Seasonal variation of bacterial community in biological aerated filter for ammonia removal in drinking water treatment

Biological aerated filter (BAF) is widely used in wastewater treatment plants (WWTPs) and shows potential application of micropolluted drinking water sources with a higher NH4+-N removal efficiency during short warm seasons. Here we adopted a pilot lava-based BAF setup as a pretreatment unit of drin...

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Published in:	Water research (Oxford) Vol. 123; pp. 668 - 677
Main Authors:	Liu, Hongyuan, Zhu, Liying, Tian, Xiaohe, Yin, Yeshi
Format:	Journal Article
Language:	English
Published:	England Elsevier Ltd 15.10.2017
Subjects:	acclimation Acclimatization ammonia Ammonia - chemistry Ammonia removal ammonium nitrogen bacterial communities biofilters denaturing gradient gel electrophoresis drinking water Flavobacterium nitrification Nitrifying bacteria nitrite nitrogen Nitrites Nitrobacter Nitrosomonas Nitrosomonas communis Nitrosomonas oligotropha Oxidation-Reduction river water Seasonal bacterial shift seasonal variation Seasons Sphingomonas summer temperature wastewater treatment Water Purification Water treatment winter Water treatment Acclimatization Nitrifying bacteria Ammonia removal Seasonal bacterial shift
ISSN:	0043-1354, 1879-2448, 1879-2448
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Abstract	Biological aerated filter (BAF) is widely used in wastewater treatment plants (WWTPs) and shows potential application of micropolluted drinking water sources with a higher NH4+-N removal efficiency during short warm seasons. Here we adopted a pilot lava-based BAF setup as a pretreatment unit of drinking water treatment plant (DWTP) and achieved a great performance of ammonia removal over a two-year operation using natural river water. We respectively observed 92.62% of NH4+-N removal efficiency, 97.88% of NO2−-N removal efficiency in summer, and 77.52% NH4+-N removal efficiency in winter down to 5 °C. Based on DGGE analysis, AOB, NOB, as well as heterotrophic bacteria including genus Flavobacterium and Sphingomonas are responsible for the performance. Nitrosomonas and Nitrospira are found to be the dominant AOB and NOB in the BAF microbiota. The compositions of AOB including Nitrosomonas communis and Nitrosomonas oligotropha are different from the strains previously reported in BAF of WWTPs but similar to the observations in DWPTs. We observed seasonal bacterial shifts between summer and winter groups involved in AOB, NOB and heterotrophic genus Flavobacterium, which may be responsible for the seasonal performance fluctuation. The psychrophilic AOB belonging to Nitrosomonas likely contribute to the recovered NH4+-N removal efficiency when temperature is below 7 °C. Lack of nitrification functional psychrophilic or psychrotolerant NOB may be in charge of the severe nitrite accumulation below 7 °C. Our analysis suggests that the colonization of psychrophilic nitrifying bacteria in BAF needs at least two-year of natural acclimatization and is necessary for all-weather BAF in DWTPs. [Display omitted] •NH4+-N removal efficiency of 77.52% has been achieved over a temperature range of 5.1–8.2 °C.•Psychrophilic AOB is responsible for the great NH4+-N removal in winter.•Bacterial shift has been observed between summer and winter even in the same genus.•Two years acclimatization is needed for psychrophile colonization with raw water.
