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首页> 外文期刊>Water research: A journal of the international water association >Double-edged sword effects of dissimilatory nitrate reduction to ammonium (DNRA) bacteria on anammox bacteria performance in an MBR reactor
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Double-edged sword effects of dissimilatory nitrate reduction to ammonium (DNRA) bacteria on anammox bacteria performance in an MBR reactor

机译:异化硝酸盐还原为铵(DNRA)细菌对MBR反应器厌氧氨氧化细菌性能的双刃剑效应

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Dissimilatory nitrate reduction to ammonium (DNRA) bacteria imposing double-edged sword effects on anammox bacteria were investigated in an anammox-membrane bioreactor (MBR) experiencing an induced crashrecovery event. During the experiment, the anammox-MBR was loaded with NII4+-N:NO2---N ratios (RatioNII(4)(+)-N:NO2---N) of 1.20-1.60. Initially, the anammox-MBR removed over 95 of 100 mg/L NH4+-N and 132 mg/L NO2---N (RatioNH4+-N: NO2---N-N = 0.76, the well accepted stoichiometric RatioNH(4)(+)-N: NO2-#-N for anammox) in the influent (Stage 0). Then, we induced a system crash-recovery event via nitrite shock loadings to better understand responses from different guilds of bacteria in anammox-MBR, loaded with 1.60 RatioNII(4)(+)-N:NO2---N with 100 mg/L NO2--N in the influent (Stage 1). Interestingly, the nitrogen removal by anammox bacteria was maintained for about 20 days before starting to decrease significantly. In Stage 2, we further increased influent nitrite concentration to 120 mg/L (1.33 RatioNII(4)(+)-N: NO2- -N) to simulate a high nitrite toxicity scenario for a short period of time. As expected, nitrogen removal efficiency dropped to only 16.8. After the induced system crash, anammox-MBR performance recovered steadily to 93.2 nitrogen removal with a 1.25 RatioNH4+-N:NO2--N and a low nitrite influent concentration of 80 mg/L NO2--N. Metagenomics analysis revealed that a probable causality of the decreasing nitrogen removal efficiency in Stage 1 was the overgrowth of DNRA-capable bacteria. The results showed that the members within the Ignavibacteriales order (21.7) out competed anammox bacteria (17.0) in the anammox-MBR with elevated nitrite concentrations in the effluent. High NO2--N loading (120 mg N/L) further caused the predominant Candidatus Kuenenia spp. were replaced by Candidatus Brocadia spp. Therefore, it was evident that DNRA bacteria posed negative effects on anammox with 1.60 RatioNH(4)(+)-N: NO2--N. Also, when 120 mg/L NO2--N fed to anammox-MBR (RatioNH(4)(+)-N: NO2--N = 1.33), canonical denitrification became the primary nitrogen sink with both DNRA and anammox activities decreased. They probably fed on lysed microbial cells of anammox and DNRA. In Stage 3, a low RatioNH(4)(+)-N: NO2--N (1.25) with 80 mg/L NO2--N was used to rescue the system, which effectively promoted DNRA-capable bacteria growth. Although anammox bacteria's abundance was only 7.7 during this stage, they could be responsible for about 90 of the total nitrogen removal during this stage.
机译:在厌氧氨氧化膜生物反应器(MBR)中研究了异化硝酸盐还原为铵(DNRA)细菌对厌氧氨氧化细菌施加双刃剑效应,该反应器经历了诱导的崩溃恢复事件。实验过程中,厌氧氨氧化-MBR负载的NII4+-N:NO2---N比值(RatioNII(4)(+)-N:NO2---N)为1.20-1.60。最初,厌氧氨氧化-MBR去除了进水(第0阶段)中超过95%的100 mg/L NH4+-N和132 mg/L NO2---N(RatioNH4+-N: NO2---N-N = 0.76,公认的化学计量比NH(4)(+)-N:厌氧氨氧化的NO2-#-N)。然后,我们通过亚硝酸盐冲击载荷诱导系统崩溃恢复事件,以更好地了解厌氧氨氧化-MBR中不同细菌行列的反应,在进水中加载1.60 RatioNII(4)(+)-N:NO2---N,NO2--N(第1阶段)。有趣的是,厌氧氨氧化细菌的氮去除率维持了大约20天,然后才开始显着下降。在第 2 阶段,我们进一步将进水亚硝酸盐浓度提高到 120 mg/L(1.33 RatioNII(4)(+)-N: NO2- -N),以模拟短时间内的高亚硝酸盐毒性情景。不出所料,脱氮效率下降到只有16.8%。在诱导系统崩溃后,厌氧氨氧化-MBR性能稳步恢复到93.2%,NH4+-N:NO2--N比值为1.25,亚硝酸盐进水浓度为80 mg/L NO2--N。宏基因组学分析显示,第一阶段氮去除效率下降的一个可能的因果关系是具有DNRA能力的细菌的过度生长。结果表明,在厌氧氨氧化-MBR中,与厌氧氨氧化菌目(21.7%)的成员(17.0%)竞争,出水中亚硝酸盐浓度升高。高NO2--N负荷量(120 mg N/L)进一步导致占主导地位的Candidatus Kuenenia属被Candidatus Brocadia spp.取代。因此,很明显,DNRA细菌对氮氧氨氧化的负面影响为1.60 RatioNH(4)(+)-N: NO2--N。此外,当120 mg/L NO2--N进料到厌氧氨氧化-MBR中时(RatioNH(4)(+)-N: NO2--N = 1.33),典型反硝化作用成为主要的氮汇,DNRA和厌氧氨氧化活性均降低。他们可能以厌氧氨氧化和DNRA的裂解微生物细胞为食。在第3阶段,采用低比例的NH(4)(+)-N:NO2--N(1.25)和80 mg/L NO2--N来拯救系统,有效促进了DNRA细菌的生长。虽然厌氧氨氧化细菌的丰度在这个阶段只有7.7%,但它们可能负责这个阶段约90%的总氮去除。

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