Lee Young H, Matthews Rosalyn D, Pavlostathis Spyros G
Department of Civil and Environmental Engineering, Stanford University, California, USA.
Water Environ Res. 2006 Feb;78(2):156-69. doi: 10.2175/106143005x89616.
The decolorization of two anthraquinone dyes (Reactive Blue 4 [RB4] and Reactive Blue 19 [RB19]) and two phthalocyanine dyes (Reactive Blue 7 [RB7] and Reactive Blue 21 [RB21]) was investigated at an initial dye concentration of 300 mg/L using an unacclimated, enrichment culture. The culture was fed a mixture of organic compounds and maintained initially under aerobic conditions, and then progressively developed anoxic/ anaerobic conditions. Biotransformation-related decolorization of the dyes did not take place under aerobic conditions, but use of the feed organic mixture and biomass production by the enrichment culture were not affected. Complete ammonia removal occurred in the control and all dye-amended cultures. The development and extent of nitrification were much lower in the latter cultures, in which ammonia removal via air stripping was the dominant mechanism. Prolonged incubation of the culture under anoxic/anaerobic conditions with multiple carbon source additions resulted in a high decolorization extent of anthraquinone dyes (over 84%) and only partial decolorization of phthalocyanine dyes (49 to 66%). Development of significant methanogenic activity took place in the control and, to a lesser extent, in the two phthalocyanine dye-amended cultures, but the anthraquinone dyes severely inhibited the development of methanogenic activity. The RB4 and RB19 decolorization was attributed to nonreversible, microbially mediated dye transformation(s), demonstrated by the accumulation of decolorization products with absorbance maxima in the 420- to 460-nm region. The decolorization of RB4 and RB19 followed Michaelis-Menten kinetics. At an initial dye concentration of 300 mg/L, the observed maximum decolorization rate per unit biomass was 9.1 and 37.5 mg dye/mg volatile suspended solids x day for the RB4 and RB19, respectively. Thus, partial decolorization of reactive phthalocyanine dyes and extensive biological decolorization of reactive anthraquinone dyes is feasible only under anoxic/anaerobic conditions.
使用未驯化的富集培养物,在初始染料浓度为300 mg/L的条件下,研究了两种蒽醌染料(活性蓝4 [RB4]和活性蓝19 [RB19])以及两种酞菁染料(活性蓝7 [RB7]和活性蓝21 [RB21])的脱色情况。向培养物中投喂有机化合物混合物,最初在有氧条件下维持,然后逐渐形成缺氧/厌氧条件。在有氧条件下,染料未发生与生物转化相关的脱色,但投喂的有机混合物的利用和富集培养物的生物质生产未受影响。对照和所有添加染料的培养物中均实现了完全氨去除。在后者的培养物中,硝化作用的发展程度要低得多,其中通过空气吹脱去除氨是主要机制。在缺氧/厌氧条件下,多次添加碳源对培养物进行长时间孵育,导致蒽醌染料的脱色程度较高(超过84%),而酞菁染料仅部分脱色(49%至66%)。对照以及在较小程度上两种添加酞菁染料的培养物中均出现了显著的产甲烷活性,但蒽醌染料严重抑制了产甲烷活性的发展。RB4和RB19的脱色归因于微生物介导的不可逆染料转化,在420至460 nm区域具有最大吸光度的脱色产物的积累证明了这一点。RB4和RB19的脱色遵循米氏动力学。在初始染料浓度为300 mg/L时,对于RB4和RB19,观察到的单位生物量最大脱色率分别为9.1和37.5 mg染料/mg挥发性悬浮固体×天。因此,活性酞菁染料的部分脱色和活性蒽醌染料的广泛生物脱色仅在缺氧/厌氧条件下才可行。