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Transport of surface-modified iron nanoparticle in porous media and application to arsenic(III) remediation

机译:表面修饰的铁纳米颗粒在多孔介质中的运输及其在砷(III)修复中的应用

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The surface-modified iron nanoparticles (S-INP) were synthesized, characterized and tested for the remediation of arsenite (As(III)), a well known toxic groundwater contaminant of concern. The S-INP material was fully dispersed in the aqueous phase with a particle size distribution of 2–10 nm estimated from high-resolution transmission electron microscopy (HR-TEM). X-ray photoelectron spectroscopy (XPS) revealed that an Fe(III) oxide surface film was present on S-INP in addition to the bulk zero-valent Fe0 oxidation state. Transport of S-INP through porous media packed in 10 cm length column showed particle breakthroughs of 22.1, 47.4 and 60 pore volumes in glass beads, unbaked sand, and baked sand, respectively. Un-modified INP was immobile and aggregated on porous media surfaces in the column inlet area. Results using S-INP pretreated 10 cm sand-packed columns containing ~2 g of S-INP showed that 100 % of As(III) was removed from influent solutions (flow rate 1.8 mL min?1) containing 0.2, 0.5 and 1.0 mg L?1 As(III) for 9, 7 and 4 days providing 23.3, 20.7 and 10.4 L of arsenic free water, respectively. In addition, it was found that 100% of As(III) in 0.5 mg/L solution (flow rate 1.8 mL min?1) was removed by S-INP pretreated 50 cm sand packed column containing 12 g of S-INP for more than 2.5 months providing 194.4 L of arsenic free water. Field emission scanning electron microscopy (FE-SEM) showed S-INP had transformed to elongated, rod-like shaped corrosion product particles after reaction with As(III) in the presence of sand. These results suggest that S-INP has great potential to be used as a mobile, injectable reactive material for in-situ sandy groundwater aquifer treatment of As(III).
机译:合成,表征了表面改性的铁纳米颗粒(S-INP)并测试了砷的修复方法(As(III)),这是一种众所周知的有毒地下水污染物。 S-INP材料完全分散在水相中,根据高分辨率透射电子显微镜(HR-TEM)估计其粒径分布为2-10 nm。 X射线光电子能谱法(XPS)表明,除本体的零价FeOs氧化态外,S-INP上还存在Fe(III)氧化物表面膜。 S-INP通过填充在10厘米长的色谱柱中的多孔介质的运输显示,玻璃珠,未烘烤的沙子和烘烤的沙子中的颗粒穿透分别为22.1、47.4和60孔体积。未改性的INP固定不动并聚集在色谱柱入口区域的多孔介质表面上。使用含有约2 g S-INP的S-INP预处理10 cm沙子填充柱的结果表明,从含0.2的进水溶液(流速1.8 mL min?1 )中除去了100%的As(III), 0.5、1.0 mg L?1 As(III)分别处理9、7和4天,分别提供23.3、20.7和10.4 L的无砷水。此外,还发现通过S-INP预处理的50 cm含12 g S的沙子填充柱,可以除去0.5 mg / L溶液(流速1.8 mL min?1 )中100%的As(III)。 -INP提供2.54.4个月以上的时间,提供194.4 L的无砷水。场发射扫描电子显微镜(FE-SEM)显示,在砂存在下与As(III)反应后,S-INP已转变为细长的棒状腐蚀产物颗粒。这些结果表明,S-INP具有很大的潜力,可以用作可移动的可注射的反应性材料,用于原位含沙地下水地下水中As(III)的处理。

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