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      Almond Shell-Derived, Biochar-Supported, Nano-Zero-Valent Iron Composite for Aqueous Hexavalent Chromium Removal: Performance and Mechanisms

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          Abstract

          Nano-zero-valent iron biochar derived from almond shell (nZVI-ASBC) was used for hexavalent chromium (CR) removal. Experiments showed that pH was the main factor ( p < 0.01) that affected the experimental results. At a dosage of 10 mg·L −1 and pH of 2–6, in the first 60 min, nZVI-ASBC exhibited a removal efficiency of 99.8%, which was approximately 20% higher than the removal yield at pH 7–11. Fourier transform infrared spectroscopy results indicated N-H was the main functional group that influenced the chemisorption process. The pseudo second-order dynamics and Langmuir isotherm models proved to be the most suitable. Thermodynamic studies showed that the reaction was exothermic and spontaneous at low temperatures (T < 317 K). Various interaction mechanisms, including adsorption and reduction, were adopted for the removal of Cr(VI) using the nZVI-ASBC composite. The findings showed that the BC-modified nZVI prepared with almond shell exerts a good effect and could be used for the removal of Cr(VI).

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          Stabilization of nanoscale zero-valent iron (nZVI) with modified biochar for Cr(VI) removal from aqueous solution.

          Three types of modified biochar (BC) were produced respectively with acid (HCl) treatment (HCl-BC), base (KOH) treatment (KOH-BC) and oxidation (H2O2) treatment (H2O2-BC) of raw biochar. Both the raw biochar and modified biochars supported zero valent iron nanopartilces (nZVI) (i.e. nZVI@BC, nZVI@HCl-BC, nZVI@KOH-BC and nZVI@H2O2-BC) were synthesized and their capacities for Cr(VI) removal were compared. The results showed that the nZVI@HCl-BC exhibited the best performance and the underlying mechanisms were discussed. The surface elemental distribution maps of the nZVI@HCl-BC after reaction with Cr(VI) showed that Fe, Cr and O elements were deposited on the surface of HCl-BC evenly, indicating that the formed Cr(III)/Fe(III) could settle on the surface of HCl-BC uniformly rather than coated only on the nZVI surface. This reveals that the supporter HCl-BC could also play a role in alleviating the passivation of nZVI. Besides, the effects of mass ratio (nZVI/HCl-BC), pH, and initial Cr(VI) concentration on Cr(VI) removal were examined. At lower mass of HCl-BC, nZVI aggregation cannot be fully inhibited on the surface of HCl-BC, whereas excessive biochar can block the active sites of nZVI. Additionally, it was found that Cr(VI) removal by nZVI@HCl-BC was dependent on both pH and initial Cr(VI) concentration.
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            Biochar supported nanoscale zerovalent iron composite used as persulfate activator for removing trichloroethylene.

            Biochar (BC) supported nanoscale zerovalent iron (nZVI) composite was synthesized and used as an activator for persulfate to enhance the trichloroethylene (TCE) removal in aqueous solutions. The degradation efficiency of TCE (0.15mmolL(-1)) was 99.4% in the presence of nZVI/BC (4.5mmolL(-1), nZVI to BC mass ratio was 1:5) and persulfate (4.5mmolL(-1)) within 5min, which was significantly higher than that (56.6%) in nZVI-persulfate system under the same conditions. Owing to large specific surface area and oxygen-containing functional groups of BC, nZVI/BC enhanced the SO4(-) generation and accelerated TCE degradation. On the basis of the characterization and analysis data, possible activation mechanisms of the Fe(2+)/Fe(3+) (Fe(II)/Fe(III)) redox action and the electron-transfer mediator of the BC oxygen functional groups promoting the generation of SO4(-) in nZVI/BC-persulfate system were clarified.
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              Recent bioreduction of hexavalent chromium in wastewater treatment: A review

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                Author and article information

                Journal
                Nanomaterials (Basel)
                Nanomaterials (Basel)
                nanomaterials
                Nanomaterials
                MDPI
                2079-4991
                23 January 2020
                February 2020
                : 10
                : 2
                : 198
                Affiliations
                [1 ]School of Urban Construction, Wuhan University of Science and Technology, Wuhan 430065, China; yaorongshuwust@ 123456126.com (Y.S.); binji@ 123456wust.edu.cn (B.J.); yutingshiwust@ 123456126.com (Y.S.); okwj@ 123456wust.edu.cn (J.W.)
                [2 ]Guangdong Institute of Resources Comprehensive Utilization, Guangzhou 510650, China
                [3 ]Guangdong Provincial Key Laboratory of Development and Comprehensive Utilization of Mineral Resources, Guangzhou 510650, China
                [4 ]Institute of Hydrobiology, Chinese Academy of Sciences, Wuhan 430072, China; cuibaihui@ 123456ihb.ac.cn
                [5 ]College of Environment, Zhejiang University of Technology, Hanzhoug 310014, China; mianhu@ 123456zjut.edu.cn
                [6 ]School of Environmental and Municipal Engineering, Qingdao University of Technology, Qingdao 266033, China; luosiyi666@ 123456126.com
                [7 ]School of Environmental Science and Engineering, Huazhong University of Science and Technology, Wuhan 430074, China
                Author notes
                [* ]Correspondence: dabin@ 123456hust.edu.com
                Article
                nanomaterials-10-00198
                10.3390/nano10020198
                7074915
                31979270
                0f4e66bc-4f95-4484-9d28-e761bbcb6265
                © 2020 by the authors.

                Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license ( http://creativecommons.org/licenses/by/4.0/).

                History
                : 14 December 2019
                : 21 January 2020
                Categories
                Article

                biochar,nzvi,cr(vi),orthogonal experiment,adsorption
                biochar, nzvi, cr(vi), orthogonal experiment, adsorption

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