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Heavy-metal removal from aqueous solution by fungus Mucor rouxii

机译:真菌Mucor rouxii从水溶液中去除重金属

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Biosorption of lead, cadmium, nickel and zinc by live and dead Mucor rouxii biomass treated with NaOH was studied over a range of pH. In the case of dead biomass, low pH resulted in a decrease in the biosorption capacity. At pH 3.0 or less, the inhibition of biosorption of metal ions took place. At pH 4.0 or higher, the biosorption of metal ions increased sharply. Ho's pseudo-second-order model described the biosorption kinetics better than the Lagergren model. Live biomass had high biosorption capacity, i.e. 35.69, 11.09, 8.46 and 7.75 mg/g at pH 5.0 for Pb~(2+), Ni~(2+), Cd~(2+) and Zn~(2+), respectively. The dead biomass adsorbed metal ions in the order of Pb~(2+), Zn~(2+), Cd~(2+) and Ni~(2+), with the biosorption capability of 25.22, 16.62, 8.36 and 6.34 mg/g at pH 5.0, respectively. At pH 6.0, the capacity of the dead biomass increased to 53.75, 53.85, 20.31 and 20.49 mg/g, respectively. For bi- or multi-metal ion adsorption, biosorption capacity of individual metal ion was reduced in the presence of other metal ions, but the total biosorption capacity increased, indicating the capability of M. rouxii biomass in adsorbing multi-metal ions. In addition, M. rouxii biomasses cultured with different media exhibited the same level of capacity to bind metal ions. Metal ions adsorbed by the biomass could be eluted effectively with HNO_3, while distilled water demonstrated negligible metal elution capability. Regeneration of the biomass with NaOH regained or enhanced the biosorption capacity even after five cycles of adsorption-elution-regeneration.
机译:在一定的pH范围内,研究了用NaOH处理的生死Mucor rouxii生物质对生铅和镉的吸附,包括铅,镉,镍和锌。在死生物质的情况下,低pH导致生物吸附能力下降。在pH 3.0或更低时,发生了金属离子生物吸附的抑制。在pH 4.0或更高时,金属离子的生物吸收急剧增加。 Ho的伪二级模型比Lagergren模型更好地描述了生物吸附动力学。活生物质在pH 5.0时对Pb〜(2 +),Ni〜(2 +),Cd〜(2+)和Zn〜(2+)具有较高的生物吸附能力,分别为35.69、11.09、8.46和7.75 mg / g,分别。死生物质以Pb〜(2 +),Zn〜(2 +),Cd〜(2+)和Ni〜(2+)的顺序吸附金属离子,生物吸附能力分别为25.22、16.62、8.36和6.34。分别在pH 5.0下为mg / g。在pH 6.0时,死生物量的容量分别增加到53.75、53.85、20.31和20.49 mg / g。对于双金属或多金属离子吸附,在存在其他金属离子的情况下单个金属离子的生物吸附能力降低,但总生物吸附能力增加,这表明鲁氏甲烷八叠球菌生物质吸附多金属离子的能力。另外,用不同培养基培养的鲁氏甲烷八叠球菌生物质表现出相同水平的结合金属离子的能力。 HNO_3可以有效地洗脱生物质吸附的金属离子,而蒸馏水的金属洗脱能力可以忽略不计。即使经过五个吸附-洗脱-再生循环,使用NaOH进行的生物质再生也可以恢复或增强生物吸附能力。

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