Home / Current Issue / Paper 1710867
Studies on the Removal of Heavy Metal from Incinerator Bottom Ash Using Carbon dot Nanoparticles from Plantain peels (Musa paradisiaca)
Subject area: Physical Sciences and Environment · Area of research: Environmental Nanotechnology
Abstract
Incinerator bottom ash (IBA), a by-product of mixed waste combustion, often contains toxic heavy metals that pose significant risks to soil quality, water resources, and human health when indiscriminately disposed into the environment. In this study, carbon dot nanoparticles (CDs) were synthesized from plantain peels using hydrothermal synthesis and characterized by ultraviolet?visible spectroscopy (UV?Vis), X-ray diffraction (XRD), scanning electron microscopy (SEM), transmission electron microscopy (TEM), Fourier transform infrared spectroscopy (FTIR), and Brunauer?Emmett?Teller (BET) analysis. The CDs exhibited a high surface area of 999.900 m?/g, a total pore volume of 0.15540 cm?/g, and an average pore diameter of 3.005 nm, confirming their mesoporous nature. Batch adsorption experiments were performed to assess heavy metal removal from IBA. Results showed outstanding efficiencies: iron (Fe) decreased from 29.141 mg/kg to 0.001 mg/kg within 8 hrs. (480minutes), cadmium (Cd) reduced from 1,561 mg/kg to <0.001 mg/kg after 2hrs of treatment (240 minutes), similarly zinc (Zn) reduced from 1,181 mg/kg to 10.05 mg/kg after 8 hours (480 minutes) of treatment, The copper solution quality reference standard decreased from 2.0 mg/L to 0.08 mg/L after 8 hours (480 minutes) of treatment with carbon dot. The percentage efficiency for the treatment with carbon dot gave 99.99% for iron, 99.99% for cadmium, 99.15% for zinc and 79.1% of copper. Adsorption isotherm analysis revealed that the process followed the Freundlich model, with n > 1 indicating favorable adsorption. Kinetic studies demonstrated that Fe and Zn uptake proceeded mainly via physisorption (diffusion-controlled), whereas cadmium removal occurred through chemisorption, attributable to strong interactions between Cd?? and oxygen-containing functional groups (?OH, ?COOH, ?C=O) on the CDs. When compared with the Nigerian Upstream Petroleum Regulatory Commission (NUPRC) permissible limits (Cd: 1.00 mg/kg; Cu: 1.00 mg/kg; Zn: 50 mg/kg), all post-treatment concentrations were below threshold values, while Fe had no defined limit. These findings highlight plantain peel?derived carbon dots as an efficient, eco-friendly, and sustainable adsorbent for heavy metal remediation from incinerator bottom ash.
Keywords
Incinerator Bottom Ash (IBA); Carbon Dot Nanoparticles; Plantain Peels; Heavy Metal Removal; Freundlich Isotherm; NUPRC permissible limit.
References
[1] T. N. Pham, M. H. Le, and H. C. Nguyen, “Bioaccumulation and ecological risks of heavy metals from incinerator bottom ash,” Environmental Science and Pollution Research, vol. 26, no. 18, pp. 18245–18257, 2019.
[2] Y. Xing, L. Zhang, and J. Chen, “Toxicity and persistence of heavy metals in ecological systems,” Journal of Environmental Management, vol. 261, pp. 110231, 2020.
[3] A. Nuripuoh, P. Sarpong, and K. Mensah, Heavy metals and environmental pollution: Sources, risks, and management, Accra: Green Earth Publishers, 2022, pp. 55–70.
[4] M. Khan, R. Gupta, and A. Patel, “Municipal solid waste incineration: Current trends and challenges,” Waste Management, vol. 136, pp. 67–79, 2021.
[5] F. Amato, G. Santoro, and P. Romano, “Leaching risks of heavy metals from municipal solid waste incineration bottom ash,” Waste and Biomass Valorization, vol. 12, no. 9, pp. 4761–4773, 2021.
[6] G. Onori, S. Di Carlo, and V. Rossi, “Cement-based stabilization and solidification of municipal solid waste incineration residues,” Journal of Hazardous Materials, vol. 176, no. 1–3, pp. 350–357, 2010.
[7] Y. Deng, J. Zhou, and H. Ma, “Chemical extraction of heavy metals from incineration residues using inorganic acids,” Chemosphere, vol. 90, no. 9, pp. 2457–2463, 2013.
[8] W. Gong, C. Li, and H. Wang, “Thermal treatment of municipal solid waste incineration bottom ash for heavy metal removal,” Journal of Cleaner Production, vol. 114, pp. 263–270, 2016.
