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长期添加 Cu(II)和 Ni(II)对序批式反应器中好氧颗粒生化特性的影响。

Effects of long-term addition of Cu(II) and Ni(II) on the biochemical properties of aerobic granules in sequencing batch reactors.

机构信息

Shandong Key Laboratory of Water Pollution Control and Resource Reuse, School of Environmental Science and Engineering, Shandong University, Jinan, 250100, China.

出版信息

Appl Microbiol Biotechnol. 2010 May;86(6):1967-75. doi: 10.1007/s00253-010-2467-9. Epub 2010 Feb 19.

Abstract

Copper (Cu(II)) and nickel (Ni(II)) are often encountered in wastewaters. This study investigated the individual toxic effects of long-term addition of Cu(II) and Ni(II) on the biochemical properties of aerobic granules in sequencing batch reactors (SBRs). The biochemical properties of aerobic granules were characterized by extracellular polymeric substances (EPS) content, dehydrogenase activity, microbial community biodiversity, and SBR performance. One SBR was used as a control system, while another two received respective concentration of Cu(II) and Ni(II) equal to 5 mg/L initially and increased to 15 mg/L on day 27. Results showed that the addition of Cu(II) drastically reduced the biomass concentration, bioactivity, and biodiversity of aerobic granules, and certainly deteriorated the treatment performance. The toxic effect of Ni(II) on the biodiversity of aerobic granules was milder and the aerobic granular system elevated the level of Ni(II) toxicity tolerance. Even at a concentration of 15 mg/L, Ni(II) still stimulated the biomass yield and bioactivity of aerobic granules to some extent. The elevated tolerance seemed to be owed to the concentration gradient developed within granules, increased biomass concentration, and promoted EPS production in aerobic granular systems.

摘要

铜(Cu(II))和镍(Ni(II))在废水中经常遇到。本研究调查了 Cu(II)和 Ni(II)的长期单独添加对序批式反应器(SBR)中好氧颗粒生化特性的影响。好氧颗粒的生化特性通过胞外聚合物(EPS)含量、脱氢酶活性、微生物群落生物多样性和 SBR 性能进行表征。一个 SBR 用作对照系统,而另外两个系统分别在初始时添加 5 mg/L 的 Cu(II)和 Ni(II),并在第 27 天增加到 15 mg/L。结果表明,Cu(II)的添加大大降低了好氧颗粒的生物量浓度、生物活性和生物多样性,并肯定恶化了处理性能。Ni(II)对好氧颗粒生物多样性的毒性影响较轻,好氧颗粒系统提高了 Ni(II)毒性的耐受水平。即使在 15 mg/L 的浓度下,Ni(II)仍在一定程度上刺激了好氧颗粒的生物量产量和生物活性。这种较高的耐受性似乎归因于颗粒内形成的浓度梯度、生物量浓度的增加以及促进好氧颗粒系统中 EPS 产生。

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