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磁性介孔碳负载纳米零价铁的制备及其去除高盐废水中Cr(Ⅲ)有机配合物

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采用液相还原法制备了磁性介孔碳(Fe3O4@C)负载纳米零价铁(nano zero-valent iron,nZVI)复合材料(Fe3O4@C-nZVI),并将其用于高盐水中Cr(Ⅲ)-EDTA(EDTA:乙二胺四乙酸)的去除.扫描电镜、透射电镜、X射线衍射等表征表明nZVI成功负载且分散良好,可磁性分离,在碳层保护下nZVI稳定性强,有利于材料的重复利用.nZVI的加入大大提高了Fe3O4@C-nZVI对Cr(Ⅲ)-EDTA的吸附能力,在pH=4.0、反应温度为25 ℃时,Fe3O4@C-nZVI对Cr(Ⅲ)-EDTA的最大吸附量为10.24 mg·g-1,显著高于Fe3O4@C(4.31 mg·g-1).吸附Cr(Ⅲ)-EDTA的过程更符合Langmuir模型和准二级动力学模型.Fe3O4@C-nZVI对Cr(Ⅲ)-EDTA的吸附能力随着溶液pH值的增加先增加后减小;低浓度络合剂(EDTA、柠檬酸)会促进Cr(Ⅲ)-EDTA的吸附,而络合剂浓度增加时则表现为抑制;高浓度阳离子(Na+、K+、Ca2+)会促进Cr(Ⅲ)-EDTA的吸附.Fe3O4@C-nZVI在盐和络合剂环境中对Cr(Ⅲ)-EDTA仍表现出显著的吸附效果.经过3次再生循环后,Fe3O4@C-nZVI对Cr(Ⅲ)-EDTA的吸附量达6.90mg·g-1.X射线光电子能谱分析表明,Fe3O4@C-nZVI通过表面Fe(Ⅲ)与Cr(Ⅲ)-EDTA之间的配位作用形成Fe(Ⅲ)-EDTA-Cr(Ⅲ)配合物从而将Cr(Ⅲ)-EDTA去除,随后通过离子置换作用将Cr(Ⅲ)置换出来,置换出的Cr(Ⅲ)会与表面氧化铁共沉淀为CrxFe1-x(OH)3,进而沉积在nZVI表面被去除.
Preparation of magnetic mesoporous carbon loaded nano zero-valent iron for removal of Cr(Ⅲ)organic complexes from high-salt wastewater
Magnetically mesoporous carbon(Fe3O4@C)/nano-zerovalent iron(nZVI)composites(Fe3O4@C-nZVI)were successfully prepared by a liquid-phase reduction for the effective removal of Cr(Ⅲ)-EDTA(EDTA:ethylenedi-aminetetra-acetic acid)in high-salinity wastewater.By characterization and analysis by scanning electron micro-scope(SEM)and electron microscope(TEM),the nZVI has been successfully loaded into the carbon layer without significant agglomeration and can be magnetically separated and nZVI was stable under the protection of a carbon layer which is favorable for the reuse of materials.The presence of nZVI on the adsorbents greatly improved the adsorption of Cr(Ⅲ)-EDTA and the maximum adsorption capacity of Fe3O4@C-nZVI was 10.24 mg·g-1 at pH=4.0,25 ℃,which was remarkably higher than that of Fe3O4@C(4.31 mg·g-1).The results showed that the Langmuir model and the pseudo-second-order kinetic model can better describe the adsorption of Cr(Ⅲ)-EDTA by Fe3O4@C-nZVI.The adsorption capacity of Fe3O4@C-nZVI on Cr(Ⅲ)-EDTA increased and then decreased with the increase of solu-tion pH value;low concentrations of complexing agents(EDTA,citric acid)would promote the adsorption of Cr(Ⅲ)-EDTA,whereas an increase in the concentration of the complexing agents showed inhibition;due to the charge shielding effect,high concentrations of cations(Na+,K+,Ca2+)in the solution will promote the adsorption of Cr(Ⅲ)-EDTA.Fe3O4@C-nZVI still showed significant adsorption of Cr(Ⅲ)-EDTA in a salt and complexant environment.The adsorption saturated Fe3O4@C-nZVI was regenerated by 0.1 mol·L-1 HC1 solution,the adsorption of Cr(Ⅲ)-EDTA by Fe3O4@C-nZVI reached 6.90 mg·g-1 after three regeneration cycles.X-ray photoelectron spectrum analysis of Fe3O4@C-nZVI before and after reaction showed that the adsorption mechanism was mainly through complexation between surface Fe(Ⅲ)and Cr(Ⅲ)-EDTA to form Fe(Ⅲ)-EDTA-Cr(Ⅲ)complexation products,and subsequently displaces Cr(Ⅲ)due to ionic displacement,and the displaced Cr(Ⅲ)will be removed by co-precipitation with Fe(Ⅲ)as CrxFe1-x(OH)3 deposited on the nZVI surface.

magnetically mesoporous carbonnano zero-valent ironCr(Ⅲ)high salinity wateradsorption mechanism

张元培、王家宏、黄金明、胡智

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陕西科技大学环境科学与工程学院,西安 710021

陕西省无机材料绿色制备与功能化重点实验室,西安 710021

磁性介孔碳 纳米零价铁 Cr(Ⅲ) 高盐废水 吸附机制

国家自然科学基金

22076111

2024

无机化学学报
中国化学会

无机化学学报

CSTPCD北大核心
影响因子:0.665
ISSN:1001-4861
年,卷(期):2024.40(9)