Boundary conditions for exploiting the cooperation of Aminobacter niigataensis MSH1 with Piscinibacter sp. K169 to support 2,6-dichlorobenzamide biodegradation in sand filters for drinking water treatment: role of cell density and organic carbon.

IF 3.7 2区 生物学 Q2 BIOTECHNOLOGY & APPLIED MICROBIOLOGY
Siyao Du, Aura Wouters, Manon Glorieux, Laurien van Lieshout, Benjamin Horemans, Dirk Springael
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引用次数: 0

Abstract

Aminobacter niigataensis MSH1 mineralizes the groundwater micropollutant 2,6-dichlorobenzamide (BAM) and is a candidate for bioaugmentation of sand filters in drinking water treatment plants (DWTP) to avert BAM-contamination. Piscinibacter sp. K169 is a sand filter isolate that improves MSH1-mediated BAM mineralization through a cooperative interaction, and co-inoculation of MSH1 with K169 is proposed as a strategy to support bioaugmentation with MSH1. In this study, boundaries regarding the initial population size and the supply of organic carbon resources determining the interaction between MSH1 and K169 in sand filter microcosms were explored. The cooperative interaction was only disturbed when initial cell densities of one of the two partners were 104 cells/mL or lower. Supplying acetate as a carbon source appeared redundant for supporting BAM mineralization. Instead, the organic carbon present on the sand drove the cooperative interaction between K169 and MSH1 as the effect of K169 on BAM mineralization disappeared, and none of the two strains showed growth in sand devoid from organic carbon. These findings highlight the feasibility of K169-assisted bioaugmentation with MSH1 under realistic field conditions, as it requires no supplementary organic carbon and remains effective, even at relatively low inoculum densities, thereby addressing key challenges in bioaugmentation strategies.IMPORTANCEBioaugmentation of sand filters exploited in drinking water treatment, with the BAM catabolic strain Aminobacter niigataensis MSH1, has previously been successful during the first 1-2 weeks, where after BAM degradation deteriorated together with the loss of MSH1 cell density and cell activity. Bacterial isolates obtained from sand filters can support BAM degradation activity by MSH1 involving mutualistic interactions which resulted in the proposition of a novel bioaugmentation approach involving the co-inoculation of "support" bacteria that are adapted to the target environment. This paper focuses on understanding the boundary conditions required for sustaining the mutualistic interaction between MSH1 and such a "supportive" sand filter isolate in sand microcosm, showing that the interaction could be maintained when using relatively low cell densities and with no additional carbon supplemented. To the best of our knowledge, this paper is the first study to examine the boundary conditions of a bacterial mutualistic interaction, particularly in a bioaugmentation context of water treatment.

利用niigataensis MSH1与Piscinibacter sp. K169协同作用支持饮用水处理砂过滤器中2,6-二氯苯酰胺生物降解的边界条件:细胞密度和有机碳的作用
新塔台氨基杆菌MSH1矿化地下水微污染物2,6-二氯苯甲酰胺(BAM),是饮用水处理厂(DWTP)砂过滤器生物强化以避免BAM污染的候选者。Piscinibacter sp. K169是一种沙滤分离物,通过协同相互作用改善MSH1介导的BAM矿化,MSH1与K169共接种被认为是支持MSH1生物增强的策略。本研究探讨了砂滤微环境中MSH1与K169相互作用的初始种群大小和有机碳资源供应边界。只有当两个伙伴中的一个初始细胞密度为104个细胞/mL或更低时,合作相互作用才会受到干扰。提供醋酸盐作为碳源对于支持BAM矿化显得多余。相反,随着K169对BAM矿化的影响消失,K169与MSH1之间的协同作用被K169驱动,两株菌株在缺乏有机碳的沙土中均未生长。这些发现强调了在现实的野外条件下,k169辅助MSH1生物强化的可行性,因为它不需要补充有机碳,即使在相对较低的接种密度下也保持有效,从而解决了生物强化策略中的关键挑战。在饮用水处理中,利用BAM分解代谢菌株niigataaminobacter niigataensis MSH1对砂过滤器进行生物强化处理,在最初的1-2周内取得了成功,在此期间,BAM降解恶化,MSH1细胞密度和细胞活性下降。从沙子过滤器获得的细菌分离物可以通过相互作用支持MSH1降解BAM的活性,这导致了一种新的生物增强方法的提出,该方法涉及共同接种适应目标环境的“支持”细菌。本文的重点是了解在沙子微观世界中维持MSH1与这种“支持性”砂过滤器分离物之间相互作用所需的边界条件,表明在使用相对较低的细胞密度和不补充额外碳的情况下,相互作用可以维持。据我们所知,这篇论文是第一个研究细菌共生相互作用的边界条件的研究,特别是在水处理的生物增强环境中。
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来源期刊
Applied and Environmental Microbiology
Applied and Environmental Microbiology 生物-生物工程与应用微生物
CiteScore
7.70
自引率
2.30%
发文量
730
审稿时长
1.9 months
期刊介绍: Applied and Environmental Microbiology (AEM) publishes papers that make significant contributions to (a) applied microbiology, including biotechnology, protein engineering, bioremediation, and food microbiology, (b) microbial ecology, including environmental, organismic, and genomic microbiology, and (c) interdisciplinary microbiology, including invertebrate microbiology, plant microbiology, aquatic microbiology, and geomicrobiology.
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