Microbial population shifts during disturbance induced foaming in anaerobic digestion of primary and activated sludge

IF 11.4 1区 环境科学与生态学 Q1 ENGINEERING, ENVIRONMENTAL
Christian Krohn , Leadin Khudur , Sali Khair Biek , Jake AK Elliott , Seyedali Tabatabaei , Chenjing Jiang , Jennifer L. Wood , Daniel Anthony Dias , Morten K.D. Dueholm , Catherine A. Rees , Denis O'Carroll , Richard Stuetz , Damien J. Batstone , Aravind Surapaneni , Andrew S. Ball
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Abstract

Foaming during anaerobic digestion (AD) of sewage sludge is poorly understood and remains an uncontrollable operational obstacle for sewage treatment systems globally, causing mechanical damage, increased hazards and reduced biogas recovery. Foams during AD commonly occur after process disturbances, such as organic loading shocks. However, it is still unclear whether these foam events are biologically driven and linked to the abundance of organisms like filamentous or hydrophobic bacteria. A time-series study was conducted, comparing digestion performance, microbial community succession, metagenomes, and metabolomes in six anaerobic continuous stirred-tank reactors (CSTRs): a control group fed normally (n = 3), and one treated group inhibited through organic shock loading of more than twice the steady state loading rate with glycerol (treatment, n = 3). As soon as microbial activity and methanogenesis recovered after inhibition, significant volumes of foam accumulated simultaneously in the reactor headspace of the three treated CSTRs. Microbial abundance profiles (16S rRNA, V3-V4) from 165 days of operation showed that filamentous or mycolic acid-producing organisms were not associated with this foam event. Shock loading led to acidification, biomass decline and microbial imbalance, contributing indirectly to the foam event. During that period, metabolomes and functional pathway abundances indicated that the stressed microbial biomass was enriched in long-chain fatty acids prior to foaming. This biomass, combined with pH changes, may have modified the physicochemical properties of sludge, leading to the fractionation of organic mass once gas production resumed. More research is needed to understand how abiotic and biotic interactions contribute to foam formation.

Abstract Image

Abstract Image

人们对污水污泥厌氧消化(AD)过程中产生的泡沫知之甚少,在全球范围内,泡沫仍是污水处理系统无法控制的运行障碍,会造成机械损坏、增加危害并降低沼气回收率。厌氧消化过程中的泡沫通常发生在有机物装载冲击等工艺干扰之后。然而,目前还不清楚这些泡沫事件是否由生物驱动,是否与丝状菌或疏水性细菌等生物的数量有关。我们进行了一项时间序列研究,比较了六个厌氧连续搅拌槽反应器(CSTR)中的消化性能、微生物群落演替、元基因组和代谢组:一个正常进料的对照组(n = 3)和一个通过有机物冲击加载抑制的处理组(处理,n = 3),有机物加载率是甘油稳定状态加载率的两倍多。抑制后,微生物活性和甲烷生成一恢复,三个处理过的 CSTR 反应器顶空就同时积累了大量泡沫。运行 165 天的微生物丰度图谱(16S rRNA,V3-V4)显示,丝状或产霉菌酸的生物与泡沫事件无关。冲击负荷导致酸化、生物量下降和微生物失衡,间接引发了泡沫事件。在此期间,代谢组和功能途径丰度表明,受压微生物生物量在起泡前富含长链脂肪酸。这种生物量加上 pH 值的变化,可能改变了污泥的物理化学特性,导致产气恢复后有机物的分馏。要了解非生物和生物的相互作用是如何促成泡沫形成的,还需要进行更多的研究。
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来源期刊
Water Research
Water Research 环境科学-工程:环境
CiteScore
20.80
自引率
9.40%
发文量
1307
审稿时长
38 days
期刊介绍: Water Research, along with its open access companion journal Water Research X, serves as a platform for publishing original research papers covering various aspects of the science and technology related to the anthropogenic water cycle, water quality, and its management worldwide. The audience targeted by the journal comprises biologists, chemical engineers, chemists, civil engineers, environmental engineers, limnologists, and microbiologists. The scope of the journal include: •Treatment processes for water and wastewaters (municipal, agricultural, industrial, and on-site treatment), including resource recovery and residuals management; •Urban hydrology including sewer systems, stormwater management, and green infrastructure; •Drinking water treatment and distribution; •Potable and non-potable water reuse; •Sanitation, public health, and risk assessment; •Anaerobic digestion, solid and hazardous waste management, including source characterization and the effects and control of leachates and gaseous emissions; •Contaminants (chemical, microbial, anthropogenic particles such as nanoparticles or microplastics) and related water quality sensing, monitoring, fate, and assessment; •Anthropogenic impacts on inland, tidal, coastal and urban waters, focusing on surface and ground waters, and point and non-point sources of pollution; •Environmental restoration, linked to surface water, groundwater and groundwater remediation; •Analysis of the interfaces between sediments and water, and between water and atmosphere, focusing specifically on anthropogenic impacts; •Mathematical modelling, systems analysis, machine learning, and beneficial use of big data related to the anthropogenic water cycle; •Socio-economic, policy, and regulations studies.
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