{"title":"污水处理厂污泥的非等温动力学分析","authors":"Ruihua Shao, P. Fang, Juan Ren, Q. Si","doi":"10.1109/RSETE.2011.5965238","DOIUrl":null,"url":null,"abstract":"The thermal decomposition kinetics of sewage sludge was investigated by means of non-isothermal TG at different heating rates of 5 K·min<sup>−1</sup>, 10 K·min<sup>−1</sup>, 15 K·min<sup>−1</sup>, 20 K·min<sup>−1</sup> and 30 K·min<sup>−1</sup>. The non-isothermal kinetic parameters and mechanical functions were analyzed by means of Flynn-Wall-Ozawa equation and Coats-Redfern equation. Before and after DTG peak, Flynn-Wall-Ozawa and Coats-Redfern were used to determine the kinetic parameters. Before and after DTG peak, E<inf>α→0</inf>=102.17 kJ·mol<sup>−1</sup>, 88.17 kJ·mol<sup>−1</sup> respectively. Before DTG peak, the most probable kinetic function was No.3 G-B Equation, and the corresponding mechanism was controlled by Three-Dimensional Diffusion (cylindrical symmetry). The apparent activation energy and the pre-exponential constant (A) were E<inf>β→0</inf>=107.44KJ·mol<sup>−1</sup>, lnA<inf>β→0</inf>=12.64 respectively. After DTG peak, the most probable kinetic function was No.13 Avrami-Erofeev Equation (n=4), and the corresponding mechanism was controlled by random nuclear producing and growing process. The apparent activation energy and the pre-exponential constant (A) were E<inf>β→0</inf>=88.34 KJ·mol<sup>−1</sup>, lnA<inf>β→0</inf>=14.25 respectively.","PeriodicalId":6296,"journal":{"name":"2011 International Conference on Remote Sensing, Environment and Transportation Engineering","volume":"130 1","pages":"4198-4201"},"PeriodicalIF":0.0000,"publicationDate":"2011-06-24","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Non-isothermal kinetic analysis of sewage sludge from wastewater treatment plant\",\"authors\":\"Ruihua Shao, P. Fang, Juan Ren, Q. Si\",\"doi\":\"10.1109/RSETE.2011.5965238\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"The thermal decomposition kinetics of sewage sludge was investigated by means of non-isothermal TG at different heating rates of 5 K·min<sup>−1</sup>, 10 K·min<sup>−1</sup>, 15 K·min<sup>−1</sup>, 20 K·min<sup>−1</sup> and 30 K·min<sup>−1</sup>. The non-isothermal kinetic parameters and mechanical functions were analyzed by means of Flynn-Wall-Ozawa equation and Coats-Redfern equation. Before and after DTG peak, Flynn-Wall-Ozawa and Coats-Redfern were used to determine the kinetic parameters. Before and after DTG peak, E<inf>α→0</inf>=102.17 kJ·mol<sup>−1</sup>, 88.17 kJ·mol<sup>−1</sup> respectively. Before DTG peak, the most probable kinetic function was No.3 G-B Equation, and the corresponding mechanism was controlled by Three-Dimensional Diffusion (cylindrical symmetry). The apparent activation energy and the pre-exponential constant (A) were E<inf>β→0</inf>=107.44KJ·mol<sup>−1</sup>, lnA<inf>β→0</inf>=12.64 respectively. After DTG peak, the most probable kinetic function was No.13 Avrami-Erofeev Equation (n=4), and the corresponding mechanism was controlled by random nuclear producing and growing process. The apparent activation energy and the pre-exponential constant (A) were E<inf>β→0</inf>=88.34 KJ·mol<sup>−1</sup>, lnA<inf>β→0</inf>=14.25 respectively.\",\"PeriodicalId\":6296,\"journal\":{\"name\":\"2011 International Conference on Remote Sensing, Environment and Transportation Engineering\",\"volume\":\"130 1\",\"pages\":\"4198-4201\"},\"PeriodicalIF\":0.0000,\"publicationDate\":\"2011-06-24\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"2011 International Conference on Remote Sensing, Environment and Transportation Engineering\",\"FirstCategoryId\":\"1085\",\"ListUrlMain\":\"https://doi.org/10.1109/RSETE.2011.5965238\",\"RegionNum\":0,\"RegionCategory\":null,\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"\",\"JCRName\":\"\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"2011 International Conference on Remote Sensing, Environment and Transportation Engineering","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.1109/RSETE.2011.5965238","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
Non-isothermal kinetic analysis of sewage sludge from wastewater treatment plant
The thermal decomposition kinetics of sewage sludge was investigated by means of non-isothermal TG at different heating rates of 5 K·min−1, 10 K·min−1, 15 K·min−1, 20 K·min−1 and 30 K·min−1. The non-isothermal kinetic parameters and mechanical functions were analyzed by means of Flynn-Wall-Ozawa equation and Coats-Redfern equation. Before and after DTG peak, Flynn-Wall-Ozawa and Coats-Redfern were used to determine the kinetic parameters. Before and after DTG peak, Eα→0=102.17 kJ·mol−1, 88.17 kJ·mol−1 respectively. Before DTG peak, the most probable kinetic function was No.3 G-B Equation, and the corresponding mechanism was controlled by Three-Dimensional Diffusion (cylindrical symmetry). The apparent activation energy and the pre-exponential constant (A) were Eβ→0=107.44KJ·mol−1, lnAβ→0=12.64 respectively. After DTG peak, the most probable kinetic function was No.13 Avrami-Erofeev Equation (n=4), and the corresponding mechanism was controlled by random nuclear producing and growing process. The apparent activation energy and the pre-exponential constant (A) were Eβ→0=88.34 KJ·mol−1, lnAβ→0=14.25 respectively.