School of Chemical and Blasting Engineering, Anhui University of Science and Technology, Huainan, Anhui, 232001, PR China.
School of Chemical and Blasting Engineering, Anhui University of Science and Technology, Huainan, Anhui, 232001, PR China; Anhui Provincial Institute of Modern Coal Processing Technology, Anhui University of Science and Technology, Huainan, Anhui, 232001, PR China.
J Environ Manage. 2024 Sep;367:122035. doi: 10.1016/j.jenvman.2024.122035. Epub 2024 Aug 5.
Vitrification is a promising treatment for municipal solid waste incineration fly ash (MSWI-FA); however, high energy consumption due to the high MSWI-FA fusion temperature limits the development and application of this technique. In this study, fine slag ash (FSA) derived from coal gasification and coal gangue ash (CGA) were mixed with MSWI-FA to reduce the ash fusion temperature. The transformation of minerals in ash during thermal treatment was examined via X-ray diffraction and thermodynamic equilibrium calculations. The ash flow behaviour was observed using a thermal platform microscope, and the silicate structure was quantified using Raman spectra. The co-melting mechanisms for the mixed ash were systematically investigated. Results indicate that the flow temperature (FT) of the mixed ash exhibited an initial decrease and subsequent increase as a function of the addition ratio of FSA or CGA. Lowest ash FT of 1215 °C and 1223 °C were recorded for addition of 50% FSA and 50% CGA, respectively; further, these temperatures were lowered by > 285 °C and >277 °C respectively, relative to FT of the MSWI-FA. The transformation of minerals and silicate structure during mixed ash heating was responsible for the variation in the ash fusion temperature. CaO in MSWI-FA tended to react with mullite, quartz and haematite in FSA and CGA, forming minerals such as anorthite, gehlenite, and andradite with relatively low melting points. The addition of FSA or CGA caused changes in the silicate network structure of the mixed ash. In particular, 50% FSA incorporation caused the transformation of Q and Q to Q, whereas 50% CGA introduction resulted in the conversion of Q and Q into Q and Q + Q, respectively. The silicate network depolymerised, causing reduction in the ash fusion temperature and increasing the melting rate.
熔融固化是一种很有前途的城市固体废物焚烧飞灰(MSWI-FA)处理方法;然而,由于 MSWI-FA 的熔融温度较高,导致该技术的发展和应用受到限制。在本研究中,将煤气化细渣灰(FSA)和煤矸石灰(CGA)与 MSWI-FA 混合,以降低灰的熔融温度。通过 X 射线衍射和热力学平衡计算研究了热处理过程中灰中矿物的转化。利用热台显微镜观察灰的流动行为,并通过拉曼光谱定量分析硅酸盐结构。系统研究了混合灰的共熔机制。结果表明,混合灰的流动温度(FT)随 FSA 或 CGA 添加比例的增加先降低后升高。当添加 50% FSA 和 50% CGA 时,混合灰的最低 FT 分别为 1215°C 和 1223°C;进一步降低了约 285°C 和 277°C,相对于 MSWI-FA 的 FT。混合灰加热过程中矿物和硅酸盐结构的转化是导致灰熔融温度变化的原因。MSWI-FA 中的 CaO 倾向于与 FSA 和 CGA 中的莫来石、石英和赤铁矿反应,形成熔点相对较低的钙长石、钙铝黄长石和钙铁辉石等矿物。FSA 或 CGA 的添加导致混合灰的硅酸盐网络结构发生变化。特别是,添加 50% FSA 导致 Q 和 Q 向 Q 的转化,而添加 50% CGA 则分别导致 Q 和 Q 向 Q 和 Q+Q 的转化。硅酸盐网络解聚,导致灰熔融温度降低,熔融速率增加。