活性污泥
移植
流出物
污水处理
丰度(生态学)
生物
微生物种群生物学
群落结构
污水
生态学
细菌
环境工程
环境科学
医学
外科
遗传学
作者
Giulia Dottorini,Dorottya Sarolta Wágner,Mikkel Stokholm-Bjerregaard,Sergey Kucheryavskiy,Thomas Yssing Michaelsen,Marta Nierychlo,Miriam Peces,Rohan B. H. Williams,Per Henrik Nielsen,Kasper Skytte Andersen,Per Halkjær Nielsen
出处
期刊:Water Research
[Elsevier]
日期:2022-12-03
卷期号:229: 119454-119454
被引量:11
标识
DOI:10.1016/j.watres.2022.119454
摘要
Well-functioning and stable microbial communities are critical for the operation of activated sludge (AS) wastewater treatment plants (WWTPs). Bioaugmentation represents a potentially useful approach to recover deteriorated systems or to support specific AS processes, but its application in full-scale WWTPs is generally problematic. We conducted a massive transplantation (in one day) exchanging AS from a donor to a recipient full-scale WWTP with similar process type (biological removal of nitrogen and phosphorus) and performance, but with differences in microbial community structure. The treatment performance in the recipient plant was not compromised and the effluent quality remained stable. The AS community structure of the recipient plant was initially very similar to the donor AS, but it almost completely restored the pre-transplantation structure approximately 40 days after transplantation, corresponding to 3 times the solid retention time. Most of the unique species of donor AS added to recipient AS disappeared quickly, although some disappeared more slowly the following months, indicating some survival and potentially a time limited function in the recipient plant. Moreover, the addition in higher abundance of most species already present in the recipient AS (e.g., the polyphosphate accumulating organisms) or the reduction of the abundance of unwanted bacteria (e.g., filamentous bacteria) in the recipient plant was not successful. Moreover, we observed similar abundance patterns after transplantation for species belonging to different functional guilds, so we did not observe an increase of the functional redundancy. Investigations of the microbial community structure in influent wastewater revealed that for some species the abundance trends in the recipient plant were closely correlated to their abundance in the influent. We showed that a very resilient microbial community was responsible for the outcome of the transplantation of AS at full-scale WWTP, potentially as a consequence of mass-immigration from influent wastewater. The overall results imply that massive transplantation of AS across different WWTPs is not a promising strategy to permanently solve operational problems. However, by choosing a compatible AS donor, short term mitigation of serious operational problems may be possible.
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