Characterization of MSWI fly ash through mineralogy and water extraction

2011 ◽  
Vol 55 (5) ◽  
pp. 524-534 ◽  
Author(s):  
Athanasius P. Bayuseno ◽  
Wolfgang W. Schmahl
2010 ◽  
Vol 69 ◽  
pp. 123-128 ◽  
Author(s):  
Salvatore Andini ◽  
Raffaele Cioffi ◽  
Francesco Colangelo ◽  
Claudio Ferone ◽  
Fabio Montagnaro ◽  
...  

In this work three samples of MSWI ash have been stabilized in systems containing coal fly ash and able to give geopolymers through a polycondensation reaction. Monolithic products were obtained with both MSWI ashes as received and after chloride partial removal by water washing. The polycondensation products have been characterized qualitatively by means of FT-IR spectroscopy and scanning electron microscopy (SEM) and quantitatively through the determination of the amount of reacted water and silicate. Differently from traditional cement based stabilization systems, those based on geopolymerization show a chemical behaviour almost insensitive to the presence of chlorides and sulphates in the MSWI ash. On the other hand, the microstructure is strongly affected by the content of soluble salts.


2009 ◽  
Vol 162 (1) ◽  
pp. 161-173 ◽  
Author(s):  
Yangsheng Liu ◽  
Liting Zheng ◽  
Xiaodong Li ◽  
Shaodong Xie

2018 ◽  
Vol 40 (26) ◽  
pp. 3502-3511 ◽  
Author(s):  
Tengtun Xu ◽  
Li’ao Wang ◽  
Yunmin Zeng ◽  
Xue Zhao ◽  
Lei Wang ◽  
...  
Keyword(s):  
Fly Ash ◽  

Chemosphere ◽  
2007 ◽  
Vol 68 (5) ◽  
pp. 880-886 ◽  
Author(s):  
Y. Kakuta ◽  
T. Matsuto ◽  
Y. Tojo ◽  
H. Tomikawa

2018 ◽  
Vol 80 ◽  
pp. 101-111 ◽  
Author(s):  
Bing Du ◽  
Jiantao Li ◽  
Wen Fang ◽  
Yili Liu ◽  
Shuyao Yu ◽  
...  
Keyword(s):  
Fly Ash ◽  

2021 ◽  
Vol 299 ◽  
pp. 02020
Author(s):  
Jing Wang ◽  
Chang-Jung Sun ◽  
Han Liu ◽  
Jiehua Li ◽  
Yan Zhang

At present, municipal solid waste incineration (MSWI) fly ash is mainly based on the solidification agent and then landfilled. How to make the fly ash harmless and reuse it will become an important step in the circular economy. In this study, the fly ash was treated by water extraction and milling to remove the soluble chloride ions and stabilize the heavy metals, and then the perforated plate was prepared by adjusting the composition and sintering technology. Research on biofilm colonization on the perforated plates is expected to achieve the purpose of stabilizing and recycling the fly ash. The fly ash is subjected to a solid-liquid ratio of 1:5 with two-stage water extraction, 2h ball milling, and then mixed at a mass ratio of waste glass powder, Palygorskite powder and the milled fly ash of 7:2:1, and calcined at 850°C for 20 minutes to prepare perforated plate. The results show that the prepared perforated plate has a rough surface, developed internal porosity, and its water absorption rate is 19.5%. The perforated plate is used as the biofilm carrier to be applied to the biological contact oxidation tank, and the natural biofilm colonization method is adopted for the 36-day biofilm culture. The average growth rate of the biofilm on the perforated plate reached 672.22 mg/(L·d), and the maximum microbial biomass was 12.1g/L.


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