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Schwertmannite Synthesis through Ferrous Ion Chemical Oxidation under Different H2O2 Supply Rates and Its Removal Efficiency for Arsenic from Contaminated Groundwater

机译:不同H2O2供给速率下亚铁离子化学氧化合成Schwertmannite及其对污染地下水中砷的去除效率

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摘要

Schwertmannite-mediated removal of arsenic from contaminated water has attracted increasing attention. However, schwertmannite chemical synthesis behavior under different H2O2 supply rates for ferrous ions oxidation is unclear. This study investigated pH, ferrous ions oxidation efficiency, and total iron precipitation efficiency during schwertmannite synthesis by adding H2O2 into FeSO4·7H2O solution at different supply rates. Specific surface area and arsenic (III) removal capacity of schwertmannite have also been studied. Results showed that pH decreased from ~3.48 to ~1.96, ~2.06, ~2.12, ~2.14, or ~2.17 after 60 h reaction when the ferrous ions solution received the following corresponding amounts of H2O2: 1.80 mL at 2 h (treatment 1); 0.90 mL at 2 h and 14 h (treatment 2); 0.60 mL at 2, 14, and 26 h (treatment 3); 0.45 mL at 2, 14, 26, and 38 h (treatment 4), or 0.36 mL at 2, 14, 26, 38, and 50 h (treatment 5). Slow H2O2 supply significantly inhibited the total iron precipitation efficiency but improved the specific surface area or arsenic (III) removal capacity of schwertmannite. For the initial 50.0 μg/L arsenic (III)-contaminated water under pH ~7.0 and using 0.25 g/L schwertmannite as an adsorbent, the total iron precipitation efficiency, specific surface area of the harvested schwertmannite, and schwertmannite arsenic(III) removal efficiency were 29.3%, 2.06 m2/g, and 81.1%, respectively, in treatment 1. However, the above parameters correspondingly changed to 17.3%, 16.30 m2/g, and 96.5%, respectively, in treatment 5.
机译:Schwertmannite介导的从污染水中去除砷已引起越来越多的关注。但是,尚不清楚在不同的H2O2供给速率下亚铁离子氧化的Schwertmannite化学合成行为。本研究通过在不同供料速率下向FeSO4·7H2O溶液中添加H2O2,研究了Schwertmannite合成过程中的pH,亚铁离子氧化效率和总铁沉淀效率。还对Schwertmannite的比表面积和除砷(III)能力进行了研究。结果表明,当亚铁离子溶液接受以下相应量的H2O2时,pH值在60 h反应后从〜3.48降至〜1.96,〜2.06,〜2.12,〜2.14或〜2.17(处理1) ;在2小时和14小时时为0.90毫升(处理2);在2、14和26小时时为0.60 mL(处理3);在2、4、14、26和38时(处理4)为0.45 mL,或在2、14、26、38和50时(处理5)为0.36 mL。缓慢的H2O2供应显着抑制了总铁的沉淀效率,但提高了Schwertmannite的比表面积或砷(III)的去除能力。对于初始pH值为7.0的50.0μg/ L砷(III)污染的水,并使用0.25 g / L schwertmannite作为吸附剂,总铁沉淀效率,收获的schwertmannite的比表面积和schwertmannite砷(III)的去除处理1的效率分别为29.3%,2.06 m 2 / g和81.1%。但是,上述参数相应地更改为17.3%,16.30 m 2 /在治疗5中分别为g和96.5%。

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