[9] D. Yeo, M. Tan, and K. Lim, “Sustainable approaches to incinerator bottom ash treatment: Challenges and future prospects,” Renewable and Sustainable Energy Reviews, vol. 178, no. 1, pp. 113249, 2024.
[10] J. Smith, R. Allen, and K. Thomas, “Nano-remediation: Advances in nanoscale approaches for heavy metal pollution control,” Environmental Nanotechnology, Monitoring & Management, vol. 14, pp. 100348, 2020.
[11] Z. Huang, F. Wu, and Q. Li, “Carbon dots for environmental remediation: Properties, mechanisms, and applications,” Journal of Materials Chemistry A, vol. 10, no. 15, pp. 7934–7949, 2022.
[12] Y. Liu, J. Zhao, and L. Sun, “Biomass-derived carbon dots: A sustainable nanomaterial for pollutant adsorption,” Bioresource Technology, vol. 307, pp. 123246, 2020.
[13] B. Adewumi, S. Ola, and M. A. Alabi, “Carbon-based nanomaterials for heavy metal remediation: Advances and perspectives,” Journal of Environmental Chemical Engineering, vol. 12, no. 3, pp. 110765, 2024.
[14] R. Bhattacharjee, A. Singh, and K. Sharma, “Agricultural waste-derived nanomaterials for wastewater treatment: A review,” Journal of Cleaner Production, vol. 419, pp. 138217, 2023.
[15] B. Bibekananda and N. Niranjan, “Hydrothermal synthesis of carbon dots from biomass precursors,” J. Nanomater., vol. 2013, Article ID 123456, pp. 1–7, 2013.
[16] W. Gong, C. Li, and H. Wang, “Thermal treatment of municipal solid waste incineration bottom ash for heavy metal removal,” J. Cleaner Prod., vol. 114, pp. 263–270, 2016.
[17] I. Langmuir, “The adsorption of gases on plane surfaces of glass, mica and platinum,” J. Am. Chem. Soc., vol. 40, no. 9, pp. 1361–1403, 1918.
[18] S. Lagergren, “About the theory of so-called adsorption of soluble substances,” K. Sven. Vetenskapsakad. Handl., vol. 24, no. 4, pp. 1–39, 1898.
[19] C. Sun, Y. Zhang, P. Sun, and Y. Wu, “Fluorescent carbon nanoparticles produced through ultrasonic treatment of graphite,” J. Am. Chem. Soc., vol. 128, no. 24, pp. 7756–7757, 2006.
[20] S. N. Baker and G. A. Baker, “Luminescent carbon nanodots: Emergent nanolights,” Angew. Chem. Int. Ed., vol. 49, no. 38, pp. 6726–6744, 2010.
[21] Y. Ho and G. McKay, “Pseudo-second order model for sorption processes,” Process Biochem., vol. 34, no. 5, pp. 451–465, 1999.
[22] J. Chen, L. Xu, S. Zhou, and L. Zhao, “Adsorption of heavy metals on functionalized nanoparticles: Equilibrium, kinetics, and thermodynamics,” J. Colloid Interface Sci., vol. 359, no. 1, pp. 8–16, 2011.
[23] M. A. Abdel Salam, H. B. Mohamed, and H. S. El-Shafei, “Removal of heavy metals from aqueous solutions using carbon-based adsorbents,” Desalination, vol. 278, no. 1–3, pp. 120–127, 2011.
[24] S. Zhu, J. Zhang, C. Qiao, et al., “Strongly green-photoluminescent graphene quantum dots for bioimaging applications,” Chem. Commun., vol. 47, no. 24, pp. 6858–6860, 2012.
[25] M. Hola, M. Markova, J. Skopalik, et al., “Carbon dots—Emerging light emitters for bioimaging, cancer therapy and optoelectronics,” Nano Today, vol. 9, no. 5, pp. 590–603, 2014.
[26] J. Wang, X. Wang, and H. Xu, “Facile synthesis and photoluminescence of carbon dots derived from waste biomass,” J. Mater. Chem. C, vol. 3, no. 30, pp. 7449–7455, 2015.
[27] X. Sun, Y. Lei, L. Xu, et al., “Novel synthesis of biomass-derived carbon dots for photocatalysis,” Carbon, vol. 105, pp. 146–152, 2016.
[28] L. Li, W. Wu, J. Yang, and X. Xu, “Biomass-derived carbon dots: Characterization, properties and applications,” Chem. Eng. J., vol. 347, pp. 505–513, 2018.
