SavedAdd your journal

Journals / Avrupa Bilim ve Teknoloji Dergisi / 2026 / Sayı: 35

Heavy Metal Removal with ZnO-Chitosan Composite

ZnO-Kitosan Kompoziti ile Ağır Metal Giderimi

Gamze Topal Canbaz(Cumhuriyet Üniversitesi | Cumhuriyet University)0000-0001-7615-7627
Unsal Açıkel(SİVAS CUMHURİYET ÜNİVERSİTESİ)0000-0003-4969-8502
Yeşim Sağ Açıkel(HACETTEPE ÜNİVERSİTESİ)0000-0002-3026-0933
Pages
603–609
Publication Date
2022-05-07
🏛️Bibliographic metadata and full text access for this article are provided via DergiPark.
DergiPark Record ↗
✨

AI Summary & Key Takeaways

AI Insight
⚡ TL;DR(Too Long; Didn't Read)

In temperature studies, the decrease in adsorption capacity with increasing temperature showed that the system was exothermic.

📌 3 Key Takeaways

🎯
Objective & Hypothesis:In the study, ZnO particles were synthesized by green synthesis using Allium cepa (A. cepa) shells and the Nickel (II) (Ni (II)) removal potential of the ZnO-Ch composite formed with chitosan (Ch) was investigated.
📊
Key Findings & Data:In the study, pH (2,0-6,0), temperature (25-55 oC), amount of adsorbent (0,,25-1,0 g/L), contact time for Ni (II) adsorption in batch system with ZnO-Ch composite. (15-1440 min) and initial pollutant concentration (20-300 mg/L) were examined and optimum removal conditions were investigated.
💡
Conclusion & Impact:In temperature studies, the decrease in adsorption capacity with increasing temperature showed that the system was exothermic.
🔬Design:Modeling & Simulation
📍Scope:Comprehensive Sample
⚙️Variables:ZnO · kitosan · Ni(II)

Abstract

In the study, ZnO particles were synthesized by green synthesis using Allium cepa (A. cepa) shells and the Nickel (II) (Ni (II)) removal potential of the ZnO-Ch composite formed with chitosan (Ch) was investigated. Characterization of the synthesized ZnO-Ch composite was performed by scanning electron microscopy (SEM), Fourier transform infrared (FTIR) and X-ray diffraction (XRD). In the study, pH (2,0-6,0), temperature (25-55 oC), amount of adsorbent (0,,25-1,0 g/L), contact time for Ni (II) adsorption in batch system with ZnO-Ch composite. (15-1440 min) and initial pollutant concentration (20-300 mg/L) were examined and optimum removal conditions were investigated. The optimum conditions obtained were determined as pH 5,0, temperature 25 0C, amount of adsorbent 0,5 g/L, contact time 300 minutes (min). The maximum adsorption capacity of the composite in Ni (II) removal was calculated as 222,22 mg/g according to the Langmuir isotherm model. In temperature studies, the decrease in adsorption capacity with increasing temperature showed that the system was exothermic.

Özet

Çalışmada Allium cepa (A. cepa) kabukları kullanılarak yeşil sentez ile ZnO partikülleri sentezlendi ve kitosan (Ch) ile oluşturulan ZnO- Ch kompozitin Nikel (II) (Ni (II)) giderim potansiyeli incelendi. Sentezlenen ZnO-Ch kompozitin taramalı elektron mikroskopisi (SEM), Fourier transform infrared (FTIR) ve X-ışını difraksiyonu (XRD) ile karakterizasyonu gerçekleştirildi. Çalışmada ZnO-Ch kompoziti ile kesikli sistemde Ni (II) adsorpsiyonu için pH (2,0-6,0), sıcaklık (25-55 oC), adsorban miktarı (0,25-1,0 g/L),temas süresi (15-1440 dk) ve başlangıç kirletici derişimi (20-300 mg/L) incelenerek optimum giderim koşulları incelenmiştir. Elde edilen optium koşullar pH 5,0, sıcaklık 25 0C, adsorban miktarı 0,5 g/L, temas süresi 300 dakika (dk) olarak belirlenmiştir. Ni (II) gideriminde kompozitin maksimum adsorpsiyon kapasitesi Langmuir izoterm modeline göre 222,22 mg/g olarak hesaplandı. Yapılan sıcaklık çalışmalarında artan sıcaklık ile adsorpsiyon kapasitesinin düşmesi sistemin ekzotermik olduğunu gösterdi.

🔖

Cite This Article

Canbaz, G. T., Açıkel, U., Açıkel, Y. S. (2022). Heavy Metal Removal with ZnO-Chitosan Composite. Avrupa Bilim ve Teknoloji Dergisi, Sayı: 35, 603–609. https://doi.org/10.31590/ejosat.1094734

📄 Full Text PDF Viewer

📄

PDF görüntüleyici hazırlanıyor...

References (25)

