|
|
Comparison of foam characteristics in biological treatment units and water supply outlet of municipal wastewater treatment plant |
WANG Fang-shu1, GUO Jia2, LI Ji-cheng3, YANG Chuan-xi1, MA Ying-zi1, DONG Xiao-wan1, CHEN Dong1 |
1. School of Environmental and Municipal Engineering, Qingdao University of Technology, Qingdao 266525, China; 2. Qingdao Licun River Water Service Co., Ltd, Qingdao 266001; 3. Hunchun Municipal Bureau of Housing and Urban-Rural Development, Hunchun 133300, China |
|
|
Abstract This study comprehensively analyzed the foam characteristics of the samples collected from the aerobic tank (H), MBR tank (M), and ecological water supply outlet (B) of a wastewater treatment plant located at Qingdao regarding water quality index, organic components and microbial community structure. Compared with H and M, the TOC, TN, protein, UV254 and DO concentrations of the foam mixture collected from B were significantly higher, while its surface tension and viscosity were slightly lower. For the organic composition, the alkanes and fatty acids concentrations of B were much higher than that of H and M, while its BFK concentration was significantly lower. It was also found that the main organic component of the three sampling points was protein which might belong to Mucin and Nisin due to the high matching points. In comparison with H and M, the proportion of fulvic acid humus of B was higher, while its protein was lower. These results indicated that BFK was the primary foaming agent for H and M, and hydrophobic protein and fulvic acid humus were the main foaming agents. However, BFK and LCFAs were the dominating foaming agents for B, and alkanes, hydrophobic proteins and fulvic acid humus were the main foaming agents. It should be noted that the microbial community of B was significantly different from that of H and M. For the microbial composition at the phylum level, the proportion of Proteobacteria of B was up to 97.27%, while the main bacterial of H and M were Actinobacteriota, accounting for 58.5% and 47.9%, respectively. Moreover, the principal genera of B were g_unclassified_Acidovorax, s_uncultured_g_Undibacterium and Pseudomonas, while that of H and M were Skermania and Candidatus Microthrix.
|
Received: 24 March 2023
|
|
|
|
|
[1] |
De los Reyes III FL, Rothauszky D, Raskin L. Microbial community structures in foaming and nonfoaming full-scale wastewater treatment plants [J]. Water Environment Research, 2002,74(5):437-449.
|
[2] |
Blackall L L, Harbers AE, Greenfield PF, et al. Foaming in activated sludge plants:a survey in Queensland, Australia and an evaluation of some control strategies [J]. Water Research, 1991,25(3):313-317.
|
[3] |
Guo F, Wang Z P, Yu K, et al. Detailed investigation of the microbial community in foaming activated sludge reveals novel foam formers [J]. Scientific Reports, 2015,5(1):7637.
|
[4] |
李探微,彭永臻,陈志根,等.活性污泥法的生物泡沫形成和控制[J]. 中国给水排水, 2001,17(4):73-76. Li T W, Peng Y Z, Chen Z G, et al. Formation and control of biological foam in activated sludge process [J]. China Water Supply and Drainage, 2001,17(4):73-76.
|
[5] |
李佶成,张金康,张崇芹,等.再生水生态补水外排口黄褐色泡沫成因研究[J]. 青岛理工大学学报, 2022,43(4):97-104. Li J C, Zhang J K, Zhang C Q, et al. Study on the cause of the yellowish brown foam at the outlet of the reclaimed water ecological makeup [J]. Journal of Qingdao University of Technology, 2022,43(4):97-104.
|
[6] |
Zhang H, Zhang Z, Song J, et al. Foam shares antibiotic resistomes and bacterial pathogens with activated sludge in wastewater treatment plants [J]. Journal of Hazardous Materials, 2021,408:124855.
|
[7] |
HJ 501-2009水质.总有机碳的测定.燃烧氧化-非分散红外吸收法[S]. HJ 501-2009 Water quality. Determination of total organic carbon. Combustion oxidation nondispersive infrared absorption method [S].
|
[8] |
HJ 636-2012水质.总氮的测定.碱性过硫酸钾消解紫外分光光度法[S]. HJ 636-2012 Water quality. Determination of total nitrogen. Alkaline potassium persulfate digestion ultraviolet spectrophotometry [S].
