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富铁炼钢轧钢污泥的热解行为和残渣特性。

Pyrolysis Behaviors and Residue Properties of Iron-Rich Rolling Sludge from Steel Smelting.

机构信息

National Engineering Research Center of Sintering and Pelletizing Equipment System, Zhongye Changtian International Engineering Co., Ltd., Changsha 410205, China.

School of Engineering, GongQing Institute of Science and Technology, Jiujiang 332020, China.

出版信息

Int J Environ Res Public Health. 2022 Feb 14;19(4):2152. doi: 10.3390/ijerph19042152.

DOI:10.3390/ijerph19042152
PMID:35206336
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC8871665/
Abstract

Iron-rich rolling sludge (FeRS) represents a kind of typical solid waste produced in the iron and steel industry, containing a certain amount of oil and large amounts of iron-dominant minerals. Pyrolysis under anaerobic environment can effectively eliminate organics at high temperatures without oxidation of Fe. This paper firstly investigated comprehensively the pyrolysis characteristics of FeRS. The degradation of organics in FeRS mainly occurred before 400 °C. The activation energy for pyrolysis of FeRS was extremely low, ca. 5.44 kJ/mol. The effects of pyrolytic temperature, atmosphere, heating rate, and stirring on pyrolysis characteristics were conducted. Commonly, the yield of solid residues maintained around 85 wt.%, with approximately 13 wt.% oil and 2 wt.% gas. Due to the low yield of oil and gas, their further utilization remains difficult despite CO introduction which could upgrade their quality. The solid residues after pyrolysis exhibited porous properties with co-existence of micropores and mesopores. Combined with the high content of zero-valent iron, magnetic property, hydrophobic characteristic, and low density, the solid residues could be further utilized for water pollution control and soil remediation. Moreover, the solid residues were suitable for sintering to recover valuable iron resources. However, the solid residues also contained certain heavy metals, such as Cd, Cr, Cu, Ni, Pb, and Zn, which might cause secondary pollution during their utilization. In particular, the toxic Cr possessed high content, which should be treated with detoxification and removal. This paper provides fundamental information for pyrolysis of FeRS and utilization of solid residues.

摘要

富铁滚动污泥(FeRS)是钢铁行业产生的一种典型固体废物,含有一定量的油和大量以铁为主的矿物质。在厌氧环境下进行热解可以在不使铁氧化的情况下有效地在高温下消除有机物。本文首先全面研究了 FeRS 的热解特性。FeRS 中有机物的降解主要发生在 400°C 之前。FeRS 热解的活化能极低,约为 5.44 kJ/mol。研究了热解温度、气氛、加热速率和搅拌对热解特性的影响。通常,固体残渣的产率保持在 85wt%左右,其中约有 13wt%的油和 2wt%的气体。由于油和气的产率较低,尽管引入 CO 可以提高其质量,但进一步利用仍然困难。热解后的固体残渣具有多孔性质,同时存在微孔和中孔。结合高含量的零价铁、磁性、疏水性和低密度,固体残渣可进一步用于水污染控制和土壤修复。此外,固体残渣适合用于烧结以回收有价值的铁资源。然而,固体残渣中还含有一定量的重金属,如 Cd、Cr、Cu、Ni、Pb 和 Zn,在利用过程中可能会造成二次污染。特别是有毒的 Cr 含量较高,应进行解毒和去除处理。本文为 FeRS 的热解和固体残渣的利用提供了基础信息。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/1c538a54e175/ijerph-19-02152-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/f042076e3591/ijerph-19-02152-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/9579f6e8d8b4/ijerph-19-02152-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/2c1688b284d8/ijerph-19-02152-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/6fa2ead314c8/ijerph-19-02152-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/d2cabe91116d/ijerph-19-02152-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/fc7456512be6/ijerph-19-02152-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/6014c7bfaef5/ijerph-19-02152-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/0df4cc6f8182/ijerph-19-02152-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/449c942ca9b7/ijerph-19-02152-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/1c538a54e175/ijerph-19-02152-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/f042076e3591/ijerph-19-02152-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/9579f6e8d8b4/ijerph-19-02152-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/2c1688b284d8/ijerph-19-02152-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/6fa2ead314c8/ijerph-19-02152-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/d2cabe91116d/ijerph-19-02152-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/fc7456512be6/ijerph-19-02152-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/6014c7bfaef5/ijerph-19-02152-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/0df4cc6f8182/ijerph-19-02152-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/449c942ca9b7/ijerph-19-02152-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/922f/8871665/1c538a54e175/ijerph-19-02152-g010.jpg

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