Interactions between metal ions and the biopolymer in activated sludge: quantification and effects of system pH value
Yun Zhou, Siqing Xia, Binh T. Nguyen, Min Long, Jiao Zhang, Zhiqiang Zhang
Interactions between metal ions and the biopolymer in activated sludge: quantification and effects of system pH value
The biopolymer showed two protein-like fluorescence peaks (peaks A and B).
Interactions of Pb(II) and biopolymer were quantified at various system pH values.
System pH values significantly affect the quenching constant values for both peaks.
Peak B plays a more important role in the interactions than peak A.
Removal mechanism of metal ions by activated sludge system was further disclosed.
The quantification and effects of system pH value on the interactions between Pb(II) and the biopolymer from activated sludge were investigated. The biopolymer had two protein-like fluorescence peaks (Ex/Em= 280 nm/326–338 nm for peak A; Ex/Em= 220–230 nm/324–338 nm for peak B). The fluorescence intensities of peak B were higher than those of peak A. The fluorophores of both peaks could be largely quenched by Pb(II), and the quencher dose for peak B was about half of that for peak A. The modified Stern-Volmer equation well depicted the fluorescence quenching titration. The quenching constant (Ka) values for both peaks decreased with rising system pH value, and then sharply decreased under alkaline conditions. It could be attributed to that the alkaline conditions caused the reduction of available Pb(II) due to the occurrence of Pb(OH)2 sediments. The Ka values of peak B were bigger than those for peak A at the same system pH values. Accordingly, the aromatic protein (peak B) plays the key role in the interactions between metal ions and the biopolymer.
Metal ions / Biopolymer / Activated sludge / Three-dimensional excitation emission matrix (3D-EEM) / Fluorescence regional integration (FRI) technique / Quantification
[1] |
Li W W, Yu H Q. Insight into the roles of microbial extracellular polymer substances in metal biosorption. Bioresource Technology, 2014, 160: 15–23
CrossRef
Pubmed
Google scholar
|
[2] |
Morgan J W, Forster C F, Evison L. A comparative study of the nature of biopolymers extracted from anaerobic and activated sludges. Water Research, 1990, 24(6): 743–750
CrossRef
Google scholar
|
[3] |
Sheng G P, Yu H Q, Li X Y. Extracellular polymeric substances (EPS) of microbial aggregates in biological wastewater treatment systems: a review. Biotechnology Advances, 2010, 28(6): 882–894
CrossRef
Pubmed
Google scholar
|
[4] |
Liu H, Fang H H P. Characterization of electrostatic binding sites of extracellular polymers by linear programming analysis of titration data. Biotechnology and Bioengineering, 2002, 80(7): 806–811
CrossRef
Pubmed
Google scholar
|
[5] |
Sheng G P, Yu H Q. Characterization of extracellular polymeric substances of aerobic and anaerobic sludge using three-dimensional excitation and emission matrix fluorescence spectroscopy. Water Research, 2006, 40(6): 1233–1239
CrossRef
Pubmed
Google scholar
|
[6] |
Sheng G P, Xu J, Luo H W, Li W W, Li W H, Yu H Q, Xie Z, Wei S Q, Hu F C. Thermodynamic analysis on the binding of heavy metals onto extracellular polymeric substances (EPS) of activated sludge. Water Research, 2013, 47(2): 607–614
CrossRef
Pubmed
Google scholar
|
[7] |
Zhang D, Pan X, Mostofa K M G, Chen X, Mu G, Wu F, Liu J, Song W, Yang J, Liu Y, Fu Q. Complexation between Hg(II) and biofilm extracellular polymeric substances: an application of fluorescence spectroscopy. Journal of Hazardous Materials, 2010, 175(1-3): 359–365
CrossRef
Pubmed
Google scholar
|
[8] |
Sheng G P, Xu J, Li W H, Yu H Q. Quantification of the interactions between Ca2+, Hg2+ and extracellular polymeric substances (EPS) of sludge. Chemosphere, 2013, 93(7): 1436–1441
CrossRef
Pubmed
Google scholar
|
[9] |
Braissant O, Decho A W, Dupraz C, Glunk C, Przekop K M, Visscher P T. Exopolymeric substances of sulfate-reducing bacteria: interactions with calcium at alkaline pH and implication for formation of carbonate minerals. Geobiology, 2007, 5(4): 401–411
CrossRef
Google scholar
|
[10] |
Salehizadeh H, Shojaosadati S A. Extracellular biopolymeric flocculants: recent trends and biotechnological importance. Biotechnology Advances, 2001, 19(5): 371–385
CrossRef
Pubmed
Google scholar
|
[11] |
Wang L L, Wang L F, Ren X M, Ye X D, Li W W, Yuan S J, Sun M, Sheng G P, Yu H Q, Wang X K. pH dependence of structure and surface properties of microbial EPS. Environmental Science & Technology, 2012, 46(2): 737–744
CrossRef
Pubmed
Google scholar
|
[12] |
Zhou Y, Xia S Q, Zhang J, Nguyen B T, Zhang Z Q. Insight into the influences of pH value on Pb(II) removal by the biopolymer extracted from activated sludge. Chemical Engineering Journal, 2017, 308(15): 1098–1104
