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研究生: 杜立凱
Tu, Li-Kai
論文名稱: 工業加熱製程中多溴二苯醚之削減及控制技術
Control and Reduction Technique for Poly Brominated Diphenyl Ethers in the Industrial Heating Process
指導教授: 吳義林
Wu, Yee-Lin
李文智
Lee, Wen-Jhy
學位類別: 博士
Doctor
系所名稱: 工學院 - 環境工程學系
Department of Environmental Engineering
論文出版年: 2013
畢業學年度: 101
語文別: 英文
論文頁數: 85
中文關鍵詞: 火力發電廠廢棄物焚化廠多溴二苯醚濾袋
外文關鍵詞: Polybrominated diphenyl ethers, waste incinerators, coal-fired power plants, filter bags
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  • 本研究共調查了兩座醫療廢棄物焚化爐(MWI-A、MWI-B)、兩座民生廢棄物焚化爐(MSWI-A、MSWI-B)以及一座燃煤火力發電廠(CFPP)中之多溴二苯醚於工業加熱製程之煙道氣以及各空氣汙染防治設備單元中之含量以前發展多溴二苯醚之削減及控制技術。此外,本研究亦採集了周界大氣之樣本以便了解這些排放源對於周遭環境之衝擊。
    本研究因MSWI-A、MSWI-B以及CFPP此三者之每日處理容量而選定其為調查對象。以叢集分析調查煙道排放之多溴二苯醚與各周界大氣受體採樣點採得之多溴二苯醚的特徵相似性,並判定相關性。結果顯示,兩者間並無直接相關性。之後,本研究以Industrial Source Complex Short Term 3 (ISCST3)進行多溴二苯醚之大氣擴散模擬,根據模擬結果, MSWI-A、MSWI-B以及CFPP各僅貢獻採樣期間0.0173% ±0.0194%的總多溴二苯醚濃度。因此,叢集分析及擴散摹擬的結果顯示MSWI-A、MSWI-B以及CFPP並非環境中主要的多溴二苯醚來源,也因此,由空氣汙染防治設備採得之飛灰可能是較為急迫的環境問題。
    為調查其多溴二苯醚之去除率及多溴二苯醚之質量分布,本研究選定兩座日處理量相仿但分別配置單濾袋(MWI-A)及雙濾袋系統(MWIB)之醫療廢棄物焚化爐,。單濾袋系統(MWI-A)之多溴二苯醚去除效率為99.60%,但其每噸垃圾須消耗60.1公斤的活性碳以吸附汙染物,而雙濾袋系統(MWI-B)的多溴二苯醚去除效率為99.86%,與MWI-A之結果相近,但其每噸垃圾僅須消耗15.9公斤的活性碳以吸附汙染物,因此可減少棘手的廢棄活性碳處置問題。本研究考慮兩種可能途徑為多溴二苯醚在雙濾袋系統中之去除機制。其一為粒狀及部分的氣狀多溴二苯醚遭單濾袋率先去除,之後剩下的氣狀多溴二苯醚因而能由第二個濾袋較好的吸收;其二為顆粒大小,較大的顆粒較易由濾袋去除。根據以上結果,將能建立目前付之闕如的多溴二苯醚之控制策略進行改進並而進一步的減少廢棄活性碳及多溴二苯醚進入環境中。

