Journal
JOURNAL OF THE AMERICAN CERAMIC SOCIETY
Volume 86, Issue 9, Pages 1527-1533Publisher
WILEY-BLACKWELL
DOI: 10.1111/j.1151-2916.2003.tb03509.x
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The conversion of bottom ash from fluidized-bed combustion of municipal solid waste (MSW) to zeolite, by means of alkaline hydrothermal treatment (FIT), in 1M NaOH solution, is presented in this work. The transformation of the bottom ash was characterized by X-ray diffraction (XRD), Fourier transform infrared (FTIR) spectroscopy, surface area (BET-N(2)), and scanning electron microscopy (SEM) analyses. As a result of the HT at 100degreesC, Na(6)[AlSiO(4)](6).4H(2)O, of the structural family of zeolites, together with Ca(3)AlFe(SiO(4))(OH)(8), of the structural family of hydrogarnets, began to appear; the surface area of the bottom ash increased 11 times. At 150degreesC, the amount of Na(6)[AlSiO(4)](6).4H(2)O increased and andradite, hydroxylian (Ca(3)Fe(2)(SiO(4))(3-x)(OH)(4-x)), of the structural family of garnet, was formed. After 200degreesC of HT, Na(6)[AlSiO(4)](6).4H(2)O was massively formed together with aluminum tobermorite (Ca(5)Si(5)Al(OH)O(17).5H(2)O); Ca(3)AlFe(SiO(4))(OH)(8) decreased. The surface area of the bottom ash increased 13 times. The conversion of bottom ash in zeolite is considered of great significance, opening new opportunities for stabilization and applications of this type of waste. Zeolite and also the other compounds-aluminum tobermorite, andradite, and Ca(3)AlFe(SiO(4))(OH)(8)-can substitute a variety of ionic species, which allows the bottom ash to be useful for immobilizing toxic and radioactive wastes. An equivalent study was conducted in water instead of NaOH as a reference.
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