Ling-Hang Li, Martin Pabst, Mark C.M. van Loosdrecht, Mario Pronk
{"title":"颗粒和絮凝体在好氧颗粒污泥过程中的不同作用","authors":"Ling-Hang Li, Martin Pabst, Mark C.M. van Loosdrecht, Mario Pronk","doi":"10.1016/j.watres.2025.124671","DOIUrl":null,"url":null,"abstract":"Aerobic Granular Sludge (AGS) is an innovative and efficient biotechnology for wastewater treatment and is successfully applied on full-scale worldwide. Full-scale municipal AGS systems typically contain both granular sludge (granules) and flocculent sludge (flocs). Studies on the different roles of granules and flocs fractions are limited. In this study, a laboratory-scale AGS reactor fed with complex synthetic wastewater was operated to simulate full-scale AGS systems and to study the different roles of granules and flocs. The laboratory reactor achieved a coexistence of granules and flocs with a floc mass fraction of 17%. Activities of different size fractions were evaluated and compared regarding carbon, nitrogen, and phosphorus removal: flocs (FL; <0.2mm), small granules (SG; 0.2∼1.0mm), medium granules (MG; 1.0∼2.0mm), and large granules (LG; >2.0mm). During feeding, large granules and medium granules exhibited more substrate uptake than small granules and flocs due to preferential substrate access. For aerobic conversion, flocs and small granules showed higher biomass-specific nitrification rates, while medium granules and large granules showed higher phosphorus uptake and denitrification capacity. Furthermore, large granules and medium granules showed higher mass transfer limitation of oxygen, which limits their nitrification capability. Microbial community analysis using metagenomics and metaproteomics was performed across size fractions, and distinct communities in granules and flocs were shown. Granules showed a high abundance of <em>Candidatus</em> Accumulibacter (Polyphosphate-accumulating organism, PAO) and <em>Candidatus</em> Competibacter (Glycogen-accumulating organism, GAO). Flocs showed a high abundance of <em>Nitrosomonas</em> (Ammonium-oxidizing bacteria, AOB) and <em>Tetrasphaera</em> (Fermentative PAO) and a low abundance of <em>Ca.</em> Accumulibacter. The distribution of microbial activities and microbial community over sludge size fractions in the laboratory reactor is similar to full-scale AGS systems, indicating that this laboratory setup can simulate full-scale systems and can be used for future research. Overall, this study highlights the importance of maintaining a good balance between different granule sizes and flocs to optimize nutrient removal.","PeriodicalId":443,"journal":{"name":"Water Research","volume":"41 1","pages":""},"PeriodicalIF":12.4000,"publicationDate":"2025-09-24","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Distinct roles of granules and flocs in aerobic granular sludge processes\",\"authors\":\"Ling-Hang Li, Martin Pabst, Mark C.M. van Loosdrecht, Mario Pronk\",\"doi\":\"10.1016/j.watres.2025.124671\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"Aerobic Granular Sludge (AGS) is an innovative and efficient biotechnology for wastewater treatment and is successfully applied on full-scale worldwide. Full-scale municipal AGS systems typically contain both granular sludge (granules) and flocculent sludge (flocs). Studies on the different roles of granules and flocs fractions are limited. In this study, a laboratory-scale AGS reactor fed with complex synthetic wastewater was operated to simulate full-scale AGS systems and to study the different roles of granules and flocs. The laboratory reactor achieved a coexistence of granules and flocs with a floc mass fraction of 17%. Activities of different size fractions were evaluated and compared regarding carbon, nitrogen, and phosphorus removal: flocs (FL; <0.2mm), small granules (SG; 0.2∼1.0mm), medium granules (MG; 1.0∼2.0mm), and large granules (LG; >2.0mm). During feeding, large granules and medium granules exhibited more substrate uptake than small granules and flocs due to preferential substrate access. For aerobic conversion, flocs and small granules showed higher biomass-specific nitrification rates, while medium granules and large granules showed higher phosphorus uptake and denitrification capacity. Furthermore, large granules and medium granules showed higher mass transfer limitation of oxygen, which limits their nitrification capability. Microbial community analysis using metagenomics and metaproteomics was performed across size fractions, and distinct communities in granules and flocs were shown. Granules showed a high abundance of <em>Candidatus</em> Accumulibacter (Polyphosphate-accumulating organism, PAO) and <em>Candidatus</em> Competibacter (Glycogen-accumulating organism, GAO). Flocs showed a high abundance of <em>Nitrosomonas</em> (Ammonium-oxidizing bacteria, AOB) and <em>Tetrasphaera</em> (Fermentative PAO) and a low abundance of <em>Ca.</em> Accumulibacter. The distribution of microbial activities and microbial community over sludge size fractions in the laboratory reactor is similar to full-scale AGS systems, indicating that this laboratory setup can simulate full-scale systems and can be used for future research. 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Distinct roles of granules and flocs in aerobic granular sludge processes
Aerobic Granular Sludge (AGS) is an innovative and efficient biotechnology for wastewater treatment and is successfully applied on full-scale worldwide. Full-scale municipal AGS systems typically contain both granular sludge (granules) and flocculent sludge (flocs). Studies on the different roles of granules and flocs fractions are limited. In this study, a laboratory-scale AGS reactor fed with complex synthetic wastewater was operated to simulate full-scale AGS systems and to study the different roles of granules and flocs. The laboratory reactor achieved a coexistence of granules and flocs with a floc mass fraction of 17%. Activities of different size fractions were evaluated and compared regarding carbon, nitrogen, and phosphorus removal: flocs (FL; <0.2mm), small granules (SG; 0.2∼1.0mm), medium granules (MG; 1.0∼2.0mm), and large granules (LG; >2.0mm). During feeding, large granules and medium granules exhibited more substrate uptake than small granules and flocs due to preferential substrate access. For aerobic conversion, flocs and small granules showed higher biomass-specific nitrification rates, while medium granules and large granules showed higher phosphorus uptake and denitrification capacity. Furthermore, large granules and medium granules showed higher mass transfer limitation of oxygen, which limits their nitrification capability. Microbial community analysis using metagenomics and metaproteomics was performed across size fractions, and distinct communities in granules and flocs were shown. Granules showed a high abundance of Candidatus Accumulibacter (Polyphosphate-accumulating organism, PAO) and Candidatus Competibacter (Glycogen-accumulating organism, GAO). Flocs showed a high abundance of Nitrosomonas (Ammonium-oxidizing bacteria, AOB) and Tetrasphaera (Fermentative PAO) and a low abundance of Ca. Accumulibacter. The distribution of microbial activities and microbial community over sludge size fractions in the laboratory reactor is similar to full-scale AGS systems, indicating that this laboratory setup can simulate full-scale systems and can be used for future research. Overall, this study highlights the importance of maintaining a good balance between different granule sizes and flocs to optimize nutrient removal.
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.