Modeling of Iron Removal from Spent Passivation Baths by Ion Exchange in Fixed-Bed Operation

In this work the mathematical model that describes the kinetics of the fixed-bed ion exchange iron separation from chromium(III) passivating baths is presented. Passivation is a common step in the zinc electrodeposition galvanic process. The removal of iron species from the passivation baths allows the extention of their life, thus reducing the amount of waste to be managed and the consumption of raw materials. A commercial chelating resin, Purolite S-957, containing sulfonic and phosphonic acid functional groups was employed. Equilibrium experiments, carried out under isothermal conditions at 20 °C, were correlated to the Freundlich equation, with the following parameters KF = 25 700((mg(n−1)/n L1/n)/kgdry_resin) and n = 2.45. A simple mathematical model assuming a reversible chemical reaction as the rate-controlling step has been developed to describe the fixed-bed iron removal rate in the media solutions under study. The value of the unknown parameter, the rate coefficient for the forward reaction, kd ...

[1]  I. Ortiz,et al.  Selective iron removal from spent passivation baths by ion exchange , 2008 .

[2]  W. Höll,et al.  Column performance of ion exchange resins with aminophosphonate functional groups for elimination of heavy metals , 2007 .

[3]  B. McKevitt Removal of iron by ion exchange from copper electrowinning electrolyte solutions containing antimony and bismuth , 2007 .

[4]  I. Caro,et al.  Theoretical model for ion exchange of iron (III) in chelating resins: Application to metal ion removal from wine , 2005 .

[5]  A. H. Martins,et al.  Selective sorption of nickel and cobalt from sulphate solutions using chelating resins , 2004 .

[6]  M. Ortiz,et al.  Modelling of Cr(VI) removal from polluted groundwaters by ion exchange , 2004 .

[7]  G. Foutch,et al.  Binary Liquid-Phase Mass Transport in Mixed-Bed Ion Exchange at Low Solute Concentration , 2003 .

[8]  F. M. Doyle,et al.  EFFECT OF pH ON THE ADSORPTION OF SELECTED HEAVY METAL IONS FROM CONCENTRATED CHLORIDE SOLUTIONS BY THE CHELATING RESIN DOWEX M-4195 , 2002 .

[9]  W. Höll,et al.  Sorption of Heavy Metals onto Selective Ion-Exchange Resins with Aminophosphonate Functional Groups , 2001 .

[10]  H. Sastre,et al.  Preliminary study of iron removal from hydrochloric pickling liquor by ion exchange , 1999 .

[11]  S. H. Laurie,et al.  Ion exchange studies on zinc-rich waste liquors , 1999 .

[12]  M. Saǧlam,et al.  Removal of Metal Pollutants (Cd(II) and Cr(III)) from Phosphoric Acid Solutions by Chelating Resins Containing Phosphonic or Diphosphonic Groups , 1998 .

[13]  E. Horwitz,et al.  Diphonix® Resin: A Review of Its Properties and Applications , 1997 .

[14]  S. Alexandratos,et al.  Bifunctionality as a means of enhancing complexation kinetics in selective ion exchange resins , 1995 .

[15]  E. Horwitz,et al.  Uptake of metal ions by a new chelating ion-exchange resin. Part 4. Kinetics , 1994 .

[16]  E. Horwitz,et al.  UPTAKE OF METAL IONS BY A NEW CHELATING ION-EXCHANGE RESIN. PART 1: ACID DEPENDENCIES OF ACTINIDE IONS* , 1993 .

[17]  F. Helfferich,et al.  Models and physical reality in ion-exchange kinetics , 1990 .

[18]  C. Haas,et al.  Kinetics of metal removal by chelating resin from a complex synthetic wastewater , 1984 .

[19]  C. Haas,et al.  Application of ion exchangers to recovery of metals from semiconductor wastes , 1984 .

[20]  F. Helfferich Ion-Exchange Kinetics. V. Ion Exchange Accompanied by Reactions , 1965 .