利用螺旋藻提取的磁性生物炭去除水溶液中的砷

IF 5.4 Q2 ENGINEERING, ENVIRONMENTAL Journal of hazardous materials advances Pub Date : 2024-10-02 DOI:10.1016/j.hazadv.2024.100490
Hyunsoo Kim , Eunji Myung , Nagchoul Choi , Kanghee Cho
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引用次数: 0

摘要

地表水和地下水中的砷污染每天影响着数百万人。将 As(III)氧化成毒性较低的 As(V)是一种广泛使用的策略,可提高从溶液中去除砷的能力。本研究开发并评估了一种铁改性生物炭(FeSP600)。Platensis 螺旋藻(SP)因其理化特性和潜在应用而成为最有前途的微藻之一。SP 中的高氮含量可能会影响生物炭的理化性质,可将其作为固有的氮源,通过碳化掺入氮的生物炭。铁改性后,SP 中形成的铁物种和含 N 成分被用于引入吡啶 N,吡啶 N 可与铁配位形成 Fe-N。我们证明,FeSP600 中形成的铁物种(Fe0、Fe2+ 和 Fe3+)和缺陷结构可作为表面催化反应的活性位点。FeSP600 不仅具有磁性,还能有效去除水溶液中的砷。这些特性归因于结晶缺陷结构上的γ-Fe2O3 颗粒释放了 Fe2+ 和活性氧(ROS)。As(III) 和 As(V) 的去除率受初始 pH 值的影响。当 pH 值从 3 升至 9 时,As(III) 的去除率从 57.2% 升至 94.9%,而 As(V) 的去除率则从 80.1% 降至 46.8%。共存离子的存在完全(PO43-)或部分(Cl-、CO32- 和 SO42-)抑制了 As 的去除。As(V) 的去除取决于静电相互作用,但 As(III) 的去除是一个复杂的过程,包括氧化和表面吸附,因为 ROS 能够将 As(III) 氧化成 As(V)。我们的研究表明,FeSP600 具有有利于从水环境中去除 As(III) 和 As(V) 的特性。这项研究的结果有可能实际应用于处理砷污染的水源,特别是改善发展中国家的饮用水净化系统。更重要的是,需要评估使用 FeSP600 对水生生态系统的影响,以确保该技术的安全应用。因此,开发大规模生产 FeSP600 的方法对于该技术的商业化至关重要,这就需要在该领域开展工艺工程研究。
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Removal of arsenic from aqueous solution using magnetic biochar derived from Spirulina platensis
Arsenic contamination in surface waters and groundwater affects millions of people on a daily basis. Oxidation of As(III) to less toxic As(V) is a widely used strategy to enhance the removal of As from solution. This study developed and evaluated a Fe-modified biochar (FeSP600). Spirulina platensis (SP) is one of the most promising microalgae because of its physicochemical properties and potential applications. The high N content of SP may affect the physicochemical properties of the biochar, which could be used as an inherent N source for N doping biochar by carbonization. After Fe modification, the formed Fe species and N-containing components of SP were used to introduce pyridinic N, which can be coordinated with Fe to form Fe-N. We demonstrated that the formed Fe species (Fe0, Fe2+ and Fe3+) and the defective structures in FeSP600 could act as active sites for surface catalytic reactions. FeSP600 not only had magnetic properties but also could effectively remove As from an aqueous solution. These properties were attributed to the release of Fe2+ and the reactive oxygen species (ROSs) generated by the γ-Fe2O3 particles on the crystalline defect structure. As(III) and As(V) removal were affected by the initial pH values. The removal efficiencies for As(III) increased from 57.2 % to 94.9 % as the pH increased from 3 to 9, whereas that for As(V) decreased from 80.1 % to 46.8 %. The presence of coexisting ions either completely (PO43) or partially (Cl, CO32 and SO42) inhibited As removal. The removal of As(V) depended on electrostatic interactions, but As(III) removal was a complex process, including both oxidation and surface adsorption, as the ROSs were able to oxidize As(III) to As(V). Our study demonstrates that FeSP600 has properties that are beneficial for the removal of As(III) and As(V) from aqueous environments. The findings of this study have potential for real-world application in treating As-contaminated water sources, particularly in improving drinking water purification systems in developing countries. More importantly, an assessment of the impact of FeSP600 usage on aquatic ecosystems is required to ensure the safe application of this technology. Therefore, developing methods for mass production of FeSP600 is essential for the commercialization of this technology, necessitating process engineering studies in this area.
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Journal of hazardous materials advances
Journal of hazardous materials advances Environmental Engineering
CiteScore
4.80
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50 days
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