AbstractList	Biological aerated filter (BAF) is widely used in wastewater treatment plants (WWTPs) and shows potential application of micropolluted drinking water sources with a higher NH -N removal efficiency during short warm seasons. Here we adopted a pilot lava-based BAF setup as a pretreatment unit of drinking water treatment plant (DWTP) and achieved a great performance of ammonia removal over a two-year operation using natural river water. We respectively observed 92.62% of NH -N removal efficiency, 97.88% of NO -N removal efficiency in summer, and 77.52% NH -N removal efficiency in winter down to 5 °C. Based on DGGE analysis, AOB, NOB, as well as heterotrophic bacteria including genus Flavobacterium and Sphingomonas are responsible for the performance. Nitrosomonas and Nitrospira are found to be the dominant AOB and NOB in the BAF microbiota. The compositions of AOB including Nitrosomonas communis and Nitrosomonas oligotropha are different from the strains previously reported in BAF of WWTPs but similar to the observations in DWPTs. We observed seasonal bacterial shifts between summer and winter groups involved in AOB, NOB and heterotrophic genus Flavobacterium, which may be responsible for the seasonal performance fluctuation. The psychrophilic AOB belonging to Nitrosomonas likely contribute to the recovered NH -N removal efficiency when temperature is below 7 °C. Lack of nitrification functional psychrophilic or psychrotolerant NOB may be in charge of the severe nitrite accumulation below 7 °C. Our analysis suggests that the colonization of psychrophilic nitrifying bacteria in BAF needs at least two-year of natural acclimatization and is necessary for all-weather BAF in DWTPs. Biological aerated filter (BAF) is widely used in wastewater treatment plants (WWTPs) and shows potential application of micropolluted drinking water sources with a higher NH₄⁺-N removal efficiency during short warm seasons. Here we adopted a pilot lava-based BAF setup as a pretreatment unit of drinking water treatment plant (DWTP) and achieved a great performance of ammonia removal over a two-year operation using natural river water. We respectively observed 92.62% of NH₄⁺-N removal efficiency, 97.88% of NO₂⁻-N removal efficiency in summer, and 77.52% NH₄⁺-N removal efficiency in winter down to 5 °C. Based on DGGE analysis, AOB, NOB, as well as heterotrophic bacteria including genus Flavobacterium and Sphingomonas are responsible for the performance. Nitrosomonas and Nitrospira are found to be the dominant AOB and NOB in the BAF microbiota. The compositions of AOB including Nitrosomonas communis and Nitrosomonas oligotropha are different from the strains previously reported in BAF of WWTPs but similar to the observations in DWPTs. We observed seasonal bacterial shifts between summer and winter groups involved in AOB, NOB and heterotrophic genus Flavobacterium, which may be responsible for the seasonal performance fluctuation. The psychrophilic AOB belonging to Nitrosomonas likely contribute to the recovered NH₄⁺-N removal efficiency when temperature is below 7 °C. Lack of nitrification functional psychrophilic or psychrotolerant NOB may be in charge of the severe nitrite accumulation below 7 °C. Our analysis suggests that the colonization of psychrophilic nitrifying bacteria in BAF needs at least two-year of natural acclimatization and is necessary for all-weather BAF in DWTPs. Biological aerated filter (BAF) is widely used in wastewater treatment plants (WWTPs) and shows potential application of micropolluted drinking water sources with a higher NH4+-N removal efficiency during short warm seasons. Here we adopted a pilot lava-based BAF setup as a pretreatment unit of drinking water treatment plant (DWTP) and achieved a great performance of ammonia removal over a two-year operation using natural river water. We respectively observed 92.62% of NH4+-N removal efficiency, 97.88% of NO2--N removal efficiency in summer, and 77.52% NH4+-N removal efficiency in winter down to 5 °C. Based on DGGE analysis, AOB, NOB, as well as heterotrophic bacteria including genus Flavobacterium and Sphingomonas are responsible for the performance. Nitrosomonas and Nitrospira are found to be the dominant AOB and NOB in the BAF microbiota. The compositions of AOB including Nitrosomonas communis and Nitrosomonas oligotropha are different from the strains previously reported in BAF of WWTPs but similar to the observations in DWPTs. We observed seasonal bacterial shifts between summer and winter groups involved in AOB, NOB and heterotrophic genus Flavobacterium, which may be responsible for the seasonal performance fluctuation. The psychrophilic AOB belonging to Nitrosomonas likely contribute to the recovered NH4+-N removal efficiency when temperature is below 7 °C. Lack of nitrification functional psychrophilic or psychrotolerant NOB may be in charge of the severe nitrite accumulation below 7 °C. Our analysis suggests that the colonization of psychrophilic nitrifying bacteria in BAF needs at least two-year of natural acclimatization and is necessary for all-weather BAF in DWTPs.Biological aerated filter (BAF) is widely used in wastewater treatment plants (WWTPs) and shows potential application of micropolluted drinking water sources with a higher NH4+-N removal efficiency during short warm seasons. Here we adopted a pilot lava-based BAF setup as a pretreatment unit of drinking water treatment plant (DWTP) and achieved a great performance of ammonia removal over a two-year operation using