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用于猪场废水处理的厌氧氨氧化反应器中微生物群落动态,包括启动、提高氮负荷和稳定运行阶段

Microbial community dynamics in an ANAMMOX reactor for piggery wastewater treatment with startup, raising nitrogen load, and stable performance.

作者信息

Huang Qiang, Du Wei-Li, Miao Li-Li, Liu Ying, Liu Zhi-Pei

机构信息

State Key Laboratory of Microbial Resources, Institute of Microbiology, Chinese Academy of Sciences, No. 1 West Beichen Road, Chaoyang District, Beijing, 100101, People's Republic of China.

University of Chinese Academy of Sciences, Beijing, 100049, People's Republic of China.

出版信息

AMB Express. 2018 Oct 1;8(1):156. doi: 10.1186/s13568-018-0686-0.

DOI:10.1186/s13568-018-0686-0
PMID:30276499
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC6167272/
Abstract

Bacterial community dynamics of the ANAMMOX reactor of an integrated "UASB + SHARON + ANAMMOX" system for treating piggery wastewater were investigated using the Illumina MiSeq method with samples obtained at ~ 2-week intervals during a 314-day period. With aerobic activated sludge as seeds and low content artificial wastewater (NH-N 50 mg/L; NO-N 55 mg/L) as influent for the ANAMMOX reactor, nitrogen removal was initially observed on day 38 with a removal rate 1.3 mg N L day, and increased to 90.4 mg N L day on day 55 with almost complete removal of ammonia and nitrite, indicating a successful startup of the reactor. Increasing influent load stepwise to NH-N 272.7 mg/L/NO-N 300 mg/L, nitrogen removal rate increased gradually to 470 mg N L day on day 228, and maintained a stable level (~ 420 mg N L day) following introduction of SHARON effluent since day 229. Correlation between microbial community dynamics and nitrogen removal capability was significant (r = 0.489, p < 0.001). Microbial community composition was determined by influent ammonia, influent nitrite, effluent nitrate and some undefined factors. Anammox bacteria, accounting for ~ 98.7% of Planctomycetes, became detectable (0.03% relative abundance) since day 38 and increased to 0.9% on day 58, well consistent with nitrogen removal performance of the reactor. Relative abundance of anammox bacteria gradually increased to 38.4% on day 140 with stepwise increased influent load; decreased to 0.4% on day 169 because of nitrite inhibition; increased to 19.24% on day 233 when the influent load was dropped; kept at ~ 9.0% with SHARON effluent used as influent and dropped to 3.3% finally. Anammox bacteria, only Candidatus Brocadia and Ca. Kuenenia detected, were the most abundant at genus level. Ca. Brocadia related taxa were enriched firstly under low load and detectable during the entire experimental period. Three main groups represented by Ca. Brocadia related OTUs were enriched or eliminated at different loads, but Ca. Kuenenia related taxa were enriched only under high load (NO-N > 300 mg/L), suggesting their different niches and application for different loads. These findings improve the understanding of relationships among microbial community/functional taxa, running parameters and reactor performance, and will be useful in optimizing running parameters for rapid startup and high, stable efficiency.

摘要

采用Illumina MiSeq方法,对一个集成式“UASB+SHARON+ANAMMOX”系统处理猪场废水的厌氧氨氧化(ANAMMOX)反应器中的细菌群落动态进行了研究,该研究在314天内每隔约2周采集一次样本。以好氧活性污泥为种子,以低含量人工废水(NH-N 50mg/L;NO-N 55mg/L)作为ANAMMOX反应器的进水,在第38天首次观察到氮去除,去除率为1.3mg N/L·天,在第55天增加到90.4mg N/L·天,氨和亚硝酸盐几乎完全去除,表明反应器成功启动。逐步将进水负荷增加到NH-N 272.7mg/L/NO-N 300mg/L,氮去除率在第228天逐渐增加到470mg N/L·天,自第229天引入SHARON出水后保持稳定水平(约420mg N/L·天)。微生物群落动态与氮去除能力之间的相关性显著(r=0.489,p<0.001)。微生物群落组成由进水氨、进水亚硝酸盐、出水硝酸盐和一些未定义因素决定。厌氧氨氧化细菌占浮霉菌门的约98.7%,自第38天起可检测到(相对丰度为0.03%),在第58天增加到0.9%,与反应器的氮去除性能高度一致。随着进水负荷逐步增加,厌氧氨氧化细菌的相对丰度在第140天逐渐增加到38.4%;由于亚硝酸盐抑制,在第169天降至0.4%;当进水负荷下降时,在第233天增加到19.24%;以SHARON出水为进水时保持在约9.0%,最终降至3.3%。仅检测到“Candidatus Brocadia”和“Ca. Kuenenia”属的厌氧氨氧化细菌,在属水平上最为丰富。与“Ca. Brocadia”相关的分类单元在低负荷下首先富集,并且在整个实验期间均可检测到。以与“Ca. Brocadia”相关的操作分类单元(OTUs)为代表的三个主要组在不同负荷下富集或消除,但与“Ca. Kuenenia”相关的分类单元仅在高负荷(NO-N>300mg/L)下富集,表明它们具有不同的生态位以及适用于不同的负荷。这些发现增进了对微生物群落/功能分类单元、运行参数和反应器性能之间关系的理解,并将有助于优化运行参数以实现快速启动和高效稳定运行。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/da04/6167272/8ad8d6f21376/13568_2018_686_Fig6_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/da04/6167272/d6dda50936dd/13568_2018_686_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/da04/6167272/f479339351dd/13568_2018_686_Fig2_HTML.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/da04/6167272/1a858bd00dae/13568_2018_686_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/da04/6167272/8ec66eb5412e/13568_2018_686_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/da04/6167272/8ad8d6f21376/13568_2018_686_Fig6_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/da04/6167272/d6dda50936dd/13568_2018_686_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/da04/6167272/f479339351dd/13568_2018_686_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/da04/6167272/bf7ab618babd/13568_2018_686_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/da04/6167272/1a858bd00dae/13568_2018_686_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/da04/6167272/8ec66eb5412e/13568_2018_686_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/da04/6167272/8ad8d6f21376/13568_2018_686_Fig6_HTML.jpg

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