Investigation of the cyclic separation of dioxins from municipal solid waste incineration fly ash by using fat

Liu, Jun; Wang, Zhengdong; Li, Zhenlin; Xie, Guangming; Zhang, Weizhuo; Jin, Hesong; Xing, Feng

doi:10.1016/j.jclepro.2024.141840

Cited by 3 publications

(1 citation statement)

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“…In general, MSW incineration treatment can reduce its mass by 70% and its volume by 90% [2,3], while the rate of unburned ash in the ash residue is 0.7-2%. The residual rates of MSWIBA and fly ash generation from MSW incineration are approximately 20% and 2% [4], respectively. Even after incineration, a large amount of MSW incineration bottom ash (MSWIBA) is still generated [5].…”

Section: Introductionmentioning

confidence: 99%

Preparation and Hydration Properties of Sodium Silicate-Activated Municipal Solid Waste Incineration Bottom Ash Composite Ground-Granulated Blast Furnace Slag Cementitious Materials

Deng,

Wu,

Xia

et al. 2024

Materials

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The production of municipal solid waste incineration bottom ash (MSWIBA) is substantial and has the potential to replace cement, despite challenges such as complex composition, uneven particle size distribution, and low reactivity. This paper employs sodium silicate activation of MSWIBA composite Ground-granulated Blast Furnace slag (GGBS) to improve the reactivity in preparing composite cementitious materials. It explores the hydration performance of the composite cementitious materials using isothermal calorimetric analysis, Fourier-transform infrared (FTIR) spectroscopy, XRD physical diffraction analysis, and SEM tests. SEM tests were used to explore the hydration properties of the composite gelling. The results show that with an increase in MSWIBA doping, the porosity between the materials increased, the degree of hydration decreased, and the compressive strength decreased. When the sodium silicate concentration increased from 25% to 35%, excessive alkaline material occurred, impacting the alkaline effect. This inhibited particle hydration, leading to a decrease in the degree of hydration and, consequently, the compressive strength. The exothermic process of hydration can be divided into five main stages; quartz and calcite did not fully participate in the hydration reaction, while aluminum did. The vibrational peaks of Si-O-Ti (T = Si and Al) were present in the material. The vibrational peaks of XRD, FTIR, and SEM all indicate the presence of alumosilicate network structures in the hydration products, mainly N-A-S-H and C-A-S-H gels.

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