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气氛对 MSWI 飞灰热处理过程中重金属形态转化的影响:通过热力学平衡计算。

Effect of Atmospheres on Transformation of Heavy Metals during Thermal Treatment of MSWI Fly Ash: By Thermodynamic Equilibrium Calculation.

机构信息

School of Chemical Engineering, Anhui University of Science and Technology, Huainan 232001, China.

Institute of Energy, Hefei Comprehensive National Science Center, Hefei 230031, China.

出版信息

Molecules. 2021 Dec 27;27(1):131. doi: 10.3390/molecules27010131.

DOI:10.3390/molecules27010131
PMID:35011362
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC8746557/
Abstract

The vaporization behaviors of eight heavy metals (Pb, Zn, Cu, Cd, Cr, Co, Mn, and Ni) in municipal solid wastes incineration (MSWI) fly ash during thermal treatment under air atmosphere (21% O/79% N), an inert atmosphere (100% N), and a reducing atmosphere (50% CO/50% N) were evaluated based on a thermodynamic equilibrium calculation by FactSage 8.1. The results show that the reducing atmosphere promotes the melting of MSWI fly ash, resulting in a more liquid phase than in air or an inert atmosphere. Except for Cd, the formation of liquids can dissolve heavy metals and reduce their vaporization ratio. In the air and inert atmospheres, Pb, Zn, Cu, Co, Mn, and Ni vaporize mainly in the form of metallic chlorides, while Cd volatilizes in the form of metallic Cd (g) and CdO (g). In the reducing atmosphere, Co, Mn, and Ni still vaporize as chlorides. Zn and Cd mainly vaporize in the form of Zn (g) and Cd (g), respectively. In terms of Pb, in addition to its chlorides, the volatiles of Pb contain some Pb (g) and PbS (g). Cr has a low vaporization ratio, accounting for 2.4% of the air atmosphere. Cr, on the other hand, readily reacts with Ca to form water-soluble CrCaO, potentially increasing Cr leaching. Except for Cd, the results of this study suggest that the reducing atmosphere is used for the thermal treatment of MSWI fly ash because it promotes the melting of fly ash and thus prevents heavy metal vaporization.

摘要

基于 FactSage 8.1 热力学平衡计算,评估了在空气气氛(21% O/79% N)、惰性气氛(100% N)和还原气氛(50% CO/50% N)下,城市固体废物焚烧(MSWI)飞灰中八种重金属(Pb、Zn、Cu、Cd、Cr、Co、Mn 和 Ni)在热处理过程中的蒸发行为。结果表明,还原气氛促进 MSWI 飞灰的熔化,导致液相比空气或惰性气氛更多。除 Cd 外,液体的形成可以溶解重金属并降低其蒸发率。在空气和惰性气氛中,Pb、Zn、Cu、Co、Mn 和 Ni 主要以金属氯化物的形式蒸发,而 Cd 以金属 Cd(g)和 CdO(g)的形式挥发。在还原气氛中,Co、Mn 和 Ni 仍以氯化物的形式蒸发。Zn 和 Cd 分别主要以 Zn(g)和 Cd(g)的形式蒸发。对于 Pb,除了其氯化物之外,挥发物还含有一些 Pb(g)和 PbS(g)。Cr 的蒸发率较低,占空气气氛的 2.4%。Cr 很容易与 Ca 反应生成水溶性 CrCaO,可能会增加 Cr 的浸出。除 Cd 外,本研究结果表明,还原气氛用于 MSWI 飞灰的热处理,因为它促进了飞灰的熔化,从而防止了重金属的蒸发。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/eaacf98f52ba/molecules-27-00131-g012.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/2adcac8d92e2/molecules-27-00131-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/996671473287/molecules-27-00131-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/a1a0e9ef1e37/molecules-27-00131-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/6433aa0be9a0/molecules-27-00131-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/0f525211f905/molecules-27-00131-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/2abae0024c22/molecules-27-00131-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/5b5967b6a2cf/molecules-27-00131-g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/eaacf98f52ba/molecules-27-00131-g012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/3ced1b12bde2/molecules-27-00131-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/830bdf9d35d6/molecules-27-00131-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/71f0fd15d282/molecules-27-00131-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/78c129e3311e/molecules-27-00131-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/2adcac8d92e2/molecules-27-00131-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/996671473287/molecules-27-00131-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/a1a0e9ef1e37/molecules-27-00131-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/6433aa0be9a0/molecules-27-00131-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/0f525211f905/molecules-27-00131-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/2abae0024c22/molecules-27-00131-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/5b5967b6a2cf/molecules-27-00131-g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1be7/8746557/eaacf98f52ba/molecules-27-00131-g012.jpg

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