The selective pressure of quorum quenching on microbial communities in membrane bioreactors
Graphical abstract
Introduction
Membrane biofouling has been recognized as the most challenging issue in membrane bioreactor (MBR) technology, due to its strong undesirable effects such as membrane clogging, fast trans-membrane pressure (TMP) build-up, low treatment efficiency and high energy demands (Lee et al., 2014; Vrouwenvelder et al., 2008). Various measures such as changing hydro-dynamical parameters (aeration rate and air diffuser position, relaxation/filtration mode and backwashing), pre-treatment of feed by coagulation/flocculation, chemical cleaning, membrane surface conditioning, and modifications in reactor design and filtration modes, have been attempted to mitigate membrane biofouling (Kobayashi et al., 2003; Liu et al., 2010; Yang et al., 2013). However, no significant progress had been made until the quorum quenching (QQ)-based biofouling control technology emerged a decade ago. This biological approach retards biocake formation via disrupting bacteria social communication, i.e. quorum sensing, and thus reducing the production of extracellular polymeric substances (EPS) – the backbone providing structural properties and mechanical strength of biofilms – in biocake. Since the first demonstration of its feasibility by Yeon et al. (2009), this technology has attracted extensive attention over the last decade (Oh and Lee, 2018).
Application of a single QQ bacterial strain such as Rhodococcus BH4, or a QQ consortium in disrupting the quorum sensing (QS) mechanism at lab-scale MBRs has been extensively investigated and proved to be effective in MBR systems (Kim et al., 2013; Maqbool et al., 2015; Oh et al., 2012; Waheed et al., 2017; Xiao et al., 2018). Moreover, the composition of bacteria-entrapping media and their geometric structure have been continuously modified to enhance their durability at large scale applications (Iqbal et al., 2018; Kim et al., 2015; Lee et al., 2016; Nahm et al., 2017). Most of these studies have been limited to target the acyl-homoserine lactone (AHL) -based QS, which is known to regulate the Gram-negative bacterial populations only. This regulation may affect the relative distribution of Gram-positive and -negative bacteria in QQ-MBR. However, this has rarely been reported in the literature, except that Jo et al. (2016) observed a lower abundance of Gram-negative phylum/genus e.g. Proteobacteria and Thiothrix sp. in the biofilm of a QQ MBR than a conventional MBR. Hence, it is expected that in QQ-MBRs, a selective pressure is created to favor the growth of Gram-positive bacteria, resulting in distinct microbial community structures in both bulk sludge and biocake from those in conventional MBRs. Therefore, one of the objectives of this study was to investigate the selective accumulation of Gram-positive bacteria in QQ-MBRs.
Most of the QQ related studies monitored the changes in EPS contents and QS signal molecule levels in the sludge, but overlooked the impacts of several other factors such as sludge microbial ecology, sludge physicochemical properties and soluble microbial products (SMPs). In addition to the similar role of EPS in determining sludge hydrophobicity, surface charge, adhesion and flocculation ability, and thus affecting biofouling indirectly, SMPs also contribute to the membrane fouling directly and have been considered as a major (26–52%) organic foulant (Bouhabila et al., 2001; Liang et al., 2007). However, the role of these factors and their possible variations under QQ conditions are far from completely understood. It was, therefore, our second objective to understand the changes of key sludge components, sludge properties and microbial composition due to the quorum quenching phenomenon.
Overall, the objectives of the present study were to i) check the biofouling control potential of an AHL- and AI-2 degrading QQ consortium, ii) investigate the role of EPS in sludge filterability and membrane fouling, and iii) examine microbial responses to the QQ. To this end, a consortium of QQ bacteria with overlapping potential to mineralize various signal molecules, immobilized in a modified alginate-polysulfone mixture, was applied in a lab-scale MBR system. The QQ effects on biocake and mixed liquor were explored in terms of sludge dewaterability, settleability, microbial activity, floc size, production of SMPs and EPS. The microbial abundance and composition in mixed liquor, biocake and the immobilizing media were also investigated. This study is the first of this type to comprehensively examine the impacts of QQ on microbial ecology and highlights the overlooked microbial response.
Section snippets
Selection & immobilization of the QQ consortium
The QQ consortium comprising of four AHLs-degrading strains Rhodococcus BH4, Enterobacter cloaca QQ13, Microbacterium sp. QQ1 and Pseudomonas sp. QQ3, and one AI-2 degrading Escherichia coli strain ΔlsrRΔluxS (Thompson et al., 2015) had been used in our previous studies (Waheed et al., 2017; Xiao et al., 2018). QQ bacteria-immobilizing beads were prepared with a method modified from previous reports (Kim et al., 2013; Maqbool et al., 2015; Oh et al., 2012). Briefly, optimized concentrations of
Effects of quorum quenching on fouling control/filtration cycle
The trans-membrane pressure (TMP) rise is an important indicator of MBR performance, and each operation cycle was terminated when TMP values reached 30 kPa. As shown in Fig. 1a, the membrane in MBR-C fouled after 10 days of operation, whereas vacant beads along with backwash (MBR-Vb) increased the filtration cycle by ∼ 50%. Addition of QQ consortium further reduced the fouling rate by ∼78% and increased the filtration time by 3.5 times in MBR-QQb. The TMP profile of MBR-QQb clearly indicates
Conclusions
The research work aimed at addressing the selective accumulation of microbial communities and altered sludge characteristics through quorum quenching mechanism. The major conclusions are as follows:
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Addition of the QQ consortium increased the filtration time by 3.5 times in MBR-QQb.
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QQ activity was the dominant factor regulating bound EPS composition and quantity, and floc size in MBR-QQb. The endless ‘battle’ between QS and QQ resulted in a larger variation in EPS content and floc size in
Acknowledgments
This research was jointly supported by the Key-Area Research and Development Program of Guangdong Province, China (No.: 2019B110205001), the National Natural Science Foundation of China (No.: 51750110514), Shantou University Scientific Research Foundation for Talents (No.: NTF16015), the International Research Support Initiative Program of Higher Education Commission (HEC), Pakistan (IRSIP-29 BMS 39), Environment & Water Industry Programme Office of Singapore (EWIM4095030), and Nanyang
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2022, Microbiological ResearchCitation Excerpt :The aggregated microbes and their products form a three-dimension biocake or biofilm, and this product can block the pores of the membranes to reduce membrane permeability, resulting in membrane biofouling and lowering the efficiency of the wastewater treatment. AHLs are known to play an important role in regulating the formation of biofilm on the membranes of bioreactors in MBR (Gamage et al., 2011; Waheed et al., 2020). The QQ strategy used to mitigate membrane biofouling is sustainable and promising (Lee et al., 2016b) since it merely blocks bacterial communication without killing the bacteria.
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