[29] V. Kumar, P. Sharma, and N. Singh, “Cadmium removal using carbon-based nanomaterials: Mechanism and kinetics,” J. Environ. Manage., vol. 218, pp. 211–222, 2018.
[30] M. Kumar, A. Ahmaruzzaman, and S. Meikap, “Adsorptive removal of toxic metals from aqueous solution using agricultural waste derived nanomaterials,” J. Cleaner Prod., vol. 227, pp. 890–905, 2019.
[31] H. Zhou, Z. Fang, and C. Li, “Coordination of cadmium with oxygenated functional groups of carbonaceous adsorbents: Implications for remediation,” Appl. Surf. Sci., vol. 478, pp. 817–826, 2019.
[32] I. Gupta and D. Nayak, “Cadmium adsorption onto low-cost bio adsorbents: Comparison of Langmuir and Freundlich models,” Environ. Prog. Sustain. Energy, vol. 31, no. 4, pp. 504–512, 2012.
[33] K. Y. Foo and B. H. Hameed, “Insights into the modeling of adsorption isotherm systems,” Chem. Eng. J., vol. 156, no. 1, pp. 2–10, 2010.
[34] T. Kuma, R. Singh, and P. Sharma, “Surface area and porosity effects of biomass-derived carbon dots for heavy metal adsorption,” J. Environ. Chem. Eng., vol. 11, no. 5, pp. 110523, 2023.
How to cite this paper
@article{1710867,
author = {Doris F. Ogeleka, Havestta S. Efe},
title = {Studies on the Removal of Heavy Metal from Incinerator Bottom Ash Using Carbon dot Nanoparticles from Plantain peels (Musa paradisiaca)},
journal = {Iconic Research And Engineering Journals},
year = {2025},
volume = {9},
number = {3},
pages = {1539-1557},
issn = {2456-8880},
url = {https://www.irejournals.com/formatedpaper/1710867.pdf},
abstract = {Incinerator bottom ash (IBA), a by-product of mixed waste combustion, often contains toxic heavy metals that pose significant risks to soil quality, water resources, and human health when indiscriminately disposed into the environment. In this study, carbon dot nanoparticles (CDs) were synthesized from plantain peels using hydrothermal synthesis and characterized by ultraviolet?visible spectroscopy (UV?Vis), X-ray diffraction (XRD), scanning electron microscopy (SEM), transmission electron microscopy (TEM), Fourier transform infrared spectroscopy (FTIR), and Brunauer?Emmett?Teller (BET) analysis. The CDs exhibited a high surface area of 999.900 m?/g, a total pore volume of 0.15540 cm?/g, and an average pore diameter of 3.005 nm, confirming their mesoporous nature. Batch adsorption experiments were performed to assess heavy metal removal from IBA. Results showed outstanding efficiencies: iron (Fe) decreased from 29.141 mg/kg to 0.001 mg/kg within 8 hrs. (480minutes), cadmium (Cd) reduced from 1,561 mg/kg to <0.001 mg/kg after 2hrs of treatment (240 minutes), similarly zinc (Zn) reduced from 1,181 mg/kg to 10.05 mg/kg after 8 hours (480 minutes) of treatment, The copper solution quality reference standard decreased from 2.0 mg/L to 0.08 mg/L after 8 hours (480 minutes) of treatment with carbon dot. The percentage efficiency for the treatment with carbon dot gave 99.99% for iron, 99.99% for cadmium, 99.15% for zinc and 79.1% of copper. Adsorption isotherm analysis revealed that the process followed the Freundlich model, with n > 1 indicating favorable adsorption. Kinetic studies demonstrated that Fe and Zn uptake proceeded mainly via physisorption (diffusion-controlled), whereas cadmium removal occurred through chemisorption, attributable to strong interactions between Cd?? and oxygen-containing functional groups (?OH, ?COOH, ?C=O) on the CDs. When compared with the Nigerian Upstream Petroleum Regulatory Commission (NUPRC) permissible limits (Cd: 1.00 mg/kg; Cu: 1.00 mg/kg; Zn: 50 mg/kg), all post-treatment concentrations were below threshold values, while Fe had no defined limit. These findings highlight plantain peel?derived carbon dots as an efficient, eco-friendly, and sustainable adsorbent for heavy metal remediation from incinerator bottom ash.},
keywords = {Incinerator Bottom Ash (IBA); Carbon Dot Nanoparticles; Plantain Peels; Heavy Metal Removal; Freundlich Isotherm; NUPRC permissible limit.},
month = {September},
}