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Recovery of zero-valent ruthenium from acetic acid waste solution by a combined process of biosorption with bacterial biosorbent fibers and incineration

机译:通过用细菌生物吸附纤维的生物吸附的组合过程从醋酸废液中恢复零价钌,并焚烧

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This study introduces a new process for the recovery of zero-valent ruthenium (Ru) from acetic acid waste solution by a combined process of biosorption with bacterial biosorbent fibers and incineration. As an effective sorbent to bind Ru-acetate complexes, polyethylenimine (PEI)- modified bacterial biosorbent fibers (PBBF) were developed and used for the experiments. The PBBF were prepared by extruding the blended mixture of chitosan-Corynebacterium glutamicum biomass as a fiber, coating the fiber with PEI and cross-linked using glutaraldehyde, consecutively. The role of chitosan in the bacterial biosorbent fiber was binder of the biomass. Batch biosorption studies showed that the maximum Ru uptakes of raw biomass and PBBF were estimated to be 16.0 and 110.5 mg/g, respectively. Kinetic studies showed that PBBF was as fast as powder form of raw biomass. After biosorption, the Ru-acetate complexes ions sorbed biosorbents were incinerated for recover Ru as a metallic form. These biosorbent constituents could be burnt out and at the same time, the sorbed Ru-acetate complexes ions could be reduced to Ru0. X-ray photoelectron spectroscopy (XPS) results indicated that the Ru-acetate complexes ions were able to be reduced into metallic form of zero-valent Ru. X-ray fluorescence spectrometry (XRF) was applied for analysis of impurity metals in the recovered Ru containing ashes. The purity of metallic Ru by means of XRF was 99.79%. The proposed sequential process of biosorption and incineration for recovery of Ru from acetic acid waste solution would contribute to the solution of several problems such as the Ru recovery efficiency, generation of secondary waste, and recover costs and energy.
机译:本研究介绍了通过使用细菌生物吸附纤维的生物吸附的组合过程和焚烧从乙酸废液中恢复零价钌(Ru)的新方法。作为结合Ru-醋酸络合物的有效吸附剂,产生聚对乙基(PEI)改性的细菌生物吸附纤维(PBBF)并用于实验。通过挤出壳聚糖 - 棒状杆菌生物量作为纤维的混合混合物来制备PBBF,用PEI涂覆纤维并连续地用戊二醛交联。壳聚糖在细菌生物吸附纤维中的作用是生物质的粘合剂。分批生物吸附研究表明,原料生物量和PBBF的最大Ru将估计分别为16.0和110.5mg / g。动力学研究表明,PBBF与原料生物质的粉末形式一样快。生物吸附后,将Ru-乙酸盐复合物离子被吸附的生物吸水剂作为金属形式回收Ru。这些生物吸附成分可以烧坏,同时,可以将吸附的Ru-乙酸盐络合物离子降至Ru0。 X射线光电子能谱(XPS)结果表明,Ru-醋酸络合物离子能够减少到零价ru的金属形式中。 X射线荧光光谱法(XRF)被施加用于含有灰烬中回收的Ru中的杂质金属的分析。通过XRF金属Ru的纯度为99.79%。从乙酸废物溶液中提出的生物吸附和焚烧的序列过程将有助于解决若干问题,例如RU回收效率,二次浪费的产生和恢复成本和能量。

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