首页|赤铁矿的硫化改性及硫化产物对水中六价铬的还原固定化

赤铁矿的硫化改性及硫化产物对水中六价铬的还原固定化

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以赤铁矿为原料、硫化钠为硫化试剂,对赤铁矿进行了硫化改性,考察了硫化赤铁矿(SH)对水中六价铬Cr(Ⅵ)的还原固定化性能.Langmuir等温吸附模型拟合结果表明,该材料在pH=7时对Cr(Ⅵ)的最大吸附量为66.7 mg·g-1,约为原始赤铁矿的39倍.SH对Cr(Ⅵ)的去除过程符合准二级动力学模型,表明该过程可能受化学吸附控制.进一步采用TEM、XRD等手段对SH进行了表征,并结合材料吸附前后的XPS图谱变化,对SH去除水中Cr(Ⅵ)的机制进行了分析.结果表明,与未改性的赤铁矿相比,硫化改性赤铁矿对Cr(Ⅵ)去除性能显著提高的原因可能源于赤铁矿表面形成的铁-硫化合物层.在SH还原固定化Cr(Ⅵ)的过程中,表面硫化层中的还原性物质FeS、吸附态Fe(Ⅱ)和S(-Ⅱ)将Cr(Ⅵ)还原为Cr(Ⅲ),从而实现对Cr(Ⅵ)的稳定化.
Hematite sulfidation and its product for reductive immobilization of chromate in water
Sulfidated Hematite(SH)was synthesized using sodium sulfide as a sulfidation reagent,and its reductive immobilization performance for chromate in water was examined for the resulted material.Model fitting by Langmuir isothermal equation indicated that the material had a maximum adsorption capacity of 66.7 mg·g-1 to chromate at neutral pH,which was about 39 times that of the original hematite.The removal process of chromate by SH was well described by the pseudo-second-order kinetic model,suggesting that the process might be controlled by a chemical adsorption.TEM and XRD were utilized to characterize SH and the associated mechanism of chromate removal was analyzed in combination with the changes in XPS spectra of the material before and after adsorption.The result showed that the improved performance of SH in chromate reduction could be ascribed to the Fe-S layer formed on hematite surface.During reductive immobilization of chromate by SH,the reducing substances FeS,adsorbed Fe(Ⅱ)and S(-Ⅱ)on the surface of sulfidated hematite jointly participated in Cr(Ⅵ)reduction to Cr(Ⅲ),thereby achieving chromate stabilization.

hematitesodium sulfidesulfidationsulfidated hematitechromate reductive immobilization

薛轲歆、赵亮、张旭升、何雅莉、王建城、郑建中

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中国科学院大学资源与环境学院,北京 100049

滨州魏桥国科高等技术研究院,滨州 256606

赤铁矿 硫化钠 硫化改性 硫化赤铁矿 Cr(Ⅵ)还原固定化

中央高校基本科研业务费专项教育部产学合作协同育人项目

E3E40501E1410504

2024

环境工程学报
中国科学院生态环境研究中心

环境工程学报

CSTPCD北大核心
影响因子:0.804
ISSN:1673-9108
年,卷(期):2024.18(2)
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