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Received February 27, 2003
Accepted November 7, 2003
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The Characteristics of Microbial Ecosystem Response with the Changes of Hydrolic Retention Time on an Aerobic Fixed-Biofilm Biological Nutrient Removal System
Institute for Environmental Technology and Industry, Pusan National University, Busan 609-735, Korea 1Dept. of Environmental Engineering, Pusan National University, Busan 609-735, Korea 2Safety and Environment Team, SK Corp., Ulsan 680-130, Korea
Korean Journal of Chemical Engineering, May 2004, 21(3), 635-639(5), 10.1007/BF02705498
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Abstract
The influence of an aerobic fixed-biofilm activity, microbial ecosystem and mass transfer with respect to HRT variation in a BNR (biological nutrient removal) system has been investigated in this study. The process used in this study was an anoxic (1)/aerobic (1)/anoxic (2)/aerobic (2) system. The study was demonstrated by several kinds of techniques such as INT-dehydrogenase activity (DHA), INT (2-(p-iodophenyl)-3-(p-nitrophenyl)-5-phenyl tetrazolium chloride), DAPI (4',6'-diamidino-2-phenylindole hydrochloride), and microelectrode. The study used by synthetic wastewater and HRT variation demonstrated that the DHA activity, density and heterotrophs/autotrophs ratio increased, as the HRT decreased from 8 hr to 4 hr. In comparing two aerobic reactors in fixed-biofilm process, the first aerobic reactor of the higher C/N ratio showed higher heterotrophs/autotrophs ratio and microbial activity than the second aerobic reactor. It was therefore concluded that the heterotrophs/autotrophs ratio and microbial activity were a greater influence on the first aerobic reactor, as organic loading rate was increased by HRT variation.
References
Antonisen AC, Loehr RC, Prakasam TBS, Srinath EG, JWPCF, 48(5), 835 (1976)
Carrand G, Capon B, Rasconi A, Brenner R, Water Sci. Technol., 22(1-2), 261 (1990)
Debeer D, Stoodley P, Roe F, Lewandowski Z, Biotechnol. Bioeng., 43(11), 1131 (1994)
Horn H, Hempel DC, Water Sci. Technol., 32(8), 199 (1995)
Liu Y, Capdeville B, Water Res., 30(7), 1645 (1996)
Lopez JM, Koopman B, Bitton G, Biotechnol. Bioeng., 28, 1080 (1986)
Park JH, Lee YO, Park JK, Korean J. Chem. Eng., 20(5), 878 (2003)
Peyton BM, Water Res., 30(1), 29 (1996)
Okabe S, Satoh H, Watanabe Y, Appl. Environ. Microbiol., 65(7), 3182 (1999)
Su JL, Ouyang CF, Water Sci. Technol., 34(1-2), 477 (1996)
Suthersan S, Ganczarczyk JJ, Water Pollution Res. J. Canada, 21(2), 257 (1986)
Wang B, Yang O, Liu R, Yuan J, Ma F, He J, Li G, Water Sci. Technol., 24(4), 197 (1991)
Zhangg TC, Bishop PL, Water Res., 28, 2267 (1994)
Carrand G, Capon B, Rasconi A, Brenner R, Water Sci. Technol., 22(1-2), 261 (1990)
Debeer D, Stoodley P, Roe F, Lewandowski Z, Biotechnol. Bioeng., 43(11), 1131 (1994)
Horn H, Hempel DC, Water Sci. Technol., 32(8), 199 (1995)
Liu Y, Capdeville B, Water Res., 30(7), 1645 (1996)
Lopez JM, Koopman B, Bitton G, Biotechnol. Bioeng., 28, 1080 (1986)
Park JH, Lee YO, Park JK, Korean J. Chem. Eng., 20(5), 878 (2003)
Peyton BM, Water Res., 30(1), 29 (1996)
Okabe S, Satoh H, Watanabe Y, Appl. Environ. Microbiol., 65(7), 3182 (1999)
Su JL, Ouyang CF, Water Sci. Technol., 34(1-2), 477 (1996)
Suthersan S, Ganczarczyk JJ, Water Pollution Res. J. Canada, 21(2), 257 (1986)
Wang B, Yang O, Liu R, Yuan J, Ma F, He J, Li G, Water Sci. Technol., 24(4), 197 (1991)
Zhangg TC, Bishop PL, Water Res., 28, 2267 (1994)