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软模板法合成有机 ZnCr-LDH 对阴离子染料的增强吸附性能。

Enhanced adsorption properties of organic ZnCr-LDH synthesized by soft template method for anionic dyes.

机构信息

School of Chemistry and Chemical Engineering, Henan Key Laboratory of Coal Green Conversion, Henan Polytechnic University, Jiaozuo, 454000, China.

Collaborative Innovation Center of Coal Work Safety of Henan Province, Jiaozuo, 454000, China.

出版信息

Environ Sci Pollut Res Int. 2021 Sep;28(35):48236-48252. doi: 10.1007/s11356-021-14035-w. Epub 2021 Apr 27.

DOI:10.1007/s11356-021-14035-w
PMID:33905058
Abstract

Organic ZnCr-LDH (ST-LDH) was synthesized by a facile one-step hydrothermal technique using methyl orange (MO) as a soft template agent, which can efficiently remove methyl orange (MO), Congo red (CR), and orange II (OII) from aqueous solution. The microstructure of ST-LDH by modifying changed obviously, from the cellular structure to the stacking structure formed by the face-face contact of hydrotalcite nanosheets, which resulted in much more exchangeable nitrate ions to remain in the interlayer space. The pre-insertion of benzene sulfonate as a pillar expanded the interlayer gallery, which facilitated the pollutant anions (MO, CR, and OII) into the interlayer of LDH in the subsequent adsorption process. The maximum adsorption capacity of ST-LDH for MO, CR, and OII was 4200.8 mg/g, 1252.0 mg/g, and 1670.6 mg/g, respectively, which is approximately 1.86 times, 1.8 times, and 2.32 times that of the pristine NO-LDH, respectively. The removal mechanism of anionic dyes was determined as anion exchange between NO anions and dye molecules. The adsorption behavior for MO and OII is multilayer adsorption, while the adsorption behavior for CR is monolayer adsorption. The adsorption process mainly was controlled by the chemical bonding between the dye molecules and adsorbent active sites. The LDH can be effectively regenerated by photocatalysis after MO adsorption. The ST-LDH has a great potential to be used as a high-efficient adsorbent to remove anionic dyes from aqueous solution. The schematic illustration of the synthetic process of soft template agent modified and unmodified hydrotalcites by one-pot hydrothermal method and the adsorption process of MO by ST-LDH were shown in Fig. 12. Modified hydrotalcite (ST-LDH) was prepared using methyl orange (MO) as a soft template agent. Compared with unmodified hydrotalcite (NO-LDH), the insertion of benzene sulfonate anions into the hydrotalcite layer resulted in the increase of the interlayer spacing from 8.269 to 8.654Å. The LDH host structure pre-intercalated by benzene sulfonate anions evolved into pillared materials in interlayer; benzene sulfonate anions as a column expanded the interlayer spacing of (003) base plane, which facilitated the pollutant anions (MO, CR, and OII) into the interlayer of ST-LDH and exchanged with NO anion in the subsequent adsorption process. It can be inferred that in the process of modification hydrotalcite by benzene sulfonate, a small amount of benzene sulfonate anions pre-inserted into the gallery of hydrotalcite with a monolayer model in the process of hydrotalcite modification, and its inclination angle is calculated to be about 29.1°. After ST-LDH sample adsorbed the MO molecules, dye molecules intercalated into the LDH host, and successful exchange with NO anions, the d value increased to 24.78 Å. A large amount of MO anions were intercalated into the gallery of ST-LDH with a bilayer model according to the Freundlich isotherm model, and the tilting angle increases to 53.6°. The adsorption capacity of MO by ST-LDH was significantly enhanced to 4200.8 mg/g, which was much higher than that of NO-LDH (2252.8 mg/g). Schematic illustration of the synthetic process of LDH materials and adsorption process of MO by ST-LDH.

摘要

有机 ZnCr-LDH(ST-LDH)通过简便的一步水热技术合成,使用甲基橙(MO)作为软模板剂,可有效去除水溶液中的甲基橙(MO)、刚果红(CR)和橙色 II(OII)。通过修饰改变的 ST-LDH 的微观结构明显改变,从细胞结构到水滑石纳米片面对面接触形成的堆叠结构,这导致更多的可交换的硝酸盐离子保留在层间空间中。苯磺酸根的预插入作为支柱扩展了层间通道,这有利于在随后的吸附过程中使污染物阴离子(MO、CR 和 OII)进入 LDH 的层间。ST-LDH 对 MO、CR 和 OII 的最大吸附容量分别为 4200.8、1252.0 和 1670.6 mg/g,分别约为原始 NO-LDH 的 1.86、1.8 和 2.32 倍。阴离子染料的去除机制被确定为 NO 阴离子和染料分子之间的阴离子交换。MO 和 OII 的吸附行为是多层吸附,而 CR 的吸附行为是单层吸附。吸附过程主要受染料分子和吸附剂活性位点之间的化学键合控制。MO 吸附后,LDH 可通过光催化有效再生。ST-LDH 具有作为高效吸附剂从水溶液中去除阴离子染料的巨大潜力。图 12 显示了通过一锅水热法合成软模板剂改性和未改性水滑石的合成过程示意图以及 ST-LDH 对 MO 的吸附过程。使用甲基橙(MO)作为软模板剂制备改性水滑石(ST-LDH)。与未改性水滑石(NO-LDH)相比,苯磺酸根阴离子的插入导致层间距从 8.269 增加到 8.654Å。预插入苯磺酸根阴离子的 LDH 主体结构在层间演变为支柱材料;苯磺酸根阴离子作为支柱扩展了(003)基面的层间距,这有利于污染物阴离子(MO、CR 和 OII)进入 ST-LDH 的层间,并在随后的吸附过程中与 NO 阴离子交换。可以推断,在苯磺酸根改性水滑石的过程中,少量的苯磺酸根阴离子在水滑石改性过程中以单层模型预先插入水滑石的层间,其倾斜角计算约为 29.1°。在 ST-LDH 样品吸附 MO 分子后,染料分子插入 LDH 主体,与 NO 阴离子成功交换,d 值增加到 24.78Å。根据 Freundlich 等温模型,大量 MO 阴离子以双层模型插入 ST-LDH 的层间,倾斜角增加到 53.6°。ST-LDH 对 MO 的吸附容量显著增强至 4200.8 mg/g,远高于 NO-LDH(2252.8 mg/g)。LDH 材料的合成过程示意图和 ST-LDH 对 MO 的吸附过程。

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