|
[9] |
李政,高健磊,闫怡新.一种快速测定污泥滤液中蛋白质含量的方法[J]. 给水排水, 2022,58(S1). Li Z, Gao J L, Yan Y X. A rapid method for determining protein content in sludge filtrate [J]. Water Supply and Drainage, 2022,58(S1).
|
[10] |
罗海斌.臭氧/紫外-活性炭去除水中UV254的效能研究[J]. 炭素, 2017,2:39-42. Luo H B. Study on removal efficiency of UV254 in water by ozone/UV activated carbon [J]. Carbon, 2017,2:39-42.
|
[11] |
王薇,任红星,胡震超,等.管材对供水管网生物膜微生物种群多样性的影响[J]. 环境学学报, 2015,35(3):699-704. Wang W, Ren H X, Hu Z C, et al. The impact of pipe materials on the diversity of biofilm microbial populations in water supply networks [J]. Journal of Environmental Science, 2015,35(3):699-704.
|
[12] |
Chowdhury S. Heterotrophic bacteria in drinking water distribution system:A review [J]. Environmental Monitoring and Assessment, 2012,184(10):6087-6137.
|
[13] |
Wu M, Chen Y, Lin H, et al. Membrane fouling caused by biological foams in a submerged membrane bioreactor:Mechanism insights [J]. Water Research, 2020,181:115932.
|
[14] |
Edzwald J K. Coagulation in drinking water treatment:Particles, organics and coagulants [J]. Water Science and Technology, 1993, 27(11):21-35.
|
[15] |
刘洋.养殖废水生化处理单元泡沫特性表征及其消控对策初步研究[D]. 杭州:浙江大学, 2020. Liu Y. Preliminary study on characterization of foam characteristics of biochemical treatment unit for aquaculture wastewater and its control countermeasures [D]. Hangzhou:Zhejiang University, 2020.
|
[16] |
Wen C, Paul W, Leenheer J A, et al. Fluorescence excitation-emission matrix regional integration to quantify spectra for dissolved organic matter [J]. Environmental Science & Technology, 2003,37(24):5701-5710.
|
[17] |
黄慧婷,张明明,王敏,等.紫外/氯消毒在饮用水处理中的应用[J]. 净水技术, 2018,37(10):44-48. Huang H T, Zhang M M, Wang M, et al. Application of UV/chlorine disinfection in drinking water treatment [J]. Water Purification Technology, 2018,37(10):44-48.
|
[18] |
Petrovski S, Dyson Z A, Quill E S, et al. An examination of the mechanisms for stable foam formation in activated sludge systems [J]. Water Research, 2011,45(5):2146-2154.
|
[19] |
宋阳,姜成英,王爱杰,等.城市污水处理厂活性污泥生物泡沫研究进展[J]. 微生物学通报, 2019,46(8):1954-1970. Song Y, Jiang C Y, Wang A J, et al. Research progress on biological foam of activated sludge from urban sewage treatment plants [J]. Microbiology Bulletin, 2019,46(8):1954-1970.
|
[20] |
Blackbeard J R, Gabb D M D, Ekama GA, et al. Identification of filamentous organisms in nutrient removal activated sludge plants in South Africa [J]. Water SA, 1988,14(1):29-33.
|
[21] |
Goddard A J, Forster C F. Surface tension of activated sludges in relation to the formation of stable foams [J]. Microbios, 1986,46(186):29-43.
|
[22] |
Durban N, Juzan L, Krier J, et al. Control of Microthrix parvicella by aluminium salts addition [J]. Water Science & Technology, 2016, 73(2):414-422.
|
[23] |
Xie B, Dai X C, Xu Y T. Cause and pre-alarm control of bulking and foaming by Microthrix parvicella——a case study in triple oxidation ditch at a wastewater treatment plant [J]. Journal of Hazardous Materials, 2007,143(1/2):184-191.
|
[24] |
Nielsen P H, Roslev P, Dueholm T E, et al. Microthrix parvicella, a specialized lipid consumer in anaerobic-aerobic activated sludge plants [J]. Water Science & Technology, 2002,46(1/2):73-80.
|
[25] |
Simona R, Tomei M C, Nielsen P H, et al. "Microthrix parvicella",a filamentous bacterium causing bulking and foaming in activated sludge systems:A review of current knowledge [J]. FEMS Microbiology Reviews, 2005,29(1):49-64.
|
|
|
|