Title of article :
Lead and cadmium biosorption by extracellular polymeric substances (EPS) extracted from activated sludges: pH-sorption edge tests and mathematical equilibrium modelling
Author/Authors :
Gilles Guibaud، نويسنده , , Eric Van Hullebusch، نويسنده , , François Bordas، نويسنده ,
Issue Information :
روزنامه با شماره پیاپی سال 2006
Pages :
8
From page :
1955
To page :
1962
Abstract :
The sorption of Cd and Pb by extracellular polymeric substances (EPS) extracted from activated sludges originated from wastewater treatment plants (WWTPs) or Lab-scale bioreactors was investigated as a function of pH. The study was carried out using a polarographic method in the SMDE (stripping mercury dropping electrode) mode which is suited to determine labile metals in solution containing soluble ligands such as EPS. The results obtained provide evidence of the presence of a pH-sorption/desorption edge for Cd and Pb by EPS. The use of Kurbatov’s model gives information on the mechanisms involved through the determination of “relative complexation constants” (operationally defined) and the number of protons exchanged. The use of this model demonstrates that proton exchange with metals is not the only mechanism involved in metal biosorption by EPS. Other mechanisms such as cation exchange with Ca or Mg, global electric field surrounding the ligand or micro-precipitation of metals could be involved in metal sorption by EPS. The position of the pH-sorption edge curves and the “relative complexation constants” show that Pb displays a greater affinity for EPS than Cd. The studied EPS have large differences regarding binding strength of Cd and Pb. These differences are not correlated with the organic parameters measured to characterize the EPS, however the mineral fraction of the EPS could be involved to a large extent in the sorption of metal.
Keywords :
Activated sludge , Metal , pH , Extracellular polymers , sorption edge
Journal title :
Chemosphere
Serial Year :
2006
Journal title :
Chemosphere
Record number :
739091
Link To Document :
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