Effective utilization of waste cathode ray tube glass--crystalline silicotitanate synthesis.

A novel process for crystalline silicotitanate (CST) synthesis was developed using waste cathode ray tube (CRT) panel glass as silicon source. The key trait of the process was to extract most of the silicon out of the glass for CST preparation, but leave Ba and Sr in the residue which had the potential to be employed as raw material for metallic Ba and Sr metallurgy. In the synthesis process, waste CRT panel glass was firstly treated by supercritical water (SCW)-NaOH solution for Si extraction, then sol-gel and hydrothermal treatments were used for CST preparation. 80% of Si in the glass could be extracted into the solution, while Sr and Ba were enriched in the residue in the form of Sr(2)SiO(4) and Ba(2)Si(3)O(8), respectively. Sr and Ba contents in the residue were 2-3 times higher than those in the raw glass. SEM, XRD and TEM results indicated that CST was successfully synthesized. Ion exchanging experiments showed that the batch distribution coefficient of the synthesized CST to Cs(+) was up to 1.2x10(4) mL/g at pH 0.26.

[1]  E. Bernardo,et al.  Sintering behaviour and mechanical properties of Al2O3 platelet-reinforced glass matrix composites obtained by powder technology , 2004 .

[2]  Chonglin Song,et al.  Crystalline Silicotitanate: a New Type of Ion Exchanger for Cs Removal from Liquid Waste , 2009 .

[3]  J. F. Walker,et al.  CESIUM REMOVAL FROM HIGH-pH, HIGH-SALT WASTEWATER USING CRYSTALLINE SILICOTITANATE SORBENT , 1997 .

[4]  Pascal G. Yot,et al.  Elaboration and characterisation of foam glass from cathode ray tubes , 2005 .

[5]  E. Karamanova,et al.  Recycling of CRT panel glass as fluxing agent in the porcelain stoneware tile production , 2008 .

[6]  A. Clearfield,et al.  The origin of ion exchange selectivity in a porous framework titanium silicate , 2007 .

[7]  A. Clearfield,et al.  Optimizing Synthesis of Na2Ti2SiO7 - 2H2O (Na-CST) and Ion Exchange Pathways for Cs0.4H1.6Ti2SiO7 - H2O (Cs-CST) Determined from in situ Synchrotron X-ray Powder Diffraction , 2005 .

[8]  E. Bernardo,et al.  Micro- and macro-cellular sintered glass-ceramics from wastes , 2007 .

[9]  Timothy G. Townsend,et al.  Characterization of Lead Leachability from Cathode Ray Tubes Using the Toxicity Characteristic Leaching Procedure , 2000 .

[10]  A. Clearfield,et al.  The mechanism responsible for extraordinary Cs ion selectivity in crystalline silicotitanate. , 2008, Journal of the American Chemical Society.

[11]  Danping Chen,et al.  A Novel Process Utilizing Subcritical Water to Remove Lead from Wasted Lead Silicate Glass , 2004 .

[12]  M. Andrews Glass formation development and testing for the vitrification of cesium-loaded Crystalline Silicotitanate (CST) , 1997 .

[13]  Teh Fu Yen,et al.  Evaluation of Biopolymer-Modified Concrete Systems for Disposal of Cathode Ray Tube Glass , 2005, Journal of the Air & Waste Management Association.

[14]  ION EXCHANGE OF SEVERAL RADIONUCLIDES ON THE HYDROUS CRYSTALLINE SILICOTITANATE, UOP IONSIV IE-911 , 1999 .

[15]  A. R. Boccaccini,et al.  Innovative manufacturing technique for glass matrix composites: extrusion of recycled TV set screen glass reinforced with Al2O3 platelets , 2003 .

[16]  M. Ribes,et al.  The characterization of waste cathode-ray tube glass. , 2006, Waste management.

[17]  Fu-Shen Zhang,et al.  A novel process utilizing subcritical water and nitrilotriacetic acid to extract hazardous elements from MSW incinerator fly ash. , 2006, Science of the Total Environment.

[18]  A. Clearfield,et al.  Synthesis, Crystal Structures, and Ion-Exchange Properties of a Novel Porous Titanosilicate , 1994 .

[19]  Fernanda Andreola,et al.  Cathode ray tube glass recycling: an example of clean technology , 2005, Waste management & research : the journal of the International Solid Wastes and Public Cleansing Association, ISWA.

[20]  D. Gu,et al.  Estimation of Cesium Ion Exchange Distribution Coefficients for Concentrated Electrolytic Solutions When Using Crystalline Silicotitanates , 1995 .

[21]  E. Bernardo,et al.  Development and mechanical characterization of Al2O3 platelet-reinforced glass matrix composites obtained from glasses coming from dismantled cathode ray tubes , 2005 .

[22]  Richard G. Compton,et al.  Towards greener disposal of waste cathode ray tubes via ultrasonically enhanced lead leaching , 2001 .

[23]  A. Clearfield,et al.  Selectivity for Cs and Sr in Nb-substituted titanosilicate with sitinakite topology , 2003 .

[24]  E. Bernardo,et al.  Mechanical properties of metal-particulate lead-silicate glass matrix composites obtained by means of powder technology , 2003 .

[25]  D. Gu,et al.  Cs+ Ion Exchange Kinetics in Complex Electrolyte Solutions Using Hydrous Crystalline Silicotitanates , 1997 .

[26]  Mengjun Chen,et al.  Lead recovery and the feasibility of foam glass production from funnel glass of dismantled cathode ray tube through pyrovacuum process. , 2009, Journal of hazardous materials.

[27]  Pascal G. Yot,et al.  Effects of temperature, reaction time and reducing agent content on the synthesis of macroporous foam glasses from waste funnel glasses , 2006 .

[28]  Kazumichi Yanagisawa,et al.  Preparation of foamed glasses from CRT TV glass by means of hydrothermal hot-pressing technique , 2008 .

[29]  E. Bernardo,et al.  Glass foams from dismantled cathode ray tubes , 2006 .

[30]  D. Gu,et al.  Use of silicotitanates for removing cesium and strontium from defense waste , 1994 .

[31]  Pascal G. Yot,et al.  The changes in lead silicate glasses induced by the addition of a reducing agent (TiN or SiC) , 2005 .

[32]  Pascal G. Yot,et al.  Mechanical behaviour and thermal and electrical properties of foam glass , 2007 .

[33]  R. Ewing,et al.  Synthesis and characterization of a new microporous cesium silicotitanate (SNL-B) molecular sieve , 2000 .

[34]  S. Hreglich,et al.  Reutilization and stabilization of wastes by the production of glass foams , 2007 .