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Removal of hexavalent chromium by biochar supported nZVI composite: Batch and fixed-bed column evaluations, mechanisms, and secondary contamination prevention

机译:通过生物炭支持的nZVI复合材料去除六价铬:分批和固定床色谱柱评估,机理和二次污染预防

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Conversion of carcinogenic Cr(VI) to less toxic Cr(III) has long been regarded as the most efficient and effective method to remediate Cr(VI)-contaminated water. However, the widely used reducing agents such as nano zero-valent iron (nZVI) and its derivatives often have low stability and their applications in water treatment may introduce secondary contaminations. To shed light on these, nZVI was loaded on sludge derived biochar to produce nZVI-BC composite for Cr(VI) removal. Batch experiments showed that Cr(VI) adsorption on nZVI-BC was endothermic and highly pH dependent. The adsorption kinetic and isotherm data were described by the pseudo second-order kinetic model and the Langmuir isotherm model, respectively. The removal of Cr(VI) by nZVI-BC was mainly through reduction-adsorption. After the experiment, nZVI-BC was transformed into a stable magnetic adsorbent that can be magnetically separated from aqueous phase during first circle application. In fix-bed columns, nZVI-BC also effectively removed Cr(VI) under various operation conditions and the Thomas and Yoon-Nelson models described the experimental breakthrough curves well. The post-adsorption nZVI-BC was re-pyrolyzed, which stabilized and reduced the bioavailability of Cr in the biochar. Re-pyrolysis thus can be used as an effective technology to reduce the environmental risks of post-adsorbent biochar for safe disposal. (C) 2018 Elsevier Ltd. All rights reserved.
机译:长期以来,将致癌性六价铬转化为毒性较小的三价铬是补救污染六价铬水的最有效方法。但是,广泛使用的还原剂,例如纳米零价铁(nZVI)及其衍生物通常具有较低的稳定性,它们在水处理中的应用可能会引入二次污染。为了阐明这些,将nZVI加载到污泥衍生的生物炭上,以生产用于去除Cr(VI)的nZVI-BC复合材料。批处理实验表明,Cr(VI)在nZVI-BC上的吸附是吸热的,并且对pH的依赖性很高。吸附动力学和等温线数据分别用伪二级动力学模型和Langmuir等温线模型描述。 nZVI-BC去除Cr(VI)主要是通过还原吸附。实验后,将nZVI-BC转化为稳定的磁性吸附剂,该吸附剂可在第一圈施加过程中与水相磁性分离。在固定床色谱柱中,nZVI-BC还可以在各种操作条件下有效去除Cr(VI),Thomas和Yoon-Nelson模型很好地描述了实验突破曲线。吸附后的nZVI-BC被重新热解,从而稳定并降低了生物炭中Cr的生物利用度。因此,再热解可以用作减少吸附后生物炭安全处理的环境风险的有效技术。 (C)2018 Elsevier Ltd.保留所有权利。

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