College of Marine and Environmental Sciences, Tianjin University of Science & Technology, Tianjin, 300457, People's Republic of China.
Tianjin Key Laboratory of Marine Resources & Chemistry, Tianjin, 300457, China.
Environ Sci Pollut Res Int. 2023 Nov;30(52):112422-112432. doi: 10.1007/s11356-023-30246-9. Epub 2023 Oct 13.
A novel layer-by-layer adsorption was proposed and used for adsorption of Cu(II) and Cr(VI) on the pre-bleached sawdust cellulose coated with polyethylenimine (PSC-PEI). It was found that PSC-PEI loaded with Cu(II) cations was favorable for Cr(VI) anions adsorption. The maximum adsorption capacities estimated by Langmuir model for Cu(II) and Cr(VI) were 80.0 and 93.5 mg/g, respectively. The kinetic regression results, as fitted by the pseudo-second order model, revealed that the rate constant (k) for Cr(VI) at 0.07 g/mg/min is significantly greater than that observed for Cu(II) at 0.02 g/mg/min, indicating that PSC-PEI exhibited a stronger affinity towards Cr(VI). The first-layer adsorption mechanism for Cu(II) involved the formation of copper-amine complex. Zeta potential and XPS results revealed that the second-layer adsorption of Cr(VI) mainly involved electrostatic attraction and redox reaction. The simulated results for dynamic column test showed good agreement between the theoretical values and the experimental values. The mass transfer mechanism indicated that Cu(II) adsorption was dependent on external mass transfer process, while the internal mass transfer is the rate-determining step for Cr(VI) adsorption. The saturated adsorbent was regenerated by washing with 5% NaOH and 5% HSO solutions and the adsorption ability of more than 70% was sustained after three cycles of regeneration. This study demonstrated that the oppositely charged Cu(II) cations and Cr(VI) anions could be effectively removed by amine-rich cellulose adsorbent from wastewater through layer-by-layer adsorption.
提出了一种新型的逐层吸附方法,并将其用于负载聚乙烯亚胺(PEI)的预处理漂白木纤维素对 Cu(II)和 Cr(VI)的吸附。结果表明,负载 Cu(II)阳离子的 PSC-PEI 有利于 Cr(VI)阴离子的吸附。通过 Langmuir 模型估算的 Cu(II)和 Cr(VI)的最大吸附容量分别为 80.0 和 93.5mg/g。准二级动力学回归结果表明,Cr(VI)的速率常数(k)为 0.07g/mg/min,明显大于 Cu(II)的 0.02g/mg/min,表明 PSC-PEI 对 Cr(VI)具有更强的亲和力。Cu(II)的第一层吸附机制涉及铜-胺配合物的形成。Zeta 电位和 XPS 结果表明,Cr(VI)的第二层吸附主要涉及静电吸引和氧化还原反应。动态柱试验的模拟结果表明,理论值与实验值之间具有良好的一致性。传质机制表明,Cu(II)的吸附取决于外部传质过程,而 Cr(VI)的吸附则受内部传质过程的限制。饱和吸附剂通过 5%NaOH 和 5%HSO4 溶液进行再生,经过三次再生循环后,吸附能力仍保持在 70%以上。该研究表明,带相反电荷的 Cu(II)阳离子和 Cr(VI)阴离子可以通过胺基丰富的纤维素吸附剂通过逐层吸附从废水中有效地去除。