4.6 Article

Preparation and optimization of a low-cost adsorbent for heavy metal ions from red mud using fraction factorial design and Box-Behnken response methodology

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ELSEVIER
DOI: 10.1016/j.colsurfa.2021.127198

关键词

Red mud; Adsorbent; Preparation condition; Heavy metal ions; Fraction factorial design; Response surface methodology

资金

  1. School of Minerals Processing and Bioengineering, Central South University
  2. National Key Research and Development Program of China [2018YFC1901901]

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The utilization of red mud (RM) to prepare an adsorbent for heavy metal ions has attracted attention. By activating RM with Ca2+ and Mg2+ mixed solution neutralization and high-temperature treatment, a low-cost adsorbent was successfully prepared. The adsorbent displayed high adsorption capacity for Pb(II) and Zn(II) in liquid, making it a promising material for removing heavy metal ions from contaminated water.
Red mud (RM) is a solid waste generated from the alumina refining industry. The utilization of RM to prepare sorbent has attracted researchers' attention. This study aimed to prepare a low-cost adsorbent for heavy metal ions by activating RM using Ca2+ and Mg2+ mixed solution neutralization and high-temperature treatment. Pb (II) and Zn(II) were selected as target contaminants to investigate the possibility of this adsorbent to remove heavy metal ions from the liquid. The Fractional Factorial Design and Box-Behnken design were used to screen the significant preparation parameters and obtain the optimum preparation conditions. The results demonstrated that neutralization time, calcination temperature, and calcination time were determined as significant factors affecting the adsorption capacity of Pb(II) and Zn(II), and the optimum preparation parameters were the solution concentration of 1.5 mol/L, the liquid-solid ratio of 40 ml/g, the neutralization time of 114 min, calcination temperature of 518 degrees C, and the calcination time of 148 min. The physicochemical characterizations of neutralization-calcination RM (NCRM) were determined by X-ray diffraction (XRD), Fourier transform infrared (FTIR), scanning electron microscopy (SEM), and N-2 adsorption isotherm analysis. The results revealed that the main mineral phase of NCRM was hematite, calcite, and cancrinite, and NCRM had a loose structure and abundant pores, which contributes to the sorption of heavy metal ions. The adsorption kinetics study referred to satisfactory adsorption of Pb(II) via pseudo-first-order model and pseudo-second-order model, while pseudosecond-order model was the best model to describe adsorption of Zn(II) onto NCRM. Based on the batch experiment, the maximum adsorption capacities of Pb(II) and Zn(II) were 218.82 and75.58 mg/g, respectively. The excellent adsorption performance of NCRM on Pb(II) and Zn(II) implies that this material is a promising material for removing heavy metal ions from contaminated water.

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