  1. Dananjaya, S. H. S., Kumar, R. S., Yang, M., Nikapitiya, C., Lee, J., & De Zoysa, M. (2018). Synthesis, characterization of ZnO-chitosan nanocomposites and evaluation of its antifungal activity against pathogenic Candida albicans. International journal of biological macromolecules, 108, 1281-1288.
  2. Deliyanni, E. A., Lazaridis, N. K., Peleka, E. N., & Matis, K. A. (2004). Metals removal from aqueous solution by iron-based bonding agents. Environmental Science and Pollution Research, 11(1), 18-21.
  3. Liu, D., Sun, D., & Li, Y. (2010). Removal of Cu (II) and Cd (II) from aqueous solutions by polyaniline on sawdust. Separation Science and Technology, 46(2), 321-329.
  4. Liu, Z. R., & Zhou, S. Q. (2010). Adsorption of copper and nickel on Na-bentonite. Process safety and environmental protection, 88(1), 62-66.
  5. Nguyen, N. V., Jeong, J., & Lee, J. C. (2013). Removal of chromium (VI) from the leachate of electronic scrap using non‐ionic Amberlite XAD‐7HP resin. Journal of Chemical Technology & Biotechnology, 88(6), 1014-1022.
  6. Qiu, B., Xu, X. F., Deng, R. H., Xia, G. Q., Shang, X. F., & Zhou, P. H. (2019). Construction of chitosan/ZnO nanocomposite film by in situ precipitation. International journal of biological macromolecules, 122, 82-87.
  7. Queiroz, M. F., Teodosio Melo, K. R., Sabry, D. A., Sassaki, G. L., & Rocha, H. A. O. (2014). Does the use of chitosan contribute to oxalate kidney stone formation?. Marine drugs, 13(1), 141-158.
  8. Abdel-Ghani, N. T., El-Chaghaby, G. A., & Helal, F. S. (2015). Individual and competitive adsorption of phenol and nickel onto multiwalled carbon nanotubes. Journal of advanced research, 6(3), 405-415.
  9. Alabbad, E. A. (2021). Efficacy assessment of natural zeolite containing wastewater on the adsorption behaviour of Direct Yellow 50 from; equilibrium, kinetics and thermodynamic studies. Arabian Journal of Chemistry, 14(4), 103041.
  10. Barati, A., Asgari, M., Miri, T., & Eskandari, Z. (2013). Removal and recovery of copper and nickel ions from aqueous solution by poly (methacrylamide-co-acrylic acid)/montmorillonite nanocomposites. Environmental Science and Pollution Research, 20(9), 6242-6255.
  11. Barkat, M., Chegrouche, S., Mellah, A., Bensmain, B., Nibou, D., & Boufatit, M. (2014). Application of algerian bentonite in the removal of cadmium (II) and chromium (VI) from aqueous solutions. Journal of Surface Engineered Materials and Advanced Technology, 2014.
  12. Betiha, M. A., Moustafa, Y. M., Mansour, A. S., Rafik, E., & El-Shahat, M. F. (2020). Nontoxic polyvinylpyrrolidone-propylmethacrylate-silica nanocomposite for efficient adsorption of lead, copper, and nickel cations from contaminated wastewater. Journal of Molecular Liquids, 314, 113656.
  13. Boran, F. (2021). Encapsulation of CuO nanoparticles inside the channels of the multi-walled carbon nanotubes functionalized with thermal stress. Diamond and Related Materials, 114, 108306.
  14. Boran, F., TAŞKIRAN, İ., & Çetinkaya, S. (2019). Poli (sodyum 4-stiren sülfonat) Kaplı SnO2 Nanoparçacıklarının Sentezi, Karakterizasyonu ve Gaz Algılama Özelliklerinin İncelenmesi. Avrupa Bilim ve Teknoloji Dergisi, (17), 412-422.
  15. Chang, Y. S., Au, P. I., Mubarak, N. M., Khalid, M., Jagadish, P., Walvekar, R., & Abdullah, E. C. (2020). Adsorption of Cu (II) and Ni (II) ions from wastewater onto bentonite and bentonite/GO composite. Environmental Science and Pollution Research, 27(26), 33270-33296.
  16. Çınar, S., Kaynar, Ü. H., Aydemir, T., Kaynar, S. C., & Ayvacıklı, M. (2017). An efficient removal of RB5 from aqueous solution by adsorption onto nano-ZnO/Chitosan composite beads. International journal of biological macromolecules, 96, 459-465.
  17. Erdem, S., Öztekin, M., & Açıkel, Y. S. (2021). Investigation of tetracycline removal from aqueous solutions using halloysite/chitosan nanocomposites and halloysite nanotubes/alginate hydrogel beads. Environmental Nanotechnology, Monitoring & Management, 16, 100576.
  18. Gurel, L. (2010). senturk I, Bahadir T, Buyukgungor H (2010) Treatment of Nickel Plating Industrial Wastewater by Fungus Immobilized onto Rice Bran. J Microbial Biochem Technol, 2, 034-037.
  19. Gürel, L. (2017). Applications of the biosorption process for nickel removal from aqueous solutions–A review. Chemical Engineering Communications, 204(6), 711-722.
  20. Huang, C., Chung, Y. C., & Liou, M. R. (1996). Adsorption of Cu (II) and Ni (II) by pelletized biopolymer. Journal of Hazardous Materials, 45(2-3), 265-277.
  21. Nesakumar, N., Rayappan, J. B. B., Jeyaprakas, B. G., & Krishnan, U. M. (2012). Influence of pH on structural morphology of ZnO nanoparticle. Journal of Applied Sciences, 12(16), 1758-1761.
  22. Rajic, N., Stojakovic, D., Jovanovic, M., Logar, N. Z., Mazaj, M., & Kaucic, V. (2010). Removal of nickel (II) ions from aqueous solutions using the natural clinoptilolite and preparation of nano-NiO on the exhausted clinoptilolite. Applied Surface Science, 257(5), 1524-1532.
  23. Shamhari, N. M., Wee, B. S., Chin, S. F., & Kok, K. Y. (2018). Synthesis and characterization of zinc oxide nanoparticles with small particle size distribution. Acta Chimica Slovenica, 65(3), 578-585.
  24. Snell, F. D., & Snell, C. T. (1959). Colorimetric Methods of Ananysis: Including Photometric Methods by Forster Dee Snell. van Nostrand.
  25. Yedurkar, S., Maurya, C., & Mahanwar, P. (2016). Biosynthesis of zinc oxide nanoparticles using ixora coccinea leaf extract—a green approach. Open Journal of Synthesis Theory and Applications, 5(1), 1-14.