natural river water. We respectively observed 92.62% of NH4+-N removal efficiency, 97.88% of NO2--N removal efficiency in summer, and 77.52% NH4+-N removal efficiency in winter down to 5 °C. Based on DGGE analysis, AOB, NOB, as well as heterotrophic bacteria including genus Flavobacterium and Sphingomonas are responsible for the performance. Nitrosomonas and Nitrospira are found to be the dominant AOB and NOB in the BAF microbiota. The compositions of AOB including Nitrosomonas communis and Nitrosomonas oligotropha are different from the strains previously reported in BAF of WWTPs but similar to the observations in DWPTs. We observed seasonal bacterial shifts between summer and winter groups involved in AOB, NOB and heterotrophic genus Flavobacterium, which may be responsible for the seasonal performance fluctuation. The psychrophilic AOB belonging to Nitrosomonas likely contribute to the recovered NH4+-N removal efficiency when temperature is below 7 °C. Lack of nitrification functional psychrophilic or psychrotolerant NOB may be in charge of the severe nitrite accumulation below 7 °C. Our analysis suggests that the colonization of psychrophilic nitrifying bacteria in BAF needs at least two-year of natural acclimatization and is necessary for all-weather BAF in DWTPs. Biological aerated filter (BAF) is widely used in wastewater treatment plants (WWTPs) and shows potential application of micropolluted drinking water sources with a higher NH4+-N removal efficiency during short warm seasons. Here we adopted a pilot lava-based BAF setup as a pretreatment unit of drinking water treatment plant (DWTP) and achieved a great performance of ammonia removal over a two-year operation using natural river water. We respectively observed 92.62% of NH4+-N removal efficiency, 97.88% of NO2−-N removal efficiency in summer, and 77.52% NH4+-N removal efficiency in winter down to 5 °C. Based on DGGE analysis, AOB, NOB, as well as heterotrophic bacteria including genus Flavobacterium and Sphingomonas are responsible for the performance. Nitrosomonas and Nitrospira are found to be the dominant AOB and NOB in the BAF microbiota. The compositions of AOB including Nitrosomonas communis and Nitrosomonas oligotropha are different from the strains previously reported in BAF of WWTPs but similar to the observations in DWPTs. We observed seasonal bacterial shifts between summer and winter groups involved in AOB, NOB and heterotrophic genus Flavobacterium, which may be responsible for the seasonal performance fluctuation. The psychrophilic AOB belonging to Nitrosomonas likely contribute to the recovered NH4+-N removal efficiency when temperature is below 7 °C. Lack of nitrification functional psychrophilic or psychrotolerant NOB may be in charge of the severe nitrite accumulation below 7 °C. Our analysis suggests that the colonization of psychrophilic nitrifying bacteria in BAF needs at least two-year of natural acclimatization and is necessary for all-weather BAF in DWTPs. [Display omitted] •NH4+-N removal efficiency of 77.52% has been achieved over a temperature range of 5.1–8.2 °C.•Psychrophilic AOB is responsible for the great NH4+-N removal in winter.•Bacterial shift has been observed between summer and winter even in the same genus.•Two years acclimatization is needed for psychrophile colonization with raw water.
Author	Yin, Yeshi Liu, Hongyuan Tian, Xiaohe Zhu, Liying
Author_xml	– sequence: 1 givenname: Hongyuan surname: Liu fullname: Liu, Hongyuan email: lhyzyy@zjut.edu.cn organization: College of Civil Engineering and Architecture, Zhejiang University of Technology, Hangzhou, 310014, PR China – sequence: 2 givenname: Liying surname: Zhu fullname: Zhu, Liying email: zhuliying@hotmail.co.jp organization: State Key Laboratory Breeding Base for Zhejiang Sustainable Pest and Disease Control, Institute of Plant Protection and Microbiology, Zhejiang Academy of Agricultural Sciences, Hangzhou, 310021, PR China – sequence: 3 givenname: Xiaohe surname: Tian fullname: Tian, Xiaohe organization: College of Civil Engineering and Architecture, Zhejiang University of Technology, Hangzhou, 310014, PR China – sequence: 4 givenname: Yeshi surname: Yin fullname: Yin, Yeshi organization: State Key Laboratory Breeding Base for Zhejiang Sustainable Pest and Disease Control, Institute of Plant Protection and Microbiology, Zhejiang Academy of Agricultural Sciences, Hangzhou, 310021, PR China
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Keywords	Water treatment Acclimatization Nitrifying bacteria Ammonia removal Seasonal bacterial shift
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Snippet	Biological aerated filter (BAF) is widely used in wastewater treatment plants (WWTPs) and shows potential application of micropolluted drinking water sources...
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SubjectTerms	acclimation Acclimatization ammonia Ammonia - chemistry Ammonia removal ammonium nitrogen bacterial communities biofilters denaturing gradient gel electrophoresis drinking water Flavobacterium nitrification Nitrifying bacteria nitrite nitrogen Nitrites Nitrobacter Nitrosomonas Nitrosomonas communis Nitrosomonas oligotropha Oxidation-Reduction river water Seasonal bacterial shift seasonal variation Seasons Sphingomonas summer temperature wastewater treatment Water Purification Water treatment winter
Title	Seasonal variation of bacterial community in biological aerated filter for ammonia removal in drinking water treatment
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