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垃圾焚烧飞灰中重金属的热稳定化条件及机理 被引量:7

Thermal stabilization condition and mechanism of heavy metals in flyash of solid waste incineration
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摘要 研究了生活-农业混合型垃圾焚烧飞灰与单一生活垃圾焚烧飞灰(简称混合型飞灰与单一型飞灰)热处理过程中的重金属挥发特性与稳定化效果,并结合FT-IR、XRD检测手段对稳定化机理进行了探讨。结果表明,单一型飞灰中重金属的挥发性普遍高于混合型飞灰,垃圾源氯含量对重金属的挥发性有明显影响。飞灰中Mn、Cr不易挥发,Zn、Cu较易挥发,Pb、Cd挥发性很强,热处理温度超过1 000℃时挥发率都超过50%。800℃为相对最优的热处理温度,兼顾了热处理过程重金属稳定化与抑制挥发。800℃以上时飞灰形成了稳定的硅酸盐结构体系,是重金属热处理后难以浸出的主要机理。 The volatility and the stabilization of heavy metals in flyash in municipality agriculture mixed waste incineration( Type A) and municipal solid waste incineration( Type B) were investigated. And the heavy metals stabilization mechanism was studied by using FT-IR and XRD. The results indicate that the volatility of heavy metals is higher in type B than that in type A,and is significantly affected by the content of chloride in waste source. The volatility of heavy metals in fly ash varies in a sequence of Mn,Cr Zn,Cu Pb,Cd. More than 50% of Pb and Cd are volatilized when the temperature exceeds 1 000 ℃. The relatively optimal thermal treatment temperature is 800 ℃ and the heavy metals stabilization is higher and the evaporation rate is lower. The primary mechanism of heavy metals stabilization is the formation of stable silicate structure system above 800 ℃.
出处 《燃料化学学报》 EI CAS CSCD 北大核心 2013年第12期1532-1538,共7页 Journal of Fuel Chemistry and Technology
基金 国家自然科学基金(51108100) 广西自然科学基金(2013GXNSFBA019249) 广西教育厅科研项目(200103YB020) 广西师范大学博士启动基金项目
关键词 垃圾焚烧 热处理 稳定化 挥发 solid waste incineration thermal treatment stabilization evaporation
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参考文献17

  • 1AHMARUZZAMAN M. A review on the utilization of fly ash[ J]. Prog Energy Combust Sci, 2010, 36(3) : 327-363. 被引量:1
  • 2MARTIN P, MICHAL T, PETR K, LADISLAV B. Waste incineration with production of clean and reliable energy[ J ]. Clean Technol Environ Policy. 2011. 13(4): 595-605. 被引量:1
  • 3于洁,孙路石,向军,胡松,苏胜,邱建荣.模拟城市生活垃圾热处理过程中Cd与Pb挥发特性研究[J].燃料化学学报,2012,40(8):1019-1024. 被引量:4
  • 4JUNG C H, MATSUTO T, TANAKA N, OKADA T. Metal distribution in incineration residues of municipal solid waste (MSW) in Japan [J]. Waste Manage, 2004, 24(4): 381-391. 被引量:1
  • 5JIANG Y H, XI B D, LI X J. Effect of water-extraction on characteristics of melting and solidification of fly ash from municipal solid waste incinerator[ J]. J Hazard Mater, 2009, 161 (2/3) : 871-877. 被引量:1
  • 6JIN J, LI X D, CHI Y, YAN J H. Co-disposal of heavy metals containing waste water and medical waste incinerator fly ash by hydrothermal process with addition of sodium carbonate: A case study on Cu (II) removal[ J]. Water Air Soil Poll, 2010, 209 (1/4) : 391-400. 被引量:1
  • 7裘娜.不同粒径城市垃圾焚烧飞灰中重金属的浸出规律研究[J].广东化工,2012,39(4):274-276. 被引量:2
  • 8NOWAK B, PESSL A, ASCHENBRENNER P, Heavy metal removal from municipal solid waste CHARLES H K L, JOHN P B, GORDON M. Technol Environ Policy, 2011, 13(4) : 607-615. 被引量:1
  • 9SZENTANNAI P, MATTENBERGER H, RECHBERGER H, HERMANN L, WINTER F. fly ash by chlorination and thermal treatment[ J]. J Hazard Mater, 2010, 179 (1/3) : 323-333. 被引量:1
  • 10SAIKIA N, CORNELIS G, MERTENS G, ELSEN J, VAN BALEN K, VAN GERVEN T, VANDECASTEELE C. Assessment of Pb-slag, MSWI bottom ash and boiler and fly ash for using as a fine aggregate in cement mortar[J]. J Hazard Mater, 2008, 154(1/3) : 766-777. 被引量:1

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