The limitations of applying zero-valent iron technology in contaminants sequestration and the corresponding countermeasures: The development in zero-valent iron technology in the last two decades (1994-2014)

被引:796
作者
Guan, Xiaohong [1 ]
Sun, Yuankui [1 ]
Qin, Hejie [1 ]
Li, Jinxiang [1 ]
Lo, Irene M. C. [2 ]
He, Di [3 ]
Dong, Haoran [4 ]
机构
[1] Tongji Univ, Coll Environm Sci & Engn, State Key Lab Pollut Control & Resources Reuse, Shanghai 200092, Peoples R China
[2] Hong Kong Univ Sci & Technol, Dept Civil & Environm Engn, Hong Kong, Hong Kong, Peoples R China
[3] Univ New S Wales, Sch Civil & Environm Engn, Sydney, NSW 2052, Australia
[4] Hunan Univ, Coll Environm Sci & Engn, Key Lab Environm Biol & Pollut Control, Changsha 410082, Hunan, Peoples R China
基金
中国国家自然科学基金;
关键词
Mass transfer; Passive layer; pH; Iron oxides; Corrosion products; PERMEABLE REACTIVE BARRIER; LONG-TERM PERFORMANCE; IN-SITU REMEDIATION; WEAK MAGNETIC-FIELD; ENHANCED REDUCTIVE DEGRADATION; OXIDE-COATED SAND; ZEROVALENT IRON; NITRATE REDUCTION; ACTIVATED CARBON; CR(VI) REMOVAL;
D O I
10.1016/j.watres.2015.02.034
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Over the past 20 years, zero-valent iron (ZVI) has been extensively applied for the remediation/treatment of groundwater and wastewater contaminated with various organic and inorganic pollutants. Based on the intrinsic properties of ZVI and the reactions that occur in the process of contaminants sequestration by ZVI, this review summarizes the limitations of ZVI technology and the countermeasures developed in the past two decades (1994-2014). The major limitations of ZVI include low reactivity due to its intrinsic passive layer, narrow working pH, reactivity loss with time due to the precipitation of metal hydroxides and metal carbonates, low selectivity for the target contaminant especially under oxic conditions, limited efficacy for treatment of some refractory contaminants and passivity of ZVI arising from certain contaminants. The countermeasures can be divided into seven categories: pretreatment of pristine ZVI to remove passive layer, fabrication of nano-sized ZVI to increase the surface area, synthesis of ZVI-based bimetals taking advantage of the catalytic ability of the noble metal, employing physical methods to enhance the performance of ZVI, coupling ZVI with other adsorptive materials and chemically enhanced ZVI technology, as well as methods to recover the reactivity of aged ZVI. The key to improving the rate of contaminants removal by ZVI and broadening the applicable pH range is to enhance ZVI corrosion and to enhance the mass transfer of the reactants including oxygen and H+ to the ZVI surface. The characteristics of the ideal technology are proposed and the future research needs for ZVI technology are suggested accordingly. (C) 2015 Elsevier Ltd. All rights reserved.
引用
收藏
页码:224 / 248
页数:25
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