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Heating Changes Bio-Schwertmannite Microstructure and Arsenic(III) Removal Efficiency

机译:加热变化生物-Schwertmannite显微组织和除砷效率

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Schwertmannite (Sch) is an efficient adsorbent for arsenic(III) removal from arsenic(III)-contaminated groundwater. In this study, bio-schertmannite was synthesized in the presence of dissolved ferrous ions and Acidithiobacillus ferrooxidans LX5 in a culture media. Bio-synthesized Sch characteristics, such as total organic carbon (TOC), morphology, chemical functional groups, mineral phase, specific surface area, and pore volume were systematically studied after it was dried at 105 ???°C and then heated at 250?¢????550 ???°C. Differences in arsenic(III) removal efficiency between 105 ???°C dried-sch and 250?¢????550 ???°C heated-sch also were investigated. The results showed that total organic carbon content in Sch and Sch weight gradually decreased when temperature increased from 105 ???°C to 350 ???°C. Sch partly transformed to another nanocrystalline or amorphous phase above 350 ???°C. The specific surface area of 250 ???°C heated-sch was 110.06 m 2 /g compared to 5.14 m 2 /g for the 105 ???°C dried-sch. Total pore volume of 105 ???°C dried-sch was 0.025 cm 3 /g with 32.0% mesopore and 68.0% macropore. However, total pore volume of 250 ???°C heated-mineral was 0.106 cm 3 /g with 23.6% micropore, 33.0% mesopore, and 43.4% macropore. The arsenic(III) removal efficiency from an initial 1 mg/L arsenic(III) solution (pH 7.5) was 25.1% when 0.25 g/L of 105 ???°C dried-sch was used as adsorbent. However, this efficiency increased to 93.0% when using 250 ???°C heated-sch as adsorbent. Finally, the highest efficiency for arsenic(III) removal was obtained with sch-250 ???°C due to high amounts of sorption sites in agreement with the high specific surface area (SSA) obtained for this sample.
机译:Schwertmannite(Sch)是从受砷(III)污染的地下水中去除砷(III)的有效吸附剂。在这项研究中,生物硅钙锰矿是在溶解的亚铁离子和酸性氧化铁硫杆菌铁氧体LX5的存在下在培养基中合成的。在105℃下干燥然后在250℃加热后,系统地研究了生物合成的Sch特性,例如总有机碳(TOC),形态,化学官能团,矿物相,比表面积和孔体积。 550℃。还研究了在105℃的干电池和250℃的550℃的加热电池之间的砷(Ⅲ)去除效率的差异。结果表明,当温度从105℃升高到350℃时,Sch中的总有机碳含量和Sch的重量逐渐减少。 Sch部分在350℃以上转变成另一种纳米晶或非晶相。 250℃加热过的比表面积为110.06m 2 / g,而105℃干燥过的比表面积为5.14m 2 / g。在32.0%的中孔和68.0%的大孔下,在105℃干燥的sch的总孔体积为0.025cm 3 / g。然而,在250℃加热的矿物中的总孔体积为0.106cm 3 / g,具有23.6%的微孔,33.0%的中孔和43.4%的大孔。当将0.25g / L的105℃干燥溶液用作吸附剂时,从最初的1mg / L砷(Ⅲ)溶液(pH 7.5)中除去砷(Ⅲ)的效率为25.1%。但是,当使用250℃加热sch作为吸附剂时,该效率提高到93.0%。最后,由于高的吸附位点与该样品所获得的高比表面积(SSA)相一致,在sch-250℃下获得了最高的砷(Ⅲ)去除效率。

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