CrossRef
Google scholar
|
[13] |
Zhou Y, Xia S Q, Zhang J, Zhang Z Q, Hermanowicz S W. Adsorption characterizations of biosorbent extracted from waste activated sludge for Pb(II) and Zn(II). Desalination and Water Treatment, 2016, 57(20): 9343–9353
CrossRef
Google scholar
|
[14] |
Zhou Y, Zhang Z, Zhang J, Xia S. New insight into adsorption characteristics and mechanisms of the biosorbent from waste activated sludge for heavy metals. Journal of Environmental Sciences (China), 2016, 45: 248–256
CrossRef
Pubmed
Google scholar
|
[15] |
Chen W, Westerhoff P, Leenheer J A, Booksh K. Fluorescence excitation-emission matrix regional integration to quantify spectra for dissolved organic matter. Environmental Science & Technology, 2003, 37(24): 5701–5710
CrossRef
Pubmed
Google scholar
|
[16] |
Cai X L, Liu G X, Zhao X, Hao Y X, Zhao Y C. Fluorescence excitation–emission matrix combined with regional integration analysis to characterize the composition and transformation of humic and fulvic acids from landfill at different stabilization stages. Waste management, 2012, 32(3):438–447
|
[17] |
Pan X, Liu J, Zhang D. Binding of phenanthrene to extracellular polymeric substances (EPS) from aerobic activated sludge: a fluorescence study. Colloids and Surfaces. B, Biointerfaces, 2010, 80(1): 103–106
CrossRef
Pubmed
Google scholar
|
[18] |
Papadopoulou A, Green R J, Frazier R A. Interaction of flavonoids with bovine serum albumin: a fluorescence quenching study. Journal of Agricultural and Food Chemistry, 2005, 53(1): 158–163
CrossRef
Pubmed
Google scholar
|
[19] |
Gauthier T D, Shane E C, Guerin W F, Seitz W R, Grant C L. Fluorescence quenching method for determining equilibrium constants for polycyclic aromatic hydrocarbons binding to dissolved humic materials. Environmental Science & Technology, 1986, 20(11): 1162–1166
CrossRef
Google scholar
|
[20] |
Lu X, Jaffe R. Interaction between Hg(II) and natural dissolved organic matter: a fluorescence spectroscopy based study. Water Research, 2001, 35(7): 1793–1803
CrossRef
Pubmed
Google scholar
|
[21] |
Hu Y J, Liu Y, Zhang L X, Zhao R M, Qu S S. Studies of interaction between colchicine and bovine serum albumin by fluorescence quenching method. Journal of Molecular Structure, 2005, 750(1): 174–178
CrossRef
Google scholar
|
[22] |
American Public Health A, American Water Works A, Water Pollution Control F, Water Environment F. Standard Methods for the Examination of Water and Wastewater: American Public Health Association, 1915
|
[23] |
Frølund B, Palmgren R, Keiding K, Nielsen P H. Extraction of extracellular polymers from activated sludge using a cation exchange resin. Water Research, 1996, 30(8): 1749–1758
CrossRef
Google scholar
|
[24] |
Yamashita Y, Tanoue E. Chemical characterization of protein-like fluorophores in DOM in relation to aromatic amino acids. Marine Chemistry, 2003, 82(3): 255–271
CrossRef
Google scholar
|
[25] |
Laane R. Influence of pH on the fluorescence of dissolved organic matter. Marine Chemistry, 1982, 11(4): 395–401
CrossRef
Google scholar
|
[26] |
Ghosh K, Schnitzer M. Fluorescence excitation spectra of humic substances. Canadian Journal of Soil Science, 1980, 60(2): 373–379
CrossRef
Google scholar
|
[27] |
Comte S, Guibaud G, Baudu M. Biosorption properties of extracellular polymeric substances (EPS) towards Cd, Cu and Pb for different pH values. Journal of Hazardous Materials, 2008, 151(1): 185–193
CrossRef
Pubmed
Google scholar
|
[28] |
Zhou Y, Zhang Z Q, Zhang J, Xia S Q. Understanding key constituents and feature of the biopolymer in activated sludge responsible for binding heavy metals. Chemical Engineering Journal, 2016, 304(15): 527–532
CrossRef
Google scholar
|
[29] |
Borisover M, Laor Y, Bukhanovsky N, Saadi I. Fluorescence-based evidence for adsorptive binding of pyrene to effluent dissolved organic matter. Chemosphere, 2006, 65(11): 1925–1934
CrossRef
Pubmed
Google scholar
|
[30] |
Guibaud G, Comte S, Bordas F, Dupuy S, Baudu M. Comparison of the complexation potential of extracellular polymeric substances (EPS), extracted from activated sludges and produced by pure bacteria strains, for cadmium, lead and nickel. Chemosphere, 2005, 59(5): 629–638
CrossRef
Pubmed
Google scholar
|
[31] |
Brown M J, Lester J N. Role of bacterial extracellular polymers in metal uptake in pure bacterial culture and activated sludge-II Effects of mean cell retention time. Water Research, 1982, 16(11): 1549–1560
CrossRef
Google scholar
|
[32] |
Merroun M L, Selenska-Pobell S. Bacterial interactions with uranium: an environmental perspective. Journal of Contaminant Hydrology, 2008, 102(3-4): 285–295
CrossRef
Pubmed
Google scholar
|
/
〈 | 〉 |