B.-P. Zhang, Xiao-Yong Yan, K. Shibata, T. Uda, M. Tada, M. Hirasawa
{"title":"惰性气氛下氧化锌、fe2o3或znfe2o4与聚氯乙烯反应的热重质谱分析","authors":"B.-P. Zhang, Xiao-Yong Yan, K. Shibata, T. Uda, M. Tada, M. Hirasawa","doi":"10.2320/MATERTRANS1989.41.1342","DOIUrl":null,"url":null,"abstract":"The mechanisms of reactions are investigated between polyvinyl chloride and oxides such as ZnO, Fe 2 O 3 and ZnFe 2 O 4 under inert gas atmosphere at high temperature with combined thermogravimetry-mass spectrometry (TG-MS) technique. From the experiments under a constant heating rate of 40 K/min, the following results are obtained. In the case of mixture pellet of ZnO and PVC, the chlorination of Zn in ZnO to ZnCl 2 by Cl in PVC starts at a relatively low temperature about 473 K without the formation of HCl. The chlorination is followed by the de-hydrochlorination of residual un-reacted PVC, also by the further degradation to lower order hydrocarbons, and finally by the evaporation of ZnCl 2 at higher temperature. On the other hand, in the case of ZnO-PVC double layer pellet in which ZnO layer is compacted at the top of PVC layer, PVC decomposition accompanying HCl formation starts at about 523 K, which is similar to the thermal decomposition of pure PVC in the absence of the oxide. The chlorination of Zn is not favored in this case of double layer sample. In the case of Fe 2 O 3 -PVC mixture, the de-hydrochlorination takes place at the temperature range of 513 to 673 K, similarly with the case of the pure PVC decomposition. With increasing temperature, the degradation of de-hydrochlorinated PVC residue to lower hydrocarbons and the stepwise reduction from Fe 2 O 3 to metallic Fe takes, place after the de-hydrochlorination. The reaction scheme of ZnFe 2 O 4 -PVC system shows intermediate character between ZnO-PVC system and Fe 2 O 3 -PVC system. The kinetic mechanisms of the reaction between the oxides and PVC are examined on the basis of the experimental results.","PeriodicalId":18264,"journal":{"name":"Materials Transactions Jim","volume":"22 1","pages":"1342-1350"},"PeriodicalIF":0.0000,"publicationDate":"2000-10-20","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"56","resultStr":"{\"title\":\"Thermogravimetric-Mass Spectrometric Analysis of the Reactions between Oxide (ZnO, Fe 2 O 3 or ZnFe 2 O 4 ) and Polyvinyl Chloride under Inert Atmosphere\",\"authors\":\"B.-P. Zhang, Xiao-Yong Yan, K. Shibata, T. Uda, M. Tada, M. Hirasawa\",\"doi\":\"10.2320/MATERTRANS1989.41.1342\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"The mechanisms of reactions are investigated between polyvinyl chloride and oxides such as ZnO, Fe 2 O 3 and ZnFe 2 O 4 under inert gas atmosphere at high temperature with combined thermogravimetry-mass spectrometry (TG-MS) technique. From the experiments under a constant heating rate of 40 K/min, the following results are obtained. In the case of mixture pellet of ZnO and PVC, the chlorination of Zn in ZnO to ZnCl 2 by Cl in PVC starts at a relatively low temperature about 473 K without the formation of HCl. The chlorination is followed by the de-hydrochlorination of residual un-reacted PVC, also by the further degradation to lower order hydrocarbons, and finally by the evaporation of ZnCl 2 at higher temperature. On the other hand, in the case of ZnO-PVC double layer pellet in which ZnO layer is compacted at the top of PVC layer, PVC decomposition accompanying HCl formation starts at about 523 K, which is similar to the thermal decomposition of pure PVC in the absence of the oxide. The chlorination of Zn is not favored in this case of double layer sample. In the case of Fe 2 O 3 -PVC mixture, the de-hydrochlorination takes place at the temperature range of 513 to 673 K, similarly with the case of the pure PVC decomposition. With increasing temperature, the degradation of de-hydrochlorinated PVC residue to lower hydrocarbons and the stepwise reduction from Fe 2 O 3 to metallic Fe takes, place after the de-hydrochlorination. The reaction scheme of ZnFe 2 O 4 -PVC system shows intermediate character between ZnO-PVC system and Fe 2 O 3 -PVC system. The kinetic mechanisms of the reaction between the oxides and PVC are examined on the basis of the experimental results.\",\"PeriodicalId\":18264,\"journal\":{\"name\":\"Materials Transactions Jim\",\"volume\":\"22 1\",\"pages\":\"1342-1350\"},\"PeriodicalIF\":0.0000,\"publicationDate\":\"2000-10-20\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"56\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"Materials Transactions Jim\",\"FirstCategoryId\":\"1085\",\"ListUrlMain\":\"https://doi.org/10.2320/MATERTRANS1989.41.1342\",\"RegionNum\":0,\"RegionCategory\":null,\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"\",\"JCRName\":\"\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"Materials Transactions Jim","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.2320/MATERTRANS1989.41.1342","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
Thermogravimetric-Mass Spectrometric Analysis of the Reactions between Oxide (ZnO, Fe 2 O 3 or ZnFe 2 O 4 ) and Polyvinyl Chloride under Inert Atmosphere
The mechanisms of reactions are investigated between polyvinyl chloride and oxides such as ZnO, Fe 2 O 3 and ZnFe 2 O 4 under inert gas atmosphere at high temperature with combined thermogravimetry-mass spectrometry (TG-MS) technique. From the experiments under a constant heating rate of 40 K/min, the following results are obtained. In the case of mixture pellet of ZnO and PVC, the chlorination of Zn in ZnO to ZnCl 2 by Cl in PVC starts at a relatively low temperature about 473 K without the formation of HCl. The chlorination is followed by the de-hydrochlorination of residual un-reacted PVC, also by the further degradation to lower order hydrocarbons, and finally by the evaporation of ZnCl 2 at higher temperature. On the other hand, in the case of ZnO-PVC double layer pellet in which ZnO layer is compacted at the top of PVC layer, PVC decomposition accompanying HCl formation starts at about 523 K, which is similar to the thermal decomposition of pure PVC in the absence of the oxide. The chlorination of Zn is not favored in this case of double layer sample. In the case of Fe 2 O 3 -PVC mixture, the de-hydrochlorination takes place at the temperature range of 513 to 673 K, similarly with the case of the pure PVC decomposition. With increasing temperature, the degradation of de-hydrochlorinated PVC residue to lower hydrocarbons and the stepwise reduction from Fe 2 O 3 to metallic Fe takes, place after the de-hydrochlorination. The reaction scheme of ZnFe 2 O 4 -PVC system shows intermediate character between ZnO-PVC system and Fe 2 O 3 -PVC system. The kinetic mechanisms of the reaction between the oxides and PVC are examined on the basis of the experimental results.