Gao Peipei, Hu Zichao, Sheng Yue, Pan Weitong, Ding Lu, Tang Longfei, Chen Xueli, Wang Fuchen
Engineering Research Center of Resource Utilization of Carbon-containing Waste with Carbon Neutrality, Ministry of Education, Shanghai 200237, PR China; Shanghai Engineering Research Center of Coal Gasification, East China University of Science and Technology, Shanghai 200237, PR China.
Engineering Research Center of Resource Utilization of Carbon-containing Waste with Carbon Neutrality, Ministry of Education, Shanghai 200237, PR China; Shanghai Engineering Research Center of Coal Gasification, East China University of Science and Technology, Shanghai 200237, PR China.
Sci Total Environ. 2024 Feb 20;912:169572. doi: 10.1016/j.scitotenv.2023.169572. Epub 2023 Dec 23.
The release of chlorine during the pyrolysis of actual municipal plastic waste (MPW) was studied. Firstly, thermogravimetry-Fourier transform infrared (TG-FTIR) was analyzed to investigate the chlorine release behavior. Then, the effect of temperature on chlorine migrations was investigated by fast pyrolysis experiments in a fixed bed reactor. Results showed that chlorine released mainly between 241 and 353 °C in the form of HCl or chloroesters during MPW pyrolysis. After pyrolysis, chlorine was mainly distributed in the pyrolytic gas (74.34-82.89 %) and char (10.17-21.29 %). However, the release of chlorine was inhibited due to the melting behavior of MPW at <350 °C. Besides, the relative contents and types of organic chlorinated compounds in liquid products were both decreased with temperature. It was observed that polyethylene terephthalate (PET) was the greatest contributor to the formation of organic chlorinated compounds during MPW pyrolysis. Meanwhile, the pyrolysis of PET was significantly promoted by the HCl released from polyvinyl chloride (PVC). Subsequently, the pathways for the formation of organic chlorinated compounds through the co-pyrolysis of PVC and PET were proposed, including the initial degradation and subsequent chlorination of PET. These findings provided new insights into the release and regulation of chlorine-containing pollutants during actual MPW pyrolysis.
研究了实际城市塑料废弃物(MPW)热解过程中氯的释放情况。首先,通过热重-傅里叶变换红外光谱法(TG-FTIR)分析来研究氯的释放行为。然后,在固定床反应器中进行快速热解实验,研究温度对氯迁移的影响。结果表明,MPW热解过程中氯主要在241至353℃之间以HCl或氯酯的形式释放。热解后,氯主要分布在热解气(74.34 - 82.89%)和焦炭(10.17 - 21.29%)中。然而,由于MPW在<350℃时的熔化行为,氯的释放受到抑制。此外,液体产物中有机氯化合物的相对含量和种类均随温度降低。观察到聚对苯二甲酸乙二酯(PET)是MPW热解过程中有机氯化合物形成的最大贡献者。同时,聚氯乙烯(PVC)释放的HCl显著促进了PET的热解。随后,提出了通过PVC和PET共热解形成有机氯化合物的途径,包括PET的初始降解和随后的氯化。这些发现为实际MPW热解过程中含氯污染物的释放和调控提供了新的见解。