呼吸器用活性炭掺杂金属的参数优化

A. Farooq, Asif Raza Sheikh, Masroor Ahmad, N. Irfan
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引用次数: 0

摘要

为了从污水流中去除不同的污染物,必须选择具有相当吸附倾向的合适材料。活性炭(AC)被认为是实现这一目标的最佳人选。本研究的核心目标是通过在不同介质(碱性和中性)中使用不同的盐浸渍活性炭表面的特定金属,提高活性炭对低分子量和高挥发性气体的吸附能力。浸渍法采用吸限浸渍法,注入少量浸渍液后,搅拌时间约为1分钟。浸渍剂的最终形式是氧化物或硫酸盐,而氧化物是理想的形式,因为在这种形式的浸渍剂中,样品不需要在高温下加热以去除挥发物或煅烧物。样品的质量随温度升高的变化表明,在160℃时,活性炭表面的煅烧物被去除。BET表面积分析得到的信息是,浸渍后活性炭的可用孔隙值没有太大的变化,这与以往的研究相反。原子吸收光谱结果证实,与在中性介质中浸渍相比,在碱性介质中掺杂金属使AC表面获得了相对较高浓度的金属锌。此外,在碱性(氨溶液)介质中氧化锌的最佳浓度为1.17 M,在中性介质中氧化锌的最佳浓度为0.4 M,样品加热去除挥发物的最佳温度为160℃。氧化锌的峰在低温时不明显,但当样品温度升高到450℃时,氧化锌的峰明显,结果与文献吻合较好。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Optimization of parameters for doping of metals on activated carbon for respirator applications
To remove different contaminants from an effluent waste stream, it is imperative that a suitable material having considerable adsorption tendency must be selected. Activated carbon (AC) is considered as the best candidate to accomplish this goal. Core objective of this work is to enhance capability of activated carbon to adsorb gases of low molecular weight and high volatility by impregnating specific metals on the surface of activated carbon using various salts in different medium i.e. basic and neutral. Imbibing limit is used as the method of impregnation and shaking time is nearly one minute after introducing few drops of impregnating solution. Final form of impregnant is either oxide or sulphate while oxide is the desirable form because in this form of impregnant, the sample needs not to be heated at elevated temperatures to remove volatiles or calciners. Mass variations of samples with rise in temperature give clue that at 160 °C calciners are removed from the surface of activated carbon. BET surface area analysis gives information that after impregnation there is no considerable change in the value of available pores of activated carbon, which is contrary to previous research. AAS results confirm that metal doping in alkaline medium has imparted a comparatively higher concentration of zinc metal to the AC surface as compared to impregnation in neutral medium. In addition, optimized concentration of zinc oxide in alkaline (ammonia solution) medium was 1.17 M of zinc oxide and in neutral medium it is 0.4 M. Optimized temperature to heat the sample to remove volatiles is 160 °C. Peaks of zinc oxide are not prominent at low temperature, nevertheless when temperature of sample is raised up to 450 °C, the peaks become prominent and the results match well with available literature.
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