[1]刘杰,齐建华,韩士群,等.生物沥浸污泥 EPS 的变化规律及对 Zeta 电位、污泥粒径的影响[J].江苏农业学报,2017,(01):107-112.[doi:10.3969/j.issn.1000-4440.2017.01.017 ]
 LIU Jie,QI Jian-hua,HAN Shi-qun,et al.Changes of EPS in bioleaching sludge and the effect on Zeta potential and floc size[J].,2017,(01):107-112.[doi:10.3969/j.issn.1000-4440.2017.01.017 ]
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生物沥浸污泥 EPS 的变化规律及对 Zeta 电位、污泥粒径的影响()
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江苏农业学报[ISSN:1006-6977/CN:61-1281/TN]

卷:
期数:
2017年01期
页码:
107-112
栏目:
耕作栽培·资源环境
出版日期:
2017-02-28

文章信息/Info

Title:
Changes of EPS in bioleaching sludge and the effect on Zeta potential and floc size
作者:
刘杰1齐建华2韩士群1周庆1
(1. 江苏省农业科学院农业资源与环境研究所,江苏南京210014;2. 中国核电工程有限公司河北分公司,河北石家庄050000)
Author(s):
LIU Jie1QI Jian-hua2HAN Shi-qun1ZHOU Qing1
(1. Institute of Agricultural Resource and Environmental Sciences, Jiangsu Academy of Agricultural Sciences,Nanjing 210014,China;2. China Nuclear power Engineering Co., Ltd. Shijiazhuang 050000, China)
关键词:
生物沥浸胞外聚合物Zeta电位污泥粒径
Keywords:
bioleachingextracellular polymeric substances(EPS)Zeta potentialfloc size
分类号:
X705
DOI:
10.3969/j.issn.1000-4440.2017.01.017
文献标志码:
A
摘要:
本研究以氧化硫硫杆菌生物沥浸提高污泥脱水性能为目的,考察生物沥浸过程中污泥pH值、EPS总量和组成、Zeta电位、粒径等的变化,研究pH值、EPS总量和组成变化对Zeta电位、粒径的影响。结果显示,生物沥浸初期污泥EPSp、EPSh减少速度较快,随后减速变缓,EPSpy在整个过程中减少速度较慢;pH值、总EPS含量(EPST)、多糖含量(EPSpy)、蛋白质含量(EPSp)、腐殖质含量(EPSh)均对Zeta电位影响显著,EPST、EPSp、EPSh与Zeta电位相互关系为非线性关系,污泥Zeta电位降低是H+的静电中和作用和EPS电荷减少共同作用的结果;Zeta电位、EPST、EPSh、EPSp、EPSpy均对生物沥浸污泥粒径影响显著,EPST、EPSh、EPSp、EPSpy与污泥粒径的相互关系为非线性关系。大量H+的中和作用、 EPS电荷的减少、污泥絮体间空间位阻的降低共同促进了污泥絮体颗粒的增大。 〖KH+*9D〗〖GK2!2〗〖HT5”H〗摘要:本研究以氧化硫硫杆菌生物沥浸提高污泥脱水性能为目的,考察生物沥浸过程中污泥pH值、EPS总量和组成、Zeta电位、粒径等的变化,研究pH值、EPS总量和组成变化对Zeta电位、粒径的影响。结果显示,生物沥浸初期污泥EPSp、EPSh减少速度较快,随后减速变缓,EPSpy在整个过程中减少速度较慢;pH值、总EPS含量(EPST)、多糖含量(EPSpy)、蛋白质含量(EPSp)、腐殖质含量(EPSh)均对Zeta电位影响显著,EPST、EPSp、EPSh与Zeta电位相互关系为非线性关系,污泥Zeta电位降低是H+的静电中和作用和EPS电荷减少共同作用的结果;Zeta电位、EPST、EPSh、EPSp、EPSpy均对生物沥浸污泥粒径影响显著,EPST、EPSh、EPSp、EPSpy与污泥粒径的相互关系为非线性关系。大量H+的中和作用、 EPS电荷的减少、污泥絮体间空间位阻的降低共同促进了污泥絮体颗粒的增大。 〖KH+*9D〗〖GK2!2〗〖HT5”H〗摘要:本研究以氧化硫硫杆菌生物沥浸提高污泥脱水性能为目的,考察生物沥浸过程中污泥pH值、EPS总量和组成、Zeta电位、粒径等的变化,研究pH值、EPS总量和组成变化对Zeta电位、粒径的影响。结果显示,生物沥浸初期污泥EPSp、EPSh减少速度较快,随后减速变缓,EPSpy在整个过程中减少速度较慢;pH值、总EPS含量(EPST)、多糖含量(EPSpy)、蛋白质含量(EPSp)、腐殖质含量(EPSh)均对Zeta电位影响显著,EPST、EPSp、EPSh与Zeta电位相互关系为非线性关系,污泥Zeta电位降低是H+的静电中和作用和EPS电荷减少共同作用的结果;Zeta电位、EPST、EPSh、EPSp、EPSpy均对生物沥浸污泥粒径影响显著,EPST、EPSh、EPSp、EPSpy与污泥粒径的相互关系为非线性关系。大量H+的中和作用、 EPS电荷的减少、污泥絮体间空间位阻的降低共同促进了污泥絮体颗粒的增大。
Abstract:
To improve the sludge dewatering performance by thiobacillus thiooxidans, the changes of pH, total EPS content and EPS components, Zeta potential, floc size of sludge was investigated during bioleaching, and the correlation between pH, total EPS content, EPS components content and Zeta potential, floc size was analyzed. The result indicated that EPSp、EPSh sharply decreased at earlier bioleaching, then the decreasing trend became slow. The decreasion of EPSpy was slower in the process of bioleaching.pH, EPST, EPSpy, EPSp and EPSh had significant impact on Zeta potential. The relationships between EPST、EPSp、EPSh and Zeta potential were non-linear. Static neutralization of H+ and reduction of EPS charges resulted the decrease of Zeta potential. Zeta potential, EPST, EPSp, EPSh, EPSpy had significant impact on floc size. The relationships between EPST, EPSh, EPSp, EPSpy and floc size were non-linear. The increasing of floc size was caused by neutralization of H+,reducing of EPS charges and decreasing of steric hindrance between sludge flocs.

