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Thermal degradation of PVC: A review

机译:PVC的热降解:综述

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摘要

This review summarized various chemical recycling methods for PVC, such as pyrolysis, catalytic dechlo-rination and hydrothermal treatment, with a view to solving the problem of energy crisis and the impact of environmental degradation of PVC. Emphasis was paid on the recent progress on the pyrolysis of PVC, including co-pyrolysis of PVC with biomass/coal and other plastics, catalytic dechlorination of raw PVC or Cl-containing oil and hydrothermal treatment using subcritical and supercritical water. Understanding the advantage and disadvantage of these treatment methods can be beneficial for treating PVC properly. The dehydrochlorination of PVC mainly happed at low temperature of 250-320 ℃. The process of PVC dehydrochlorination can catalyze and accelerate the biomass pyrolysis. The intermediates from dehydrochlorination stage of PVC can increase char yield of co-pyrolysis of PVC with PP/PE/PS. For the catalytic degradation and dechlorination of PVC, metal oxides catalysts mainly acted as adsorbents for the evolved HCl or as inhibitors of HCl formation depending on their basicity, while zeolites and noble metal catalysts can produce lighter oil, depending the total number of acid sites and the number of accessible acidic sites. For hydrothermal treatment, PVC decomposed through three stages. In the first region (T< 250 ℃), PVC went through dehydrochlorination to form polyene; in the second region (250 ℃ < T < 350 ℃), polyene decomposed to low-molecular weight compounds; in the third region (350℃<T), polyene further decomposed into a large amount of low-molecular weight compounds.
机译:综述了热解法,催化脱氯法和水热处理法等各种PVC化学回收方法,以期解决能源危机和PVC降解对环境的影响。重点关注了PVC热解的最新进展,包括PVC与生物质/煤和其他塑料的共热解,生PVC或含Cl的油的催化脱氯以及使用亚临界和超临界水进行水热处理。了解这些处理方法的优缺点对正确处理PVC有好处。 PVC的脱氯化氢主要在250-320℃的低温下进行。 PVC脱氯化氢的过程可以催化和加速生物质的热解。 PVC脱氯化氢阶段的中间体可以提高PVC与PP / PE / PS共热解的炭收率。对于PVC的催化降解和脱氯作用,金属氧化物催化剂主要根据其碱性来充当所释放的HCl的吸附剂或HCl的形成抑制剂,而沸石和贵金属催化剂可以生成更轻的油,具体取决于酸位和可访问的酸性位点的数量。对于水热处理,PVC分三个阶段分解。在第一个区域(T <250℃),PVC经过脱氯化氢反应生成多烯。在第二区域(250℃<T <350℃)中,多烯分解为低分子量化合物。在第三区(350℃<T),多烯进一步分解为大量的低分子量化合物。

著录项

  • 来源
    《Waste Management》 |2016年第2期|300-314|共15页
  • 作者单位

    State Key Laboratory of Coal Combustion, Huazhong University of Science and Technology, 1037 Luoyu Road, 430074 Wuhan, Hubei, China;

    State Key Laboratory of Coal Combustion, Huazhong University of Science and Technology, 1037 Luoyu Road, 430074 Wuhan, Hubei, China;

    State Key Laboratory of Coal Combustion, Huazhong University of Science and Technology, 1037 Luoyu Road, 430074 Wuhan, Hubei, China;

    State Key Laboratory of Coal Combustion, Huazhong University of Science and Technology, 1037 Luoyu Road, 430074 Wuhan, Hubei, China;

    State Key Laboratory of Coal Combustion, Huazhong University of Science and Technology, 1037 Luoyu Road, 430074 Wuhan, Hubei, China;

  • 收录信息
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    PVC; Recycling; Co-pyrolysis; Catalytic pyrolysis; Dechlorination;

    机译:PVC;回收;共热解;催化热解;脱氯;

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