    In this study, two medical waste incinerators (MWI-A and MWI-B), two municipal solid incinerators (MSWI-A and MSWI-B) and a coal fired power plant were investigated for PBDE concentrations and contents in the heating process for developing control and reduction technique for PBDEs. Ambient air samples were also collected in order to determine the impact caused by these plants to the environments.
    MSWI-A, MSWI-A and CFPP were chosen to assess their impacts to the surrounding via cluster analysis and dispersion modeling because they have much larger treatment capacities per day than those of MWIs. Cluster analysis was first carried out to determine the relationship of PBDE characteristics between each spot. Later, PBDE dispersion modeling in the atmosphere was applied by using ISCST3 (Industrial Source Complex Short Term 3) to assess the impact of the above two municipal solid waste incinerators and one coal-fired power plant on the ambient air. The total-PBDE concentrations in the ambient air were between 24.9 and 139 pg Nm-3, averaging 59.8 pg Nm-3 (n = 16). The BDE-209was the most predominant among all 14 PBDE congeners, which contributed more than 58% of total-PBDE mass to the ambient air. However, the results of cluster analysis indicated that no direct correlations existed among the emission sources (MSWI-A, MSWI-B, CFPP) and the receptors (sampling sites). From the results of dispersion modeling, the a total PBDE concentration in ambient air contributed by the MSWI-A, MSWI-B, CFPP together were found to be 0.0173% ±0.0194% during the sampling period. Hence, the results of both cluster analysis and dispersion modeling showed that MSWI-A, MSWI-B, and CFPP were not the major contributors of PBDEs to the ambient air environment. The ashes collected from the air pollution control devices of both the MSWIs and the CFPP are probably a more imminent environmental issue.
    Furthermore, two continuously operating medical waste incinerators (MWIs), MWI-A and MWI-B, were investigated for the PBDE removal efficiencies of the air pollution control devices and their PBDE mass distributions. The mean PBDE removal efficiency by the single bag filter system with 60.1 kg-activated carbon (AC) tonne-waste-1 of MWI-A was 99.60%, while that by the dual bag filter system with 15.9 kg AC tonne-waste-1 of MWI-B was 99.86%. While the removal efficiencies are similar, dual bag filter system can tremendously reduce activated carbon usage in the system.
    According to the results, control strategies for the PBDE removal in medical waste incinerators should be further improved to reduce the discharge of PBDEs and wasted activated carbon to the environment.

    內容 摘要 II Abstract IV 致謝 VI Contents VII List of Tables X Lists of Figures XII Chapter 1 Introduction 1 Chapter 2 Literatures review 3 2.1 Property and toxicity of PBDEs 3 2.2 Applications of PBDE products 5 2.2.1 Pentabromodiphenyl ether (penta-BDE) 5 2.2.2 Octabromodiphenyl ether (octa-BDE) 5 2.2.3 Decabromodiphenyl ether (deca-BDE) 5 2.3 Sources of PBDE emissions 6 2.3.1 Combustion Sources 6 2.3.2 Indoor Air 9 2.4 Primary PBDE exposure routes for human 10 2.5 Polybrominated dibenzodioxin/furans (PBDD/Fs) 14 2.6 Industrial heating process 16 2.6.1 Municipal solid waste incinerator 16 2.6.2 Medical waste incinerator 16 2.6.3 Coal-fired power plant 17 2.7 Reduction and Control technologies for PBDEs 18 2.7.1 Heating process 18 2.7.2 Activated carbon injection 18 2.7.3 Dual bag filter system 18 Chapter 3 Experimental Section 20 3.1 Basic Information for the MWIs, MSWIs, One Coal-fired Power Plant and the Ambient Air Sampling Sites 20 3.2 Sample Collection 23 3.3 Sample Analysis 25 3.4 Dispersion Modeling 27 Chapter 4 Results and discussion 29 4.1 Impacts of PBDE emissions to the surrounding media 29 4.1.1 PBDE concentrations in flue gases 29 4.1.2 PBDE emission rates and factors 32 4.1.3 PBDE concentrations in the ambient air sampling sites 36 4.1.4 Cluster analysis for PBDEs in ambient air 40 4.1.5 Dispersion modeling for PBDEs 42 4.2 Fates of PBDEs in incinerating process 48 4.2.1 PBDE contents in the bottom residue and fly ashes 48 4.2.2 Fate and mass distribution of PBDEs in the systems 58 4.3 PBDE removal efficiencies by the air pollution control devices 66 Chapter 5 Conclusions and suggestions 71 5.1 Conclusions 71 5.2 Suggestions 74 Reference 75 Curriculum Vitae 82

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