Emissions of PCDD/Fs and PCBs during the Cold Start-up of Municipal Solid Waste Incinerators

被引:20
作者
Guo, Chun-Jou [1 ]
Wang, Mao-Sung [2 ]
Lin, Sheng-Lun [2 ,3 ]
Mi, Hsiao-Hsuan [4 ]
Wang, Lin-Chi [5 ]
Chang-Chien, Guo-Ping [3 ,6 ]
机构
[1] Natl Cheng Kung Univ, Dept Environm Engn, Tainan 70101, Taiwan
[2] Cheng Shiu Univ, Ctr Gen Educ, Kaohsiung 83347, Taiwan
[3] Cheng Shiu Univ, Super Micro Mass Res & Technol Ctr, Kaohsiung 83347, Taiwan
[4] Chia Nan Univ Pharm & Sci, Dept Environm Engn & Sci, Tainan 71743, Taiwan
[5] Cheng Shiu Univ, Dept Civil Engn & Engn Informat, Kaohsiung 83347, Taiwan
[6] Cheng Shiu Univ, Dept Cosmet & Fash Styling, Kaohsiung 83347, Taiwan
关键词
Polychlorinated dibenzo-p-dioxins; Polychlorinated dibenzofurans; Polychlorinated biphenyls; Municipal solid waste incinerators; Cold start-up; DIBENZO-P-DIOXINS; DEPOSITION;
D O I
10.4209/aaqr.2014.06.0118
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
This study investigated the emissions of polychlorinated dibenzo-p-dioxins, dibenzofurans (PCDD/Fs) and polychlorinated biphenyls (PCBs) from 45-hr cold start-up operations (from the ambient temperature) of two municipal solid waste incinerators (MSWIs). Fifteen samples were collected during the whole process, while the sampling period was divided as follows: (1) the initial stage (25-250 degrees C); (2) the second stage (250-850 degrees C), and the final stage (850-1000 degrees C). The peak of total (PCDD/F + PCB) (WHO2005-TEQ) concentration occurred during the second stage of the cold start-up. This could because the temperature in the combustion chamber reached 295-359 degrees C, within the temperature window (250-450 degrees C) of PCDD/F reformation by de novo synthesis. However, both PCDD/F and PCB (WHO2005-TEQ) concentrations were still 2.8-3.8 times higher than the regulated standards in Taiwan 45 hours after the cold start-up began, demonstrating significant memory effects. Higher PCB/(PCDD/F + PCB) TEQ fractions were observed during the initial stage of cold start-up. This is probably due to the higher volatilities of memorized PCB-126 and -169 than PCDD/F congeners, thus making them more easily released into the flue gas. On the other hand, the total (PCDD/F + PCB) emissions during 45-hr cold start-up were estimated at 46-68 mg WHO2005-TEQ. The annual (PCDD/F + PCB) emissions from normal conditions are generally estimated by the normal operating emissions factor without the cold start-up. The normal annual (PCDD/F + PCB) emission rates of the two MSWIs were 70.7-101 mg WHO2005-TEQ, including once cold start-up emission, and these increased to 142-480 mg WHO2005-TEQ, up by 65-458%, if one to eight times of cold start-up were included. Therefore, reducing unnecessary start-ups could be more important with regard to controlling the PCDD/F and PCB emissions than only attempting to increase the pollutant removal efficiency in the steady operations of MSWIs.
引用
收藏
页码:1593 / U358
页数:35
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