Effect of proteins, polysaccharides, and particle sizes on sludge dewaterability

被引:160
作者
Shao Liming [1 ]
He Peipei [1 ]
Yu Guanghui [1 ]
He Pinjing [1 ]
机构
[1] Tongji Univ, Coll Environm Sci & Engn, Key Lab Yangtze River Water Environm, State Key Lab Pollut Control & Resources Reuse, Shanghai 200092, Peoples R China
关键词
dewaterability; extracellular polymeric substances; particle size; polysaccharides; proteins; sewage sludge; POLYMERIC SUBSTANCES EPS; WASTE-WATER SLUDGE; ACTIVATED-SLUDGE; EXTRACELLULAR POLYMER; AEROBIC DIGESTION; FLOCCULATION; HYDROLYSIS;
D O I
10.1016/S1001-0742(09)60015-2
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Four batch experiments of hydrolysis and acidification were carried out to investigate the distributions of proteins (PN) and polysaccharides (PS) in the sludge, the PN/PS ratio, the particle sizes, and their relationship with sludge dewaterability (as determined by capillary suction time, CST). The sludge flocs were stratified through centrifugation- and ultrasound-based method into four fractions: (1) slime, (2) loosely bound extracellular polymeric substances (LB-EPS), (3) tightly bound EPS (TB-EPS), and (4) pellet. The results showed that PN was mainly partitioned in the pellet (80.7%) and TB-EPS (9.6%) fractions, while PS distributed evenly in the four fractions. During hydrolysis and acidification, PN was transferred from the pellet and TB-EPS fractions to the slime fraction, but PS had no significant transfer trends. The mean particle sizes of the sludge flocs decreased with hydrolysis and acidification. The pH had a more significant influence on the dewaterability of sludge flocs than temperature. Sludge dewaterability during hydrolysis and acidification processes greatly deteriorated from 9.7 s at raw sludge to 340-450 s under alkaline conditions. However, it was just slightly increased under acidic conditions. Further investigation suggested that CST was affected by soluble PN, soluble PN/PS, and particle sizes of sludge flocs, but was affected slightly by total PIN, PS, or PN/PS in the whole sludge flocs and other fractions (except slime).
引用
收藏
页码:83 / 88
页数:6
相关论文
共 22 条
[1]  
*APHA AWWA WEF, 1998, STAND METH EX WAT WA
[2]  
BARNARD JL, 1983, WATER SCI TECHNOL, V15, P1
[3]   Hydrolysis and acidification of waste activated sludge at different pHs [J].
Chen, Yinguang ;
Jiang, Su ;
Yuan, Hongying ;
Zhou, Qi ;
Gu, Guowei .
WATER RESEARCH, 2007, 41 (03) :683-689
[4]   ANAEROBIC ACIDOGENESIS OF PRIMARY SLUDGE - THE ROLE OF SOLIDS RETENTION TIME [J].
ELEFSINIOTIS, P ;
OLDHAM, WK .
BIOTECHNOLOGY AND BIOENGINEERING, 1994, 44 (01) :7-13
[5]  
FROLUND B, 1995, APPL MICROBIOL BIOT, V43, P755, DOI 10.1007/s002530050481
[6]  
Gaudy A.F., 1962, IND WATER WASTES, V7, P17
[7]   Dewatering and settling of activated sludges: The case for using cation analysis [J].
Higgins, MJ ;
Novak, JT .
WATER ENVIRONMENT RESEARCH, 1997, 69 (02) :225-232
[8]   Effect of influent organic content on digested sludge extracellular polymer content and dewaterability [J].
Houghton, JI ;
Stephenson, T .
WATER RESEARCH, 2002, 36 (14) :3620-3628
[9]   Municipal wastewater sludge dewaterability and the presence of microbial extracellular polymer [J].
Houghton, JI ;
Quarmby, J ;
Stephenson, T .
WATER SCIENCE AND TECHNOLOGY, 2001, 44 (2-3) :373-379
[10]  
KARR PR, 1978, J WATER POLLUT CON F, V50, P1911