環境資源報告成果查詢系統

104年度高雄市都市垃圾焚化廠戴奧辛連續採樣分析方法測試及排放減量計畫

中文摘要 垃圾焚化廠排氣戴奧辛濃度易隨垃圾組成、燃燒條件等運轉狀況、起停爐以及廢氣處理裝置是否正常運轉等產生很大的變化,現行手動採樣方法實難以掌握排氣中戴奧辛的濃度實態及變動狀況。因此,開發本土化的NCU-CS3技術實屬必要,本計畫利用NCU-CS3及手動採樣方法確認焚化廠起爐操作及長時間之戴奧辛排放,以正確量測焚化廠平日及起爐期間之排放係數,並據以計算全年之PCDD/Fs排放量。本計畫之執行對國內戴奧辛總量管制具有正面助益,可減緩民眾對都市垃圾焚化廠排放戴奧辛之疑慮,提升政府於環境保護施政的決心與公信力。 研究結果顯示第一次起爐後48小時期間,廢棄物開始進料但因燃燒條件及空氣污染防制設備操作皆尚未達穩定,導致高濃度之戴奧辛排放,最高濃度達50.8 ng I-TEQ/Nm3。起爐一週後由於記憶效應導致戴奧辛排放濃度呈緩慢下降趨勢。第二次起爐階段採行有效的改善措施包括(1)嚴格控制起爐過程的CO濃度;(2)起爐前加強人工清理積灰;(3)垃圾投料前增加鹼劑及活性碳噴入量,使濾袋快速形成濾餅,提高戴奧辛的去除效率等。第二次起爐期間戴奧辛排放濃度明顯低於第一次起爐作業,最高濃度值為2.04 ng I-TEQ/Nm3,起爐2天後戴奧辛排放濃度方可穩定維持在0.1 ng-TEQ/Nm3以下(手動採樣&NCU-CS3)。 以NCU-CS3及手動採樣方法確認焚化廠168小時平時操作之戴奧辛排放方面,7組168 小時NCU-CS3 採樣分析結果顯示,僅3組符合環保署公告之大型垃圾焚化爐煙道廢氣中放限值(0.1 ng I-TEQ/Nm3),濃度介於0.072~0.753 ng I-TEQ/Nm3,平均值為0.201 ng I-TEQ/Nm3。此外,每組168小時NCU-CS3採樣期間搭配手動方法採集10樣本,分析結果顯示70組樣本中符合排放限值的比率為77%,濃度介於0.0012~0.3835 ng I-TEQ/Nm3,平均值為0.0609 ng I-TEQ/Nm3。168 小時NCU-CS3及手動採樣方法分析所得戴奧辛排放係數分別為0.845及0.346 μg I-TEQ/ton waste。 長時間戴奧辛排放濃度監控方面,焚化爐參數調整包括(1)鹼劑噴入量:煙囪出口HCl濃度分別控制於19 ppm(正常操作)及15 ppm及(2)活性碳噴入量:0.1、0.24、0.34(正常操作)、0.44 及 0.55 kg/ton waste。18組NCU-CS3採樣結果顯示隨AC噴入量增加,煙囪戴奧辛排放濃度呈現下降的趨勢,ACI+BF技術對戴奧辛的去除效率介於98.7~99.4%,而鹼劑噴入量之影響並不顯著。 NCU-CS3之穿透率測試方面,結果顯示第二段XAD-2 樣品匣戴奧辛含量隨冷凝溫度的上升而增加,且提高XAD-2填充量亦可降低樣品穿透率。在使用70克XAD-2及冷凝溫度為50℃之條件下,XAD-2樣品匣戴奧辛濃度佔總濃度之5.4%,入口溫度小於20℃則樣品穿透率均低於1%。此外,採樣管殘留量約佔總濃度之0.9~3.4%,平均值為2.8%,高於第二段XAD-2樣品匣的穿透率(<1%),故採樣完成後清洗採樣管線是必備的工作。計畫期間NCU-CS3等速吸引百分率皆可維持在±5%之內(符合90~110%之規範),擬似標準品回收率亦均符合環保署公告之標準採樣方法回收率規範(70%~130%),顯示NCU-CS3採樣結果具可信度。 藉由NCU-CS3推估高雄仁武化廠二號爐包含起爐操作之戴奧辛年排放量為150 mg I-TEQ/yr,其中兩次起爐操作各佔52%及7%,顯示戴奧辛排放量不能單只依據短期監測(定檢期間)之排放量進行推估,本計畫建立之NCU-CS3系統可進行長時期自動連續採樣將有助於準確推估焚化廠之戴奧辛年排放量。
中文關鍵字 戴奧辛連續自動採樣設備、焚化爐製程改善、排放減量

