Hexanuclear clusters. Collec. Czechoslovak Chem. Communic. 67: 219-227.
[25] Lian Q., Ahmad Z. U., Gang D. D., Zappi M. E., Fortela D. L. B., Hernandez R., (2020), The effects of carbon disulfide driven functionalization on graphene oxide for enhanced Pb (II) adsorption: Investigation of adsorption mechanism. Chemosphere. 248: 126078-126082.
[26] Mondal S. K., Welz A., Rezaei F., Kumar A., Okoronkwo M. U., (2020), Structure–property relationship of geopolymers for aqueous Pb removal. ACS Omega. 5: 21689-21699.
[27] Das A., Bar N., Das S., (2022), Adsorptive removal of Pb (II) ion on arachis hypogaea’s shell: Batch experiments, statistical, and GA modeling. Int. J. Env. Sci. Technol. 1-14.
[28] Yu X., Wang D., Yuan B., Song L., Hu Y., (2016), The effect of carbon nanotubes/NiFe2O4 on the thermal stability, combustion behavior and mechanical properties of unsaturated polyester resin. RSC Adv. 6: 96974-96983.
[29] Qu G., Zhou J., Liang S., Li Y., Ning P., Pan K., Ji W., Tang H., (2022), Thiol-functionalized multi-walled carbon nanotubes for effective removal of Pb (II) from aqueous solutions. Mater. Chem. Phys. 278: 125688-125692.
[30] Neolaka Y. A., Lawa Y., Naat J., Riwu A. A., Darmokoesoemo H., Widyaningrum B. A., Iqbal M., Kusuma H. S., (2021), Indonesian kesambi wood (Schleichera oleosa) activated with pyrolysis and H2SO4 combination methods to produce mesoporous activated carbon for Pb(II) adsorption from aqueous solution. Env. Technol. Innovat. 24: 101997-102002.
[31] Eletta O. A., Ayandele F. O., Ighalo J. O., (2021), Adsorption of Pb(II) and Fe(II) by mesoporous composite activated carbon from Tithonia diversifolia stalk and Theobroma cacao pod. Biomass Convers. Bioref. 1-10.
[32] Fu C., Zhu X., Dong X., Zhao P., Wang Z., (2021), Study of adsorption property and mechanism of lead (II) and cadmium (II) onto sulfhydryl modified attapulgite. Arab. J. Chem. 14: 102960-102966.
[33] Yan S., Ren X., Zhang F., Huang K., Feng X., Xing P., (2022), Comparative study of Pb2+, Ni2+, and methylene blue adsorption on spherical waste solid-based geopolymer adsorbents enhanced with carbon nanotubes. Separ. Purif. Technol. 284: 120234-120239.