参考文献/References:

[1]WANG J P, YUAN S J, WANG Y, et al. Synthesis, characterization and application of a novel starch-based flocculant with high flocculation and dewatering properties[J]. Water Research,2013, 47 (8), 2643-2648.
[2]LIU F W, ZHOU L X, ZHOU J, et al. Improvement of sludge dewaterability and removal of sludge-borne metals by bioleaching at optimum pH[J].Journal of Hazardous Materials, 2012, 221(4):170-177.
[3]朱海凤,周立祥,王电站.生物沥浸的酸化效应对城市污泥脱水性能的影响[J].环境科学, 2012,33(3):916-921.
[4]RAYNAUD M, VAXELAIRE J, OLIVIER J, et al. Compression dewatering of municipal activated sludge: effects of salt and pH[J].Water Research, 2012, 46(14):4448-4456.
[5]WONG J W C, ZHOU J, KURADE M B, et al. Influence of ferrous ions on extracellular polymeric substances content and sludge dewaterability during bioleaching[J].Bioresource Technology, 2015, 179(179):78-83.
[6]SUBRAMANIAN B,YAN S, TYAGI S,et al. Extracellular polymeric substances (EPS) producing bacterial strains of municipal wastewater sludge: isolation, molecular identification, EPS characterization and performance for sludge settling and dewatering[J].Water Research, 2010, 44(44):2253-2266.
[7]YANG S F, LI X Y. Influences of extracellular polymeric substances (EPS) on the characteristics of activated sludge under non-steady-state conditions[J]. Process Biochemistry, 2009, 44(1):91-96.
[8]FRLUND B, PALMGREN R, KEIDING K,et al. Extraction of extracellular polymers from activated sludge using a cation exchange resin[J]. Water Research,1996, 30(8):1749-1758.
[9]ZHOU J, ZHENG G, ZHANG X, et al. Influences of extracellular polymeric substances on the dewaterability of sewage sludge during bioleaching[J]. Plos One,2014, 9 (7): e102688.
[10]ERDINCLER A, VESILIND P A. Effect of sludge cell disruption on compactibility of biological sludges[J]Waterence & Technology,2000,42(9):119-126.
[11]HUO M,ZHENG G,ZHOU L. Enhancement of the dewaterability of sludge during bioleaching mainly controlled by microbial quantity change and the decrease of slime extracellular polymeric substances content[J].Bioresource Technology, 2014, 168(3):190-197.
[12]WATSON J D, HOPKINS N H, ROBERTS J W, et al. Sequences as biological information: cells obey the laws of chemistry and physics[M]. California:The Benjamin/Cummings Publishing Company, 1987:25-64.
[13]WINGENDER J,JAEGER K E, FLEMMING H C. Interaction between extracellular polysaccharides and enzyme[M]. Berlin: Springer, 1999.
[14]LIAO B Q, ALLEN D G, LEPPARD G G,et al. Interparticle interactions affecting the stability of sludge flocs[J].Journal of Colloid & Interface Science, 2002, 249(2):372-380.
[15]FROLUND B, GRIEBE T, NIELSEN P H. Enzymatic activities in the activated sludge floc matrix, Appl[J].Applied Microbiology & Biotechnology, 1995, 43(4):755-761.
[16]ZITA A, HERMANSSON M. Effects of bacterial cell surface structures and hydrophobicity on attachment to activated sludge flocs[J].Applied Environmental Microbiology, 1997,63(3):1168-1170.
[17]ERIKSSON L, STEEN I, TENDAJ M. Evaluation of sludge properties at an activated sludge plant[J]. Waterence Technology, 1992, 25(6):251-265.
[18]ZHU L, ZHOU J, LV M, et al. Specific component comparison of extracellular polymeric substances (EPS) in flocs and granular sludge using EEM and SDS-PAGE[J]. Chemosphere, 2015, 121(5):26-32.
[19]WANG L L , WANG L F , YE X D,et al. Spatial configuration of extracellular polymeric substances of Bacillus megaterium TF10 in aqueous solution[J]. Water Research, 2012,46(46):3490-3496. [20]SUBRAMANIAN S B, YAN S, TYAGI R D, et al. Extracellular polymeric substances (EPS) producing bacterial strains of municipal wastewater sludge: isolation, molecular identification, EPS characterization and performance for sludge settling and dewatering[J]. Water Research, 2010 ,44(44):2253-2266.

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备注/Memo

备注/Memo:
收稿日期:2016-04-20 基金项目:国家科技支撑计划项目(2015BAD13B04) 作者简介:刘杰(1984-),女,四川宜宾人,博士,助理研究员,研究方向为水污染控制。(E-mail)liujie1469@163.com 通讯作者:韩士群,(E-mail)shqunh@yahoo.com.cn
更新日期/Last Update: 2017-04-12