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利用固定化平菇废基质从水溶液中批量和固定床吸附 Cd(II)。

Batch and fixed-bed biosorption of Cd(II) from aqueous solution using immobilized Pleurotus ostreatus spent substrate.

机构信息

College of Resources and Environment, Northeast Agricultural University, Harbin 150030, China.

College of Resources and Environment, Northeast Agricultural University, Harbin 150030, China.

出版信息

Chemosphere. 2018 Jan;191:799-808. doi: 10.1016/j.chemosphere.2017.08.154. Epub 2017 Sep 27.

Abstract

To prevent the blockage in a continuous fix-bed system, Pleurotus Ostreatus spent substrate (POSS), a composite agricultural waste, was immobilized into granular adsorbents (IPOSS) with polymeric matrix, and used to remove Cd(II) from synthetic wastewater in batch experiment as well as in continuous fixed-bed column system. In batch experiment, higher pH, temperature and Cd(II) initial concentration were conducive to a higher biosorption capacity, and the maximum biosorption capacity reached up to 87.2 mg/g at Cd(II) initial concentration of 200 mg/L, pH 6 and 25 °C. The biosorption of Cd(II) onto IPOSS followed the Langmuir isotherm model with the maximum adsorption capacity(q) of 100 mg/g. The biosorption was an endothermic reaction and a spontaneous process based on positive value of ΔH and negative value of ΔG. In fixed-bed column system, higher bed depth, lower flow rate and influent Cd(II) concentration led to a longer breakthrough and exhaustion time, and the best performance (equilibrium uptake (q) of 14.4 mg, breakthrough time at 31 h and exhaustion time at 78 h) was achieved at a bed depth of 110 cm, a flow rate of 1.2 L/h and an influent concentration of 100 mg/L. Furthermore, regeneration experiment revealed a good reusability of IPOSS with 0.1 M HNO as eluting agent during three cycles of adsorption and desorption. Cd(II) biosorption onto IPOSS mainly relied on a chemical process including ion exchange and complexation or coordination revealed by SEM-EDX, FTIR and XRD analysis.

摘要

为了防止连续固定床系统的堵塞,利用农业复合废弃物糙皮侧耳废基质(POSS)制备了具有聚合基质的颗粒状吸附剂(IPOSS),并将其用于间歇实验和连续固定床柱系统中从合成废水中去除 Cd(II)。在间歇实验中,较高的 pH、温度和 Cd(II)初始浓度有利于更高的生物吸附容量,当 Cd(II)初始浓度为 200mg/L、pH 为 6 和 25°C 时,最大生物吸附容量达到 87.2mg/g。Cd(II)在 IPOSS 上的吸附符合 Langmuir 等温模型,最大吸附容量(q)为 100mg/g。吸附是一个吸热反应,是一个自发过程,其依据是ΔH 为正值和ΔG 为负值。在固定床柱系统中,较高的床深、较低的流速和较高的进水 Cd(II)浓度导致更长的穿透时间和耗尽时间,在床深为 110cm、流速为 1.2L/h 和进水浓度为 100mg/L 时,表现出最佳性能(平衡吸附量(q)为 14.4mg,穿透时间为 31h,耗尽时间为 78h)。此外,再生实验表明,用 0.1M HNO3 作为洗脱剂,在吸附和解吸三个循环后,IPOSS 具有良好的可重复使用性。SEM-EDX、FTIR 和 XRD 分析表明,Cd(II)在 IPOSS 上的吸附主要依赖于离子交换、络合或配位等化学过程。

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