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Effect of 3-Chloroaniline in Microbial Community Structure of Activated Sludge

机译:3-氯苯胺对活性污泥微生物群落结构的影响

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Present work evaluated the effects on activated-sludge reactor functions of a 3-chloroaniline (3-CA) pulse and bioaugmentation by inoculation with the 3-CA-degrading strain Pseudomonas stuzeri. Changes in functions such as nitrification, carbon removal, and sludge compaction were studied in relation to the sludge community structure, in particular the nitrifying populations. Denaturing gradient gel electrophoresis (DGGE), real-time PCR, and fluorescent in situ hybridization (FISH) were used to characterize and enumerate the ammonia-oxidizing microbial community immediately after a 3-CA shock load. Two days after the 3-CA shock, ammonium accumulated, and the nitrification activity did not recover over a 12-day period in the non bioaugmented reactors. In contrast, nitrification in the bioaugmented reactor started to recover on day 4. The DGGE patterns and the FISH and real-time PCR data showed that the ammonia-oxidizing microbial community of the bioaugmented reactor recovered in structure, activity, and abundance, while the number of ribosomes of the ammonia oxidizers in the nonbioaugmented reactor decreased drastically and the community composition changed and did not recover. The settle ability of the activated sludge was negatively influenced by the 3-CA addition, with the sludge volume index increasing by a factor of 2.3. Two days after the 3-CA shock in the non bioaugmented reactor, chemical oxygen demand (COD) removal efficiency decreased by 36% but recovered fully by day 4. In contrast, in the bioaugmented reactor, no decrease of the COD removal efficiency was observed. This study demonstrates that bioaugmentation of wastewater reactors to accelerate the degradation of toxic chlorinated organic such as 3-CA protected the nitrifying bacterial community, thereby allowing faster recovery from toxic shocks.
机译:目前的工作评估了3-氯苯胺(3-CA)脉冲对活性污泥反应器功能的影响以及接种3-CA降解菌株假单胞菌Pseudomonas stuzeri的生物强化作用。研究了诸如硝化,除碳和污泥压实等功能的变化与污泥群落结构,尤其是硝化种群的关系。变性梯度凝胶电泳(DGGE),实时PCR和荧​​光原位杂交(FISH)用于表征和枚举3-CA冲击负荷后的氨氧化微生物群落。 3-CA震荡两天后,在非生物强化反应器中,铵积累了12天,但铵离子的积累和硝化活性未恢复。相反,生物强化反应器中的硝化作用从第4天开始恢复。DGGE模式以及FISH和实时PCR数据表明,生物强化反应器的氨氧化微生物群落在结构,活性和丰度上均得到恢复,而非生物强化反应器中氨氧化剂的核糖体数量急剧减少,群落组成发生变化,无法恢复。 3-CA的添加对活性污泥的沉降能力产生了负面影响,污泥体积指数增加了2.3倍。在非生物强化反应器中发生3-CA冲击后两天,化学需氧量(COD)去除效率下降了36%,但到第4天已完全恢复。相反,在生物强化反应器中,未观察到COD去除效率下降。 。这项研究表明,废水反应器的生物增强作用可加速有毒氯化有机物(如3-CA)的降解,从而保护硝化细菌群落,从而使有毒休克的恢复更快。

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