Memory Effects of Polychlorinated Dibenzo-p-dioxin and Furan Emissions in a Laboratory Waste Incinerator

被引:18
作者
Wu, Jhong-Lin [1 ,2 ,3 ]
Lin, Ta-Chang [1 ,2 ]
Wang, Lin-Chi [4 ]
Chang-Chien, Guo-Ping [5 ,6 ]
机构
[1] Natl Cheng Kung Univ, Dept Environm Engn, Tainan 70101, Taiwan
[2] Natl Cheng Kung Univ, Sustainable Environm Res Labs, Tainan 70101, Taiwan
[3] Natl Cheng Kung Univ, Environm Resource & Management Res Ctr, Tainan 70101, Taiwan
[4] Cheng Shiu Univ, Dept Civil Engn & Geomat, Kaohsiung 83347, Taiwan
[5] Cheng Shiu Univ, Super Micro Mass Res & Technol Ctr, Kaohsiung 83347, Taiwan
[6] Cheng Shiu Univ, Dept Cosmet & Fash Styling, Kaohsiung 83347, Taiwan
关键词
PCDD/Fs; Stack flue gas; Laboratory waste; Incineration; Memory effect; DE-NOVO FORMATION; MUNICIPAL WASTE; WET SCRUBBERS; START-UP; PCDD/F; COMBUSTION; PREDICTION; BIPHENYLS; VAPOR; GAS;
D O I
10.4209/aaqr.2013.05.0179
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Laboratory wastes are discharged from experimental, testing, or analysis processes, and contain various toxic chemical compounds with a high heating-value and a high chlorine content (> 9%). Elevated PCDD/F (polychlorinated dibenzo-pdioxin and furan) emissions during start-up stages are caused by combustion of waste with high chlorine contents, incomplete combustion, and so called "memory effects". Even though the duration of cold start-up is short compared with the hours of continuous steady operation in a waste incinerator, its negative effects with regard to PCDD/F emissions on both human health and the environment cannot be neglected. A full-scale laboratory-waste incinerator which is operated for 10 days in each run and has 15 to 20 runs annually was investigated in this study. Eleven PCDD/F samples of stack flue gas were collected during the cold start-up periods (for 60.5 hrs). The gas temperature of the primary combustion chamber was above 850 degrees C, and was maintained at between 850 and 900 degrees C by injecting diesel fuel without waste feed. For first 1.5-7.5 hours, the PCDD/F concentration in the stack flue gas was as high as 0.656-1.15 ng I-TEQ/Nm(3). Afterward, during hours 10.5-35.5 and 54.5-60.5, this reduced to 0.159-0.459 and 0.218-0.254 ng I-TEQ/Nm(3), respectively. Based on principal component analysis (PCA) and the L/H ratio, the results revealed a higher L/H ratio (1.23) before hour 32, indicating that less chlorinated PCDD/F homologues (tetra and penta) dominated, while after hour 32 more chlorinated PCDD/F homologues (hexa, hepta and Octa) had a higher mass concentration and the L/H ratio fell to 0.42. These results indicate that the PCDD/F emissions during cold start-up were caused by memory effects and thermal desorption. Therefore, in order to reduce the PCDD/F emissions from the stack flue gas of waste incinerators, is highly recommended that a higher amount of activated carbon injection is used in front of the bag filters.
引用
收藏
页码:1168 / 1178
页数:11
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