KU Leuven, Department of Chemical Engineering, Process and Environmental Technology Lab, Sint-Katelijne-Waver, Belgium.
Laboratoire de Génie Chimique, Université de Toulouse, CNRS, INPT, UPS, Toulouse, France.
J Environ Manage. 2021 Jan 15;278(Pt 1):111527. doi: 10.1016/j.jenvman.2020.111527. Epub 2020 Oct 27.
The worldwide production of polymeric foam materials is growing due to their advantageous properties of light weight, high thermal insulation, good strength, resistance and rigidity. Society creates ever increasing amounts of poly-urethane (PU) waste. A major part of this waste can be recycled or recovered in order to be put into further use. The PU industry is committed to assist and play its part in the process. The recycling and recovery of PU foam cover a range of mechanical, physical, chemical and thermo-chemical processes. In addition to the well-documented mechanical and chemical processing options, thermo-chemical treatments are important either as ultimate disposal (incineration) or towards feedstock recovery, leading to different products according to the thermal conditions of the treatment. The review focuses on these thermo-chemical and thermal processes. As far as pyrolysis is concerned, TDI and mostly polyol can be recovered. The highest recovery yields of TDI and polyols occur at low temperatures (150-200 °C). It is however clear from literature that pure feedstock will not be produced, and that a further upgrading of the condensate will be needed, together with a thermal or alternative treatment of the non-condensables. Gasification towards syngas has been studied on a larger and industrial scale. Its application would need the location of the PU treatment plant close to a chemical plant, if the syngas is to be valorized or considered in conjunction with a gas-fired CHP plant. Incineration has been studied mostly in a co-firing scheme. Potentially toxic emissions from PU combustion can be catered for by the common flue gas cleaning behind the incineration itself, making this solution less evident as a stand-alone option: the combination with other wastes (such as municipal solid waste) in MSWI's seems the indicated route to go.
由于其重量轻、隔热性能好、强度高、耐腐蚀性和刚性好等优点,全球聚合物泡沫材料的产量正在增长。社会产生的聚亚安酯(PU)废物越来越多。其中很大一部分可以回收或再利用,以便进一步使用。PU 行业致力于协助并在这一过程中发挥作用。回收和再利用 PU 泡沫涵盖了一系列机械、物理、化学和热化学过程。除了有充分记录的机械和化学加工选择外,热化学处理对于最终处理(焚烧)或原料回收很重要,根据处理的热条件,可导致不同的产品。该综述重点介绍了这些热化学和热过程。就热解而言,可以回收 TDI 和大部分多元醇。TDI 和多元醇的最高回收率发生在低温(150-200°C)下。然而,从文献中可以清楚地看出,不会产生纯原料,需要对冷凝物进行进一步升级,以及对不可冷凝物进行热或替代处理。在更大规模和工业规模上研究了气化制合成气。如果要将合成气进行增值利用或与燃气热电联产厂一起考虑,那么需要将 PU 处理厂的位置靠近化工厂。焚烧在很大程度上是在联合燃烧方案中进行研究的。PU 燃烧产生的潜在有毒排放物可以通过焚烧本身后面的常见烟道气清洁来处理,这使得这种解决方案作为独立选项不太明显:与其他废物(如城市固体废物)在 MSWI 中的结合似乎是一个可行的途径。