Study on the adsorption performance of coal gangue-loaded nano-FeOOH for the removal of Pb<sup>2+</sup>, Cu<sup>2+</sup>, and Cd<sup>2+</sup> from acid mine drainage

In view of the serious pollution caused by heavy metals such as Pb<sup>2+</sup>, Cu<sup>2+</sup> and Cd<sup>2+</sup> present in acid mine drainage (AMD) and the difficulty in their treatment, based on the stable mineral skeleton structure of coal gangue and the good adsorption of nano-FeOOH, coal gangue-loaded nano-FeOOH (nFeOOH-CG) was successfully prepared <i>via</i> chemical precipitation. The effects of nFeOOH-CG on the removal of Pb<sup>2+</sup>, Cu<sup>2+</sup> and Cd<sup>2+</sup> from AMD were systematically investigated under different adsorbent dosage, initial pH, reaction time and initial concentration conditions. The adsorption mechanism of nFeOOH-CG was revealed using the adsorption isotherm, adsorption kinetics, adsorption thermodynamic model, SEM-EDS, XRD, TEM, FTIR spectroscopy and BET characterization. Results indicated that the rate of Pb<sup>2+</sup>, Cu<sup>2+</sup> and Cd<sup>2+</sup> removal by nFeOOH-CG reached 96.85%, 88.38% and 73.1%, respectively, under the conditions of 5 g per L dosage; pH 4; 150 min reaction time and 100 mg per L initial concentration of Pb<sup>2+</sup>, Cu<sup>2+</sup> and Cd<sup>2+</sup>, which were significantly better than those of unmodified coal gangue. The process of Pb<sup>2+</sup>, Cu<sup>2+</sup> and Cd<sup>2+</sup> adsorption by nFeOOH-CG conforms to the Langmuir and pseudo-second-order kinetic models, indicating that the adsorption mechanism mainly involves monolayer and chemical adsorption. The adsorption of Pb<sup>2+</sup> and Cu<sup>2+</sup> by nFeOOH-CG is a spontaneous, endothermic and entropy-increasing process, while the adsorption of Cd<sup>2+</sup> is a non-spontaneous, endothermic and entropy-increasing process. Characterization analysis showed that the specific surface area of nFeOOH-CG was 103.68 m<sup>2</sup> g<sup>-1</sup>, which was 13.22 times higher than that of coal gangue. The loading of nFeOOH significantly increased the specific surface area and surface active sites of coal gangue. The adsorption mechanism of nFeOOH-CG on Pb<sup>2+</sup>, Cu<sup>2+</sup> and Cd<sup>2+</sup> was mainly attributed to the increased specific surface area, surface complexation, electrostatic attraction and ion exchange. This study provides a theoretical basis and technical reference for the efficient resource utilization of coal gangue and the environmental remediation of AMD.

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Publication Details

Journal
RSC Advances
Published
2025-01-01
DOI
https://doi.org/10.1039/d5ra03306c
Citations
2
Primary Topic
Mine drainage and remediation techniques
Type
article
Field-Weighted Citation Impact
1.72

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article

Study on the adsorption performance of coal gangue-loaded nano-FeOOH for the removal of Pb2+, Cu2+, and Cd2+ from acid mine drainage

Xuying Guo, Yanrong Dong, Xiaoyue Zhang, Wei Sun et al.
2 citations
RSC Advances
Mine drainage and remediation techniques
1.72
article

Study on the adsorption performance of coal gangue-loaded nano-FeOOH for the removal of Pb2+, Cu2+, and Cd2+ from acid mine drainage

Xuying Guo, Yanrong Dong, Xiaoyue Zhang, Wei Sun, Fanbo Meng, Zilong Zhao, Honglei Fu
article en
2 citations

Abstract

In view of the serious pollution caused by heavy metals such as Pb<sup>2+</sup>, Cu<sup>2+</sup> and Cd<sup>2+</sup> present in acid mine drainage (AMD) and the difficulty in their treatment, based on the stable mineral skeleton structure of coal gangue and the good adsorption of nano-FeOOH, coal gangue-loaded nano-FeOOH (nFeOOH-CG) was successfully prepared <i>via</i> chemical precipitation. The effects of nFeOOH-CG on the removal of Pb<sup>2+</sup>, Cu<sup>2+</sup> and Cd<sup>2+</sup> from AMD were systematically investigated under different adsorbent dosage, initial pH, reaction time and initial concentration conditions. The adsorption mechanism of nFeOOH-CG was revealed using the adsorption isotherm, adsorption kinetics, adsorption thermodynamic model, SEM-EDS, XRD, TEM, FTIR spectroscopy and BET characterization. Results indicated that the rate of Pb<sup>2+</sup>, Cu<sup>2+</sup> and Cd<sup>2+</sup> removal by nFeOOH-CG reached 96.85%, 88.38% and 73.1%, respectively, under the conditions of 5 g per L dosage; pH 4; 150 min reaction time and 100 mg per L initial concentration of Pb<sup>2+</sup>, Cu<sup>2+</sup> and Cd<sup>2+</sup>, which were significantly better than those of unmodified coal gangue. The process of Pb<sup>2+</sup>, Cu<sup>2+</sup> and Cd<sup>2+</sup> adsorption by nFeOOH-CG conforms to the Langmuir and pseudo-second-order kinetic models, indicating that the adsorption mechanism mainly involves monolayer and chemical adsorption. The adsorption of Pb<sup>2+</sup> and Cu<sup>2+</sup> by nFeOOH-CG is a spontaneous, endothermic and entropy-increasing process, while the adsorption of Cd<sup>2+</sup> is a non-spontaneous, endothermic and entropy-increasing process. Characterization analysis showed that the specific surface area of nFeOOH-CG was 103.68 m<sup>2</sup> g<sup>-1</sup>, which was 13.22 times higher than that of coal gangue. The loading of nFeOOH significantly increased the specific surface area and surface active sites of coal gangue. The adsorption mechanism of nFeOOH-CG on Pb<sup>2+</sup>, Cu<sup>2+</sup> and Cd<sup>2+</sup> was mainly attributed to the increased specific surface area, surface complexation, electrostatic attraction and ion exchange. This study provides a theoretical basis and technical reference for the efficient resource utilization of coal gangue and the environmental remediation of AMD.

RSC AdvancesVol. 15(27)
Liaoning Technical University (CN)
National Natural Science Foundation of China, Department of Education of Liaoning Province, Department of Science and Technology of Liaoning Province
Clean water and sanitation
Openalex Percentile: Top 16%
Mine drainage and remediation techniques
1.72
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