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Enhanced Cr (VI) Removal from Landfill Leachates using Nanoscale Zero-valent Iron

机译:使用纳米尺度零价铁,从垃圾填埋渗滤液中取出增强的Cr(vi)

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Nanoscale zero-valent iron modified by citric acid (m-NZVI) was used to remove hexavalent chromium (Cr (VI)) from landfill leachates. Citric acid was useful to enhance the dispersion of NZVI. The results demonstrated that the m-NZVI particles were uniform with a mean diameter of 45.6 nm and the specific surface area was about 22.8 m~2/g. The Cr (VI) removal rates increased as an increase of the dosage of m-NZVI and the temperature but decreased as an increase of pH and the initial concentration of HA. Cr (VI) adsorption kinetics followed a pseudo-first-order rate expression and the reaction rate constants ranged from 0.05 to 0.32 min~(-1). X-ray photoelectron spectroscope (XPS) analysis confirmed that the Fe(III)-critic acid and/or Cr(III)-HA compounds were formed on the m-NZVI surface, which could hinder the formation of Fe(III)-Cr(III) compounds. It was also shown that removing Cr (VI) by m-NZVI was a chemical controlled and irreversible process.
机译:通过柠檬酸(M-NZVI)改性的纳米级零价铁用于从垃圾填埋液中除去六价铬(Cr(vi))。柠檬酸可用于增强NZVI的分散体。结果表明,M-NZVI颗粒的平均直径为45.6nm,比表面积为约22.8m〜2 / g。 Cr(VI)去除率随着M-NZVI的剂量和温度的增加而增加,但随着pH的增加和HA的初始浓度而降低。 Cr(VI)吸附动力学遵循伪一阶率表达,反应速率常数范围为0.05至0.32分钟〜(-1)。 X射线光电子体分子(XPS)分析证实,在M-NZVI表面上形成Fe(III) - 克里酸和/或Cr(III)-HA化合物,其可能阻碍Fe(III)-CR的形成(iii)化合物。还表明,通过M-NZVI去除CR(VI)是一种化学控制和不可逆转的过程。

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