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为了研究聚合氯化铝( PAC)的投加在好氧颗粒污泥培养初期的作用,本研究分别在污泥培养的第1—7天(R1)和第8—14天(R2)投加PAC,并采用三维荧光光谱(3D-EEM)和傅立叶红外光谱(FTIR)技术分析好氧颗粒污泥形成初期胞外聚合物( EPS)各组分的含量及变化规律.结果表明,PAC投加时间推迟后,污泥沉降性能良好,且反应器中胞外聚合物和蛋白质含量明显增多,松散附着的EPS( LB-EPS)中蛋白含量变化趋势明显,多糖含量保持在较小范围内波动,与溶解性胞外聚合物( S-EPS)和紧密黏附的胞外聚合物( TB-EPS)相比较,LB-EPS和污泥颗粒化有密切关系;三维荧光光谱分析结果显示,R2中荧光类蛋白物质(峰A和峰B)强度均大于R1,而腐殖酸类物质(峰C)强度小于R1,说明A和B这两种荧光类蛋白物质在微生物聚集体形成过程中的作用更加重要;红外光谱表明,1636 cm-1、1654 cm-1分别属于蛋白质二级结构中CO伸长振动引起的,分别存在于S-EPS和LB-EPS、TB-EPS中,且在投加PAC的时间推迟后1654 cm-1处的吸收峰吸收较弱,和三维荧光分析共同表明LB-EPS中的蛋白类物质是好氧颗粒污泥形成初期加入PAC进行强化造粒的核心原因之一.

In order to investigate the effect of PAC during the initial stage of aerobic granulation, two dosing periods of PAC were chosen in this study ( day 1—7, R1;day 8—14, R2) . In addition, the content of EPS components was quantified and their variation was analyzed by using three-dimensional fluorescence spectrum (3D-EEM) and Fourier transform infrared spectroscopy (FTIR). The results showed that the granules formed in R2 performed better in settling properties and EPS production than that in R1. Moreover, more proteis were also observed. The contents of proteins in Loosely Bound EPS ( LB-EPS) changed significantly, while the contents of polysaccharide fluctuated a narrow range. Compared with the Soluble EPS (S-EPS) and Tightly Bound EPS(TB-EPS), the LB-EPS was closely related to the sludge granulation. According to the 3D-EEM, compared with R1,the fluorescence intensity of peak A and B was stronger in R2, while the intensity of peak C was weaker. This result indicated that protein-like substances played a more important role on the formation of aggregations. The result of FTIR reveal C=O stretching vibration peak, which is associated with protein secondary structure, was observed in S-EPS, LB-EPS and TB-EPS. Furthermore, its intensity was higher in R1 than in R2, suggesting that the proteins in LB-EPS played a significant role during the initial period of aerobic granulation. This result was in accordance with the analysis of 3D-EEM.

参考文献

[1] Di Iaconi C;Ramadori R;Lopez A;Passino R.Hydraulic shear stress calculation in a sequencing batch biofilm reactor with granular biomass[J].Environmental Science & Technology: ES&T,20053(3):889-894.
[2] F. Xiao;S.F. Yang;X.Y. Li.Physical and hydrodynamic properties of aerobic granules produced in sequencing batch reactors[J].Separation and Purification Technology,20083(3):634-641.
[3] 陈冉妮;高景峰;郭建秋;苏凯;张倩.好氧颗粒污泥同步脱氮除磷的常温启动和低温维持[J].环境科学,2009(10):2995-3001.
[4] Extracellular polymeric substances and structural stability of aerobic granule[J].Water research: A journal of the international water association,20086/7(6/7):p.1644-1650.
[5] Li XM;Liu QQ;Yang Q;Guo L;Zeng GM;Hu JM;Zheng W.Enhanced aerobic sludge granulation in sequencing batch reactor by Mg2+ augmentation[J].Bioresource Technology: Biomass, Bioenergy, Biowastes, Conversion Technologies, Biotransformations, Production Technologies,20091(1):64-67.
[6] McSwain BS;Irvine RL;Hausner M;Wilderer PA.Composition and distribution of extracellular polymeric substances in aerobic flocs and granular sludge[J].Applied and Environmental Microbiology,20052(2):1051-1057.
[7] Adav SS;Lee DJ;Lai JY.Proteolytic activity in stored aerobic granular sludge and structural integrity[J].Bioresource Technology: Biomass, Bioenergy, Biowastes, Conversion Technologies, Biotransformations, Production Technologies,20091(1):68-73.
[8] Li, H.;Wen, Y.;Cao, A.;Huang, J.;Zhou, Q.;Somasundaran, P..The influence of additives (Ca ~(2+), Al ~(3+), and Fe ~(3+)) on the interaction energy and loosely bound extracellular polymeric substances (EPS) of activated sludge and their flocculation mechanisms[J].Bioresource Technology: Biomass, Bioenergy, Biowastes, Conversion Technologies, Biotransformations, Production Technologies,20121(1):188-194.
[9] Murthy SN.;Novak JT..Effects of potassium ion on sludge settling, dewatering and effluent properties[J].Water Science and Technology,19984/5(4/5):317-324.
[10] Namguk Her;Gary Amy;Diane McKnight;Jinsik Sohn;Yeomin Yoon.Characterization of DOM as a function of MW by fluorescence EEM and HPLC-SEC using UVA, DOC, and fluorescence detection[J].Water research: A journal of the international water association,200317(17):4295-4303.
[11] Ramesh A;Lee DJ;Lai JY.Membrane biofouling by extracellular polymeric substances or soluble microbial products from membrane bioreactor sludge[J].Applied Microbiology and Biotechnology,20073(3):699-707.
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