The Influence of Temperature on Bioflocculation and Settling of Activated Sludge and their Flocculation Mechanisms Involved

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Abstract:

Effects of temperature (conventional (25°С) vs. mesophilic (35°С) vs. thermophilic (55°С)) on activated sludge properties (production and composition of EPS and interaction potential) and their roles in bioflocculation and settling were studied using well-controlled sequencing batch reactors fed with a synthetic wastewater comprised of glucose and inorganic nutrients. The results show that thermophilic sludge had a poorer bioflocculation ability and settleability than that of conventional and mesophilic sludge. Analysis of extracellular polymeric substances (EPS) indicates that thermophilic sludge had a higher level of loosely bound EPS (LB-EPS) content than that of conventional and mesophilic sludge. The LB-EPS content of thermophilic sludge was ten times more than TB-EPS content of it, which coincided with higher supernatant turbidity. Therefore, the worse bioflocculation and settling ability of thermophilic sludge could be explained from the perspective of LB-EPS. Calculating the interaction energy of three kinds of sludge, the interaction barrier of thermophilic sludge disappeared which meant the attractive potential was dominant in the system. Thus, it should have led to a better flocculation, which did not agree with the actual performance. It indicates that the worse bioflocculation and settling ability of thermophilic sludge could be explained from the perspective of interaction energy.

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Advanced Materials Research (Volumes 518-523)

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1817-1824

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May 2012

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© 2012 Trans Tech Publications Ltd. All Rights Reserved

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[1] B. Q. Liao: Water Research Vol. 35 (2001), p.339

Google Scholar

[2] B. Q. Liao: Physicochemical studies of microbial flocs. In Graduate Department of Chernical Engineering & Applied Chemistry. University of Toronto.

Google Scholar

[3] T. M.Lapara, J. E.Alleman: Water Research Vol. 33 (1999), p.895

Google Scholar

[4] J. Suvilampi, A. Lehtomaki, J. Rintala: Bioresource Technology. Vol. 88 (2003), p.207

Google Scholar

[5] B. M.Wilen, J. L. Nielsen, K. Keiding, P. H. Nielsen: Colloids and Surfaces Biointerfaces Vol.18 (2000), p.145

Google Scholar

[6] D. C. Sobeck, M. J. Higgins: Water Research Vol. 36 (2002), p.527

Google Scholar

[7] B. M. Wilen, B. Jin, P. Lant: Water Research Vol. 37 (2003), p.2127

Google Scholar

[8] G. P. Sheng, H.Q. Yu., X. Y. Li: Biotechnology Advances Vol. 28 (2010), p.882

Google Scholar

[9] Zita, M. Hermansson: Applied and Environmental Microbiology Vol. 60 (1994), p.3041

Google Scholar

[10] C.P. Cousin, J.J. Ganczarczyk: Water Quality Research Journal of Canada Vol. 33 (1998), p.565

Google Scholar

[11] X. M. Liu, G. P. Sheng, H. Q. Yu: Environmental Science & Technology Vol. 41 (2007), p.4620

Google Scholar

[12] W. Wu, R. F. Giese, C. J. van Oss :Colloids and Surfaces B-Biointerfaces. Vol. 14 (1999), p.47

Google Scholar

[13] X. M. Liu, G. P. Sheng, H. W. Luo: Environmental Science & Technology Vol. 44 (2010), p.4355

Google Scholar

[14] X. M. Liu, G, P. Sheng, J. Wang: Applied Microbiology and Biotechnology. Vol. 79 (2008), p.187

Google Scholar

[15] J. W. Morgan, C. F. Forster, L. Evison: Water Research Vol. 24 (1990), p.743

Google Scholar

[16] X. Y. Li, S. F. Yang: Water Research Vol. 41 (2007), p.1022

Google Scholar

[17] G. H. Yu, P. J. He, L. M. Shao: Bioresource Technology Vol. 100 (2009), p.3193

Google Scholar

[18] B. Q. Liao, H. J. Lin, S. P. Langevin, et al: Water Research Vol. 45(2010), p.509

Google Scholar

[19] X. Y. Li, S. F. Yang: Water Research Vol. 41 (2007), p.1022

Google Scholar

[20] M. Lurie, M. Rebhun: Water Sci Technol Vol. 36(1997), p.93

Google Scholar