Zr/Cu改性生物炭同步吸附地下水中As—I的机制研究

Mechanism of synchronized adsorption of As-I in groundwater by Zr/Cu modified biochar

  • 摘要: 新疆奎屯地区天然共存的砷(As)和碘(I)引起了越来越多的关注,由于As、I吸附位点的竞争使得其同时去除仍然是一个挑战。本研究以小麦秸秆生物炭(XM)为载体,通过负载Zr、Cu优化制备得到生物炭基复合材料(Zr/Cu—XM),研究了Zr/Cu的不同比例调控对As(Ⅴ)、I吸附的影响,并结合SEM-EDS、FTIR、XPS等技术对材料进行表征分析,探讨了As、I同步吸附机制。结果表明: Zr、Cu调控比例后Zr/Cu的质量比为3∶1时,获得的改性生物炭Zr/Cu(3∶1)—XM是表面结构优良的介孔材料,能在2 h内同步快速吸附水中的As(Ⅴ)、I,去除率高达98%,相比于原始生物炭对As(Ⅴ)、I吸附容量增加了接近40倍, As(Ⅴ)、I的最大吸附量为22.77 mg·g−1、23.40 mg·g−1。等温吸附模型符合Langmuir等温模型,吸附As(Ⅴ)、I更符合准二级动力学方程,吸附过程不仅受颗粒内扩散控制,也依赖于表面吸附等机制。As(Ⅴ)、I在吸附过程中存在竞争吸附,当pH<6.77时吸附As(Ⅴ)、I存在静电吸附,化学吸附占据关键作用, Zr—OH吸附As亲和力更强,生成的Zr—O—As络合物更稳定, Cu—OH会提供额外的位点。I 以CuI形式沉淀,并可以形成强烈的化学键。当pH> 6.77时,静电吸附作用消失,As(Ⅴ)占据了有效吸附位点而且形成了稳定性更强的Zr—O—As, I主要与吸附剂表面金属—OH中—OH交换形成表面络合物金属,此时Cu—OH在吸附I中起关键作用,共存的As(Ⅴ)、I也将竞争表面金属羟基。

     

    Abstract: The natural coexistence of arsenic (As) and iodine (I) in the Kuytun region of Xinjiang has attracted increasing attention. Simultaneous removal of As and I remains a challenge due to competition for adsorption sites. In this study, wheat straw biochar (XM) was used as a carrier, and zirconium (Zr) and copper (Cu) were loaded onto it to optimize the preparation of a biochar-based composite material (Zr/Cu—XM). The effects of different Zr/Cu ratios and pH on the adsorption of As(Ⅴ) and I were investigated. The material was characterized using techniques such as SEM-EDS, FTIR, and XPS, and the simultaneous adsorption mechanism of As and I was explored. The results demonstrated that by fine-tuning the mass ratio of the modified metals Zr and Cu to 3∶1, the resultant Zr/Cu(3∶1)-XM material exhibit mesoporosity and possess an exceptional surface structure. This unique composition facilitat the simultaneous and rapid adsorption of both As(Ⅴ) and I ions from aqueous solutions within a mere 2 hours, achieving a remarkable removal efficiency of up to 98%. Compared to the original biochar, the adsorption capacity for As(Ⅴ) and I increased by nearly 40 times, with maximum adsorption capacities of 22.77 mg·g−1 and 23.40 mg·g−1, respectively. The isotherm adsorption model fit the Langmuir isotherm model, and the adsorption of As(Ⅴ) and I is more consistent with the pseudo-second-order kinetic equation. The adsorption process is not only controlled by intraparticle diffusion but also depend on mechanisms such as surface adsorption. Competitive adsorption of As(Ⅴ) and I occurr during the adsorption process. When pH < 6.77, electrostatic adsorption and chemical adsorption play crucial roles in the adsorption of As(Ⅴ) and I. Zr-OH has a stronger affinity for adsorbing As, forming a more stable Zr—O—As complex, while Cu-OH provided additional sites. I precipitated in the form of CuI and could form strong chemical bonds. When the pH>6.77, electrostatic adsorption vanishes. As (V) then occupies the active adsorption sites and establishes a more stable Zr—O—As linkage. I predominantly swaps with the surface metal-OH of the adsorbent to form a surface metal complex. At this stage, Cu-OH becomes pivotal in the adsorption of iodide. Concurrently present with As (V), iodide will also vie for the surface metal hydroxyl groups.

     

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