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Nanocrystalline and stacking-disordered β-cristobalite AlPO4: the now deciphered main constituent of a municipal sewage sludge ash from a full-scale incineration facility

Published online by Cambridge University Press:  16 April 2015

B. Peplinski*
Affiliation:
BAM Federal Institute for Materials Research and Testing, Berlin, Germany
C. Adam
Affiliation:
BAM Federal Institute for Materials Research and Testing, Berlin, Germany
B. Adamczyk
Affiliation:
BAM Federal Institute for Materials Research and Testing, Berlin, Germany
R. Müller
Affiliation:
BAM Federal Institute for Materials Research and Testing, Berlin, Germany
M. Michaelis
Affiliation:
BAM Federal Institute for Materials Research and Testing, Berlin, Germany
T. Krahl
Affiliation:
Humboldt-Universität zu Berlin, Berlin, Germany
F. Emmerling
Affiliation:
BAM Federal Institute for Materials Research and Testing, Berlin, Germany
*
a) Author to whom correspondence should be addressed. Electronic mail: burkhard.peplinski@bam.de

Abstract

For the first time evidence is provided that a nanocrystalline and stacking-disordered, chemically stabilized β-cristobalite form of AlPO4 occurs in a sewage sludge ash (SSA). This proof is based on a combined X-ray powder diffraction and X-ray fluorescence investigation of an SSA produced at a large-scale fluidized bed incineration facility serving a catching area with a population of 2 million. The structural and chemical characterization was carried out on ‘as received’ SSA samples as well as on solid residues remaining after leaching this SSA in sodium hydroxide solution. Thus, it was ascertained that the observed nanocrystalline and stacking-disordered cristobalite-like component belongs to the aluminum phosphate component of this SSA, rather than to its silicon dioxide component. In addition, a direct proof is presented that the chemically stabilized β-cristobalite form of AlPO4 does crystallize from X-ray amorphous precursors under conditions that mimic the huge heating rate and short retention time (just seconds at T ≈ 850°C), typical for fluidized bed incinerators.

Information

Type
Technical Articles
Copyright
Copyright © International Centre for Diffraction Data 2015 
Figure 0

Table I. Abundance of the main chemical components in the ‘as received’ raw SSAs “F–S”, “Md2” and “D”, according to XRF analysis.

Figure 1

Figure 1. (Color online) Sections of the diffraction patterns of SSA “F–S” ‘as received’ (bottom) and after the second (top) alkaline leaching (blue curves with circles) and of the nanocrystalline and stacking-disordered model sample of the chemically stabilized cubic β-cristobalite form of AlPO4 measured at room temperature (red solid curve). A, anhydrite; C, β-cristobalite form; L, lime; Q, quartz; W, whitlockite type.

Figure 2

Figure 2. (Color online) Sections of the diffraction patterns of SSA “F–S” before (bottom) and after (top) the third alkaline leaching (blue curves with circles) and of the nanocrystalline and stacking-disordered model sample of the chemically stabilized cubic β-cristobalite form of AlPO4 measured at room temperature (red solid curve). The letter “C” indicates the presence of a diffraction line of the β-cristobalite form.

Figure 3

Figure 3. (Color online) Sections of the diffraction patterns of SSA “F–S” ‘as received’ (bottom) and after the fourth (top) alkaline leaching (blue curves with circles) and of the nanocrystalline and stacking-disordered model sample of the chemically stabilized cubic β-cristobalite form of AlPO4 measured at room temperature (red solid curve). C, β-cristobalite form; Q, quartz; W, whitlockite type.

Figure 4

Figure 4. (Color online) Chemical composition of SSA “F–S” in dependence on N, the number of the applied alkaline leaching treatments. XRF data.

Figure 5

Figure 5. (Color online) as Figure 4.

Figure 6

Figure 6. (Color online) as Figure 4.