Abstract

The effectiveness of nanoscale zero-valent iron(nZVI) immobilized on activated carbon (nZVI/AC) in removing antimonite (Sb(III)) from simulated contaminated water was investigated with and without a magnetic fix-bed column reactor. The experiments were all conducted in fixed-bed columns. A weak magnetic field (WMF) was proposed to increase the exclusion of paramagnetic Sb(III) ions by nZVI/AC. The Sb(III) adsorption to the nZVI and AC surfaces, as well as the transformation of Sb(III) to Sb(V) by them, were both increased by using a WMF in nZVI/AC. The increased sequestration of Sb(III) by nZVI/AC in the presence of WMF was followed by faster nZVI corrosion and dissolution. Experiments were conducted as a function of the pH of the feed solution (pH 5.0–9.0), liquid flow rate (5–15 mL·min−1), starting Sb(III) concentration (0.5–1.5 mg·L−1), bed height nZVI/AC (10–40 cm), and starting Sb(III) concentration (0.5–1.5 mg·L−1). By analyzing the breakthrough curves generated by different flow rates, different pH values, different inlet Sb(III) concentrations, and different bed heights, the adsorbed amounts, equilibrium nZVI uptakes, and total Sb(III) removal percentage were calculated in relation to effluent volumes. At pH 5.0, the longest nZVI breakthrough time and maximal Sb(III) adsorption were achieved. The findings revealed that the column performed effectively at the lowest flow rate. With increasing bed height, column bed capacity and exhaustion time increased as well. Increasing the Sb(III) initial concentration from 0.5 to 1.5 mg·L−1 resulted in the rise of adsorption bed capacity from 3.45 to 6.33 mg·g−1.

Highlights

  • Antimony (Sb) is the ninth-largest mined metal and is used in a variety of industrial products [1]

  • Effect of Bed Height

  • Breakthrough curves for nZNI/AC produced by adjusting the bed heights of 10 to 40 cm with 1 mg·L−1 initial Sb(III) concentration at 10 mL·min−1 flow rate

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Summary

Introduction

Antimony (Sb) is the ninth-largest mined metal and is used in a variety of industrial products [1]. China produces over 88% of the world’s commercial antimony, and large quantities of antimony are discharged into the environment as a result of Sb smelting and mining processes, resulting in major contamination of soil and water. Concentrations of antimony up to 7.3–163.0 μg·L−1 have been found in natural waterways from the world’s largest Sb mine, Xikuangshan in Hunan Province, China [2]. Long-term exposure to high-level Sb-contaminated water has negative consequences that can lead to serious health problems. The most common environmental antimony species are Sb(III) and Sb(V), of which Sb(III) is 10 times more hazardous than Sb(V) [1]. The World Health Organization (WHO) and China have issued a standard for Sb in drinking water at 0.005 mg·L−1

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