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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

Postal Subscription Code 80-973

2018 Impact Factor: 3.883

Front. Environ. Sci. Eng.    2023, Vol. 17 Issue (10) : 122    https://doi.org/10.1007/s11783-023-1722-0
RESEARCH ARTICLE
Differences in distributions, assembly mechanisms, and putative interactions of AOB and NOB at a large spatial scale
Bing Zhang1,2, Chenxiang Sun2, Huimin Lin1, Wei Liu2, Wentao Qin2,3, Tan Chen1, Ting Yang1, Xianghua Wen2()
1. College of Life and Environmental Sciences, Minzu University of China, Beijing 100081, China
2. Environmental Simulation and Pollution Control State Key Joint Laboratory, School of Environment, Tsinghua University, Beijing 100084, China
3. Institute of Plant Protection, Beijing Academy of Agriculture and Forestry Sciences, Beijing 100097, China
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Abstract

● Nitrifiers in WWTP were investigated at large spatial scale.

● AOB populations varied greatly but NOB populations were similar among cities.

● Drift dominated both AOB and NOB assembling processes.

● DO did not show a significant effect on NOB.

● NOB tended to cooperate with AOB and non-nitrifying microorganisms.

Ammonia-oxidizing bacteria (AOB) and nitrite-oxidizing bacteria (NOB) play crucial roles in removing nitrogen from sewage in wastewater treatment plants (WWTPs) to protect water resources. However, the differences in ecological properties and putative interactions of AOB and NOB in WWTPs at a large spatial scale remain unclear. Hence, 132 activated sludge (AS) samples collected from 11 cities across China were studied by utilizing 16S rRNA gene sequencing technology. Results indicated that Nitrosomonas and Nitrosospira accounted for similar ratios of the AOB community and might play nearly equal roles in ammonia oxidation in AS. However, Nitrospira greatly outnumbered other NOB genera, with proportions varying from 94.7% to 99.9% of the NOB community in all WWTPs. Similar compositions and, hence, a low distance–decay turnover rate of NOB (0.035) across China were observed. This scenario might have partly resulted from the high proportions of homogenizing dispersal (~13%). Additionally, drift presented dominant roles in AOB and NOB assembling mechanisms (85.2% and 81.6% for AOB and NOB, respectively). The partial Mantel test illustrated that sludge retention time and temperature were the primary environmental factors affecting AOB and NOB communities. Network results showed that NOB played a leading role in maintaining module structures and node connections in AS. Moreover, most links between NOB and other microorganisms were positive, indicating that NOB were involved in complex symbioses with bacteria in AS.

Keywords Activated sludge      Spatial distributions      Microbial assembly      Co-occurrence patterns      Nitrifying bacteria     
Corresponding Author(s): Xianghua Wen   
About author:

*These authors equally shared correspondence to this manuscript.

Issue Date: 28 April 2023
 Cite this article:   
Bing Zhang,Chenxiang Sun,Huimin Lin, et al. Differences in distributions, assembly mechanisms, and putative interactions of AOB and NOB at a large spatial scale[J]. Front. Environ. Sci. Eng., 2023, 17(10): 122.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-023-1722-0
https://academic.hep.com.cn/fese/EN/Y2023/V17/I10/122
Fig.1  Occurrence of nitrifying bacteria populations in WWTPs at different spatial scales. (a) AOB populations across China; (b) NOB populations across China; (c) compositions of the main AOB populations at the city level; (d) compositions of the main NOB populations at the city level. Abbreviations for the sampled cities: BJ for Beijing, DL for Dalian, HB for Harbin, JN for Jinan, QD for Qingdao, XA for Xi’an, CD for Chengdu, CQ for Chongqing, CS for Changsha, SZ for Shenzhen, and XM for Xiamen.
Fig.2  The distance–decay pattern of AOB and NOB across China. The blue dots and orange dots represent AOB and NOB, respectively. The blue line represents the linear regression for AOB (y = −0.0918x −0.2879; r = 0.25; P < 0.001). The orange line represents the linear regression for NOB (y = −0.0692x −0.4221; r = 0.13; P < 0.001).
Fig.3  Assembling processes of nitrifiers in AS. DR, HeS, HoS, DL, and HD represent drift, heterogeneous selection, homogeneous selection, dispersal limitation, and homogeneous dispersal, respectively.
Fig.4  Correlation analysis between environmental factors and the whole AOB/NOB community in AS based on partial Mantel test. Each line indicates a correlation between AOB/NOB and each environmental factor. Line width corresponds to the partial Mantel’s r value, and the edge color denotes the statistical significance. Pairwise correlations among these environmental factors are shown with a color gradient denoting Pearson’s correlation coefficient. TMLSS, temperature of AS; Cond., conductivity in the aeration tank; Inf., influent.
Fig.5  Ecological network in AS where nodes are colored based on taxonomy. The size of a node is scaled by its node degree. The red links between nodes indicate significant negative correlations, whereas the blue links between nodes indicate significant positive correlations.
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