基本資訊

專案計畫編號 經費年度 104 計畫經費 8786 千元
專案開始日期 2015/11/04 專案結束日期 2016/12/31 專案主持人 張木彬
主辦單位 高雄市政府環境保護局 承辦人 周于翔 執行單位 中央大學

成果下載

類型 檔名 檔案大小 說明
期末報告 06-結案報告本文-05.pdf 9MB

Tests of continuous sampling system and strategies of emission control for a large-scale MWI in Kaohsiung City (2015)

英文摘要 In general, concentrations of polychlorinated dibenzo-p-dioxins (PCDDs) and polychlorinated dibenzofurans (PCDFs) measured in flue gas of municipal wastes incinerators (MWIs) vary significantly with waste component, combustion condition, operation stages and air pollution control devices equipped. Manual or short-time stack sampling process for dioxin-like congeners is the standard sampling method adopted by the Taiwan EPA (Method No. A807). However, it is difficult to include the dioxin emitted during unstable conditions, such as start-up process and abnormal condition. NCU-CS3 is a continuous stack sampling system developed by National Central University, Taiwan. In parallel with the Taiwan EPA standard sampling method (Method No. A807.75C), NCU-CS3 was used to monitor the emission of PCDD/Fs from a large-scale MWI in Kaohsiung city, Taiwan, including the periods of start-up and normal operation. Due to the unstable operating condition, the dioxin emission during start-up procedure (48 hours) could reach the peak of 50.8 ng I-TEQ/Nm3 before gradually decreasing in the following weeks. To reduce PCDD/F concentration in flue gas of the MWI, three measures have been carried out such as (1) reducing CO concentration, (2) removing the fly ash accumulated on the pipe and (3) alkali injection before the start-up procedure. The results obtained from the second measurements indicated the PCDD/Fs concentrations in flue gas measured by both NCU-CS3 and NIEA A807.75C were significantly lower than the first measurement and typically lower than 2.04 ng I-TEQ/Nm3. After 2 days’ operation, the PCDD/F emissions measured by NCU-CS3 and NIEA A807.75C were lower than the emission limit (0.1 ng I-TEQ/Nm3). In addition, the dioxin emissions of 168-hour continuous sampling with NCU-CS3 and NIEA A807.75C ranged from 0.072 to 0.753 ng I-TEQ/Nm3 (0.201 ng I-TEQ/Nm3 in average). Among these measurements (n=7), only three measurements are lower than 0.1 ng I-TEQ/Nm3. At the same time, 70 samples were collected with the NIEA A807.75C method (ten NIEA A807.75C samples correspond to each NCU-CS3 measurement). The measured dioxin emission was 0.0609 ng I-TEQ/Nm3 in average (0.0012~0.3835 ng I-TEQ/Nm3), while 77% samples were lower than the emission limit. The average dioxin emission factors measured by using NCU-CS3 and NIEA A807.75C methods were 0.845 and 0.346 μg I-TEQ/ton-waste, respectively. The effects of relevant operating parameters on PCDD/Fs emission are also evaluated via NCU-CS3, and they include: (1) alkali injection: HCl emission at the stack was controlled at 19 ppm (normal operation) and 15 ppm; (2) activated carbon injection: 0.24, 0.34 (normal operation), 0.44 and 0.55 kg / ton waste. Eighteen NCU-CS3 sampling results indicate that dioxins measured in smokestack decreased with the increase of AC injection rate. The dioxin removal efficiency achieved with ACI + BF technology was between 98.7% and 99.4%. Results indicate that dioxin concentration in 2nd cartridge of the NCU-CS3 increases with increasing cooling temperature. At 50oC, 5.4% of total dioxin concentration penetrated into the 2nd stage XAD-2 cartridge. As the cooling temperature was lower than 20oC, penetration was lower than 1% and could be ignored. The NCU-CS3 system showed reliable results with 70-130% recoveries of surrogate standard, which meets the regulation of standard method (NIEA A807.75C). This new system is capable of automatic, continuous sampling over a long period of time (≤4 weeks), and can accurately measure the PCDD/Fs emitted from MWIs. The PCDD/F emission from the MWI investigated included the start-up procedure via the NCU-CS3 system was around 150 mg I-TEQ/yr. The PCDD/F emission contributed by the first and second start-up procedures were 52% and 7%, respectively. Hence, the PCDD/F emission cannot be accurately quantified by relying on the manual and short-time stack sampling only. NCU-CS3 developed can provide more accurate data for government to enact effective control strategy.
英文關鍵字 polychlorinated dibenzo-p-dioxins, municipal wastes incinerators