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Bioremediation of direct dyes in simulated textile effluents by a paramorphogenic form of Aspergillus oryzae

机译:米曲霉的亚型形态对模拟纺织品废水中直接染料的生物修复

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Azo dyes are extensively used for coloring textiles, paper, food, leather, drinks, pharmaceutical products, cosmetics and inks. The textile industry consumes the largest amount of azo dyes, and it is estimated that approximately 10-15% of dyes used for coloring textiles may be lost in waste streams. Almost all azo dyes are synthetic and resist biodegradation, however, they can readily be reduced by a number of chemical and biological reducing systems. Biological treatment has advantages over physical and chemical methods due to lower costs and minimal environmental effect. This research focuses on the utilization of Aspergillus oryzae to remove some types of azo dyes from aqueous solutions. The fungus, physically induced in its paramorphogenic form (called 'pellets'), was used in the dye biosorption studies with both non-autoclaved and autoclaved hyphae, at different pH values. The goals were the removal of dyes by biosorption and the decrease of their toxicity. The dyes used were Direct Red 23 and Direct Violet 51. Their spectral stability (325-700 nm) was analyzed at different pH values (2.50, 4.50 and 6.50). The best biosorptive pH value and the toxicity limit, (which is given by the lethal concentration (LC _(100)), were then determined. Each dye showed the same spectrum at different pH values. The best biosorptive pH was 2.50, for both nonautoclaved and autoclaved hyphae of A. oryzae. The toxicity level of the dyes was determined using the Trimmed Spearman-Karber Method, with Daphnia similis in all bioassays. The Direct Violet 51 (LC _(100) 400 mg·mL ~(-1)) was found to be the most toxic dye, followed by the Direct Red 23 (LC _(100900) mg·mL ~(-1)). The toxicity bioassays for each dye have shown that it is possible to decrease the toxicity level to zero by adding a small quantity of biomass from A. oryzae in its paramorphogenic form. The autoclaved biomass had a higher biosorptive capacity for the dye than the non-autoclaved biomass. The results show that bioremediation occurs with A. oryzae in its paramorphogenic form, and it can be used as a biosorptive substrate for treatment of industrial waste water containing azo dyes.
机译:偶氮染料广泛用于纺织品,纸张,食品,皮革,饮料,药品,化妆品和油墨的着色。纺织工业消耗大量的偶氮染料,据估计,大约10-15%的用于为纺织品着色的染料可能会在废物流中损失。几乎所有的偶氮染料都是合成的,可以抵抗生物降解,但是,可以通过许多化学和生物还原系统将其还原。由于成本较低且对环境的影响最小,生物处理相对于物理和化学方法具有优势。这项研究的重点是利用米曲霉从水溶液中去除某些类型的偶氮染料。以不同形态发生形式(称为“丸粒”)物理诱导的真菌,在不同pH值的条件下,通过非高压灭菌和高压灭菌的菌丝用于染料生物吸附研究。目标是通过生物吸附去除染料并降低其毒性。使用的染料是直接红23和直接紫51。在不同的pH值(2.50、4.50和6.50)下分析了它们的光谱稳定性(325-700 nm)。然后确定最佳的生物吸附pH值和毒性极限(由致死浓度(LC _(100)给出)。每种染料在不同的pH值下显示相同的光谱。对于两种染料,最佳的生物吸附pH为2.50米曲霉的非高压灭菌和高压灭菌的菌丝。染料的毒性水平采用修剪的Spearman-Karber方法,在所有生物测定中均以水蚤进行了测定。直接紫51(LC _(100)400 mg·mL〜(-1 ))被认为是最具毒性的染料,其次是直接红23(LC _(100900)mg·mL〜(-1))。每种染料的毒性生物测定均表明可以降低毒性水平通过添加少量亚型的米曲霉生物量将其降至零。高压灭菌后的生物量对染料的吸附能力高于非高压后的生物量。结果表明,米曲霉以亚型的形式进行了生物修复。 ,并且可以用作治疗梧桐的生物吸附性基质含偶氮染料的试验废水。

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