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首页> 外文期刊>Environmental Science and Pollution Research >Removal and mechanism of Cu (II) and Cd (II) from aqueous single-metal solutions by a novel biosorbent from waste-activated sludge
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Removal and mechanism of Cu (II) and Cd (II) from aqueous single-metal solutions by a novel biosorbent from waste-activated sludge

机译:废物活化污泥中的新型生物吸附剂从单金属水溶液中去除铜(II)和镉(II)的机理

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The removal and mechanism of Cu~(2+) and Cd~(2+) from aqueous single-metal solutions were investigated by using a novel biosorbent from waste-activated sludge. A series of adsorption experiments was designed to disclose the effects of the key factors on the adsorption capacity of the biosorbent for the metal ions. The mass ratio of the biosorbent to metal ion was optimized as 2 to balance the adsorption capacity and the removal efficiency. A right shaking speed (150 r/min) not only ensured enough contact frequency between the sorbent and the adsorbate but also reduced the mass transfer resistance. The natural pH value (about 5.5) of the metal solutions benefited a high adsorption capacity of the biosorbent and avoided the consumption of acid or base for pH adjustment. The adsorption reactions belonged to the endothermic process between 15 and 45 °C. As the scanning electron microscopy (SEM) images showed, the meshy structure with long chains and many branches was ideal for the biosorbent to quickly capture the metal ions. The energy-dispersive X-ray (EDX) spectra confirmed that the adsorbed metal ions lay in the precipitates of the adsorption reactions. According to the FTIR analyses, the functional groups responsible for Cu~(2+) adsorption majorly consisted of O-H. N-H, COOH, CONH_2, and the groups containing sulfur and phosphorus, while those for Cd~(2+) adsorption contained O-H, N-H, COOH, and CONH2. The differences in the responsible functional groups explained the phenomenon that the adsorption capacity of the biosorbent for Cu~(2+) was higher than that for Cd~(2+).
机译:利用一种新型的污泥生物吸附剂,研究了单金属水溶液中Cu〜(2+)和Cd〜(2+)的去除机理。设计了一系列吸附实验,以揭示关键因素对生物吸附剂对金属离子的吸附能力的影响。将生物吸附剂与金属离子的质量比优化为2,以平衡吸附容量和去除效率。正确的摇动速度(150 r / min)不仅确保了吸附剂和被吸附物之间足够的接触频率,而且降低了传质阻力。金属溶液的自然pH值(约5.5)有利于生物吸附剂的高吸附能力,并避免了为了调节pH消耗酸或碱。吸附反应属于15至45°C之间的吸热过程。如扫描电子显微镜(SEM)图像所示,具有长链和许多分支的网状结构非常适合生物吸附剂快速捕获金属离子。能量色散X射线(EDX)光谱证实,吸附的金属离子位于吸附反应的沉淀物中。根据FTIR分析,负责Cu〜(2+)吸附的官能团主要由O-H组成。 N-H,COOH,CONH_2和含硫和磷的基团,而Cd〜(2+)吸附的基团包含O-H,N-H,COOH和CONH2。负责的官能团的差异解释了以下现象:生物吸附剂对Cu〜(2+)的吸附能力高于Cd〜(2+)。

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