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首页> 外文期刊>Chemical engineering journal >Adsorption behavior of crystal violet onto opal and reuse feasibility of opal-dye sludge for binding heavy metals from aqueous solutions
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Adsorption behavior of crystal violet onto opal and reuse feasibility of opal-dye sludge for binding heavy metals from aqueous solutions

机译:结晶紫对蛋白石的吸附行为以及蛋白石污泥可用于结合水溶液中的重金属的可行性

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The potential of opal for removing crystal violet (CV) dye and reuse feasibility of opal-CV sludge for binding heavy metals from aqueous solutions were investigated. The adsorbent was characterized by scanning electron microscopy (SEM), Fourier transform infrared spectroscopy (FTIR), X-Ray Diffraction (XRD) and the point of zero charge (pH_(pzc)) analysis. The thermal treatment of opal at temperatures of 300,400, 500, 700 °C increased the pH_(pzc) value from 6.6 to 7.4 and lead to a decrease in the adsorption of CV dye, demonstrating the significance of the functional groups spread over the surface of opal. The equilibrium adsorption data fitted well to the Freundlich model and the kinetic data conformed to the pseudo-second-order model. Intra-particle diffusion was not the sole rate-controlling factor. The maximum adsorption capacity of CV was found to be 101.13 mg g~(-1) at 30 °C. The activation energy (E_(a)) of 13.85 kJ mol~(-1) indicated that the adsorption of CV onto opal was a physisorption. Thermodynamic parameters (AG0, AH?, and AS?) were evaluated and revealed that the adsorption process was spontaneous and endothermic in nature. Moreover, the opal-CV sludge was reutilized after calcination at 250 °C (O-CV-250) for the removal of heavy metals from aqueous solution. The O-CV-250 had a maximum adsorption capacity of Pb(II) of 20.92 mgg~(-1) while has almost no adsorption of Ni(II) and Cr(VI). Enrichment of Pb(II) was conducted and almost 65% of the Pb(II) was collected. This work presents an effective approach for the treatment of dye wastewater and reutilization of dye sludge to enrich heavy metals.
机译:研究了蛋白石去除结晶紫(CV)染料的潜力以及蛋白石CV污泥用于结合水溶液中重金属的可行性。通过扫描电子显微镜(SEM),傅立叶变换红外光谱(FTIR),X射线衍射(XRD)和零电荷点(pH_(pzc))分析来表征吸附剂。蛋白石在300,400、500、700°C的温度下进行的热处理将pH_(pzc)值从6.6提高到7.4,并导致CV染料的吸附降低,证明了官能团散布在CV表面的重要性。蛋白石。平衡吸附数据与弗氏模型非常吻合,动力学数据与拟二阶模型吻合。粒子内扩散不是唯一的速率控制因素。在30°C下,CV的最大吸附容量为101.13 mg g〜(-1)。 13.85 kJ mol〜(-1)的活化能(E_(a))表明CV在蛋白石上的吸附是一种物理吸附。评估了热力学参数(AG0,AH 2和AS 2),结果表明吸附过程是自然的并且是吸热的。此外,蛋白石-CV污泥在250°C(O-CV-250)煅烧后被重新利用,以从水溶液中去除重金属。 O-CV-250的最大Pb(II)吸附量为20.92 mgg〜(-1),而Ni(II)和Cr(VI)几乎没有吸附。进行了Pb(II)的富集,并收集了近65%的Pb(II)。这项工作提出了一种处理染料废水和再利用染料污泥以富集重金属的有效方法。

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