Fe3+对铬酸盐和砷酸盐吸附的不同影响:含铁水合铁和纳米tio2吸附剂的比较

Shan Hu, Huanhuan Fu, Jingyi Fu
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引用次数: 0

摘要

Fe3+是酸性矿山水(AMD)中特别普遍存在的一种离子,对含铁矿物的结晶和Cr(VI)、as (V)等多种共存氧离子的固定化具有重要影响。为了研究Fe3+对Cr(VI)和As(V)的影响,选择了具有优异吸附效果和独特稳定性的水合铁(Fh)和纳米tio2。由于Fe3+在Fh中溶解并促进As(V)吸附,Fh对As(V)的吸附量为124.0 mg/g,是TiO2吸附量(62.76 mg/g)的2倍。Fe3+在As(V)吸附体系中的共存极大地增强了TiO2(18.9 ~ 56.5%)和Fh(1.03 ~ 15.7%)对As(V)的吸附,并且通过FTIR和EXAFS光谱证实了额外的Fe-As配合物对Fh和TiO2上额外的As(V)去除有贡献。另一方面,TiO2 (18.15 mg/g)和Fh (19.50 mg/g)对Cr(VI)的吸附能力几乎相同,Fe3+的共存在甚至轻微阻碍了Fh对Cr(VI)的吸附。光谱和模拟结果表明,单齿Cr(VI)吸附配合物被Fe3+阻断,但外球和内球双齿Cr(VI)表面配合物不受影响。此外,在三元As-Cr-Fe吸附体系中,Cr(VI)对As-Fe表面配合物或沉淀的发展影响不大。根据干扰机理,对AMD废水对Fh和TiO2的实际吸附进行了较好的解释和预测。这一发现将为amd污染地区有害金属化合物的生物利用度和命运提供新的视角。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

0Distinct Effects of Fe3+ on the Adsorption of Chromate and Arsenate: A Comparison of Iron-Bearing Ferrihydrite and Nano-TiO2 Absorbents

0Distinct Effects of Fe3+ on the Adsorption of Chromate and Arsenate: A Comparison of Iron-Bearing Ferrihydrite and Nano-TiO2 Absorbents
Fe3+, a particularly prevalent ion in acid mine drainage (AMD), has a substantial impact on the crystallization of iron-bearing minerals and the immobilization of multiple co-existing oxyanions such as Cr(VI) and As(V). To investigate the varied effects of Fe3+ on Cr(VI) and As(V), ferrihydrite (Fh) and nano-TiO2 were selected due to their superior adsorption effectiveness and distinctive stability. As a result of the dissolution of Fe3+ in Fh and its subsequent promotion to As(V) adsorption, As(V) adsorption capacity on Fh (124.0 mg/g) was twice that of TiO2 (62.76 mg/g). The co-existence of Fe3+ in the As(V) adsorption system greatly enhanced As(V) sorption on TiO2 (18.9–56.5%) and Fh (1.03–15.7%), and an additional Fe-As complex was confirmed to contribute extra As(V) removal on both Fh and TiO2 by the FTIR and EXAFS spectra. On the other hand, TiO2 (18.15 mg/g) and Fh (19.50 mg/g) exhibited nearly identical Cr(VI) adsorption capabilities, and the co-presence of Fe3+ even slightly blocked Cr(VI) sorption on Fh. The spectroscopic and modeling results showed that the monodentate Cr(VI) adsorption complex was blocked by Fe3+, but the outer-sphere and bidentate inner-sphere Cr(VI) surface complexes were unaffected. Additionally, in the ternary As-Cr-Fe adsorbate systems, Cr(VI) had little effect on the development of As-Fe surface complexes or precipitates. With the interference mechanisms, actual AMD wastewater adsorption on Fh and TiO2 was well explained and predicted. The findings would offer fresh perspectives on the bioavailability and fate of hazardous metal compounds in the AMD-polluted locations.
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