Biological nutrient removal by applying SBR technology in small wastewater treatment plants: CD carbon source and C/N/P ratio effects

被引:27
作者
Puig, S. [1 ]
Corominas, Ll. [1 ]
Balaguer, M. D. [1 ]
Colprim, J. [1 ]
机构
[1] Univ Girona, Lab Chem & Environm Engn, Fac Ciencias, E-17071 Girona, Catalonia, Spain
关键词
C/P and C/N/P ratios; nutrient removal; PAOs; SBRs; step-feed strategy;
D O I
10.2166/wst.2007.137
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
SBR technology is considered an alternative to conventional-processes such as Phoredox, Five-stage Bardenpho, among the others for treating nutrients in wastevvaters It is especially applicable to small communities of a just few people to a population equivalent (p.e) up to 4000. In this paper, biological nutrient removal using SBR technology in a single reactor is presented. Biological nutrient removal requires a sequence of anaerobic-anoxic-aerobic phases with multiple feeding events over one cycle. This filling strategy was adapted to enhance denitrification and phosphate release, using the easily biodegradable organic matter from the wastewater. In spite of using this feeding strategy, the organic matter concentration can be insufficient. The results show that biological nutrient removal was successfully achieved by using only one reactor, working with a low organic matter concentration in the influent (C/N/P ratio of 100:12:1.8) Nevertheless, when the C/P ratio was lower than 36 g COD-g(-1) P-PO4, an accumulation of phosphate was observed. After that, the system responded quickly and returned to ideal conditions (C/P ratio of 67 g COD-g(-1) (PPO4)-P-.)(1) taking only 15 days to achieve the complete nutrient removal. Furthermore, the operational conditions and the synthetic wastewater used conferred a selective advantage to polyphosphate accumulating organisms (PAOs) over glycogen accumulating non-poly-P organisms (GAOs) as shown by the FISH analysis performed.
引用
收藏
页码:135 / 141
页数:7
相关论文
共 25 条
[1]   The effect of an anoxic zone on biological phosphorus removal by a sequential batch reactor [J].
Akin, BS ;
Ugurlu, A .
BIORESOURCE TECHNOLOGY, 2004, 94 (01) :1-7
[2]   FLUORESCENTLY LABELED, RIBOSOMAL-RNA-TARGETED OLIGONUCLEOTIDE PROBES IN THE STUDY OF MICROBIAL ECOLOGY [J].
AMANN, RI .
MOLECULAR ECOLOGY, 1995, 4 (05) :543-553
[3]  
[Anonymous], 1999, REVISED EXPANDED
[4]  
[Anonymous], 2003, Wastewater engineering: treatment and reuse
[5]  
[Anonymous], 1995, Standard methods for examination of water and waste water, V19th
[6]  
Chang CH, 1996, J CHEM TECHNOL BIOT, V67, P27
[7]   Glycogen-accumulating organisms in laboratory-scale and full-scale wastewater treatment processes [J].
Crocetti, GR ;
Banfield, JF ;
Keller, J ;
Bond, PL ;
Blackall, LL .
MICROBIOLOGY-SGM, 2002, 148 :3353-3364
[8]   The domain-specific probe EUB338 is insufficient for the detection of all Bacteria:: Development and evaluation of a more comprehensive probe set [J].
Daims, H ;
Brühl, A ;
Amann, R ;
Schleifer, KH ;
Wagner, M .
SYSTEMATIC AND APPLIED MICROBIOLOGY, 1999, 22 (03) :434-444
[9]   Nutrient removal performance of a five-step sequencing batch reactor as a function of wastewater composition [J].
Kargi, F ;
Uygur, A .
PROCESS BIOCHEMISTRY, 2003, 38 (07) :1039-1045
[10]   Full-scale demonstration of biological nutrient removal in a single tank SBR process [J].
Keller, J ;
Watts, S ;
Battye-Smith, W ;
Chong, R .
WATER SCIENCE AND TECHNOLOGY, 2001, 43 (03) :355-362