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研究生: 莊亞凡
Chuang, Ya-Fan
論文名稱: 以光游離偵檢器(PID)評估及管制作業場所多重化學性物質暴露及衍生臭味之研究
A study on assessing and controlling the exposure of multiple chemicals and derived odors in workplaces by using a photoionization detector (PID)
指導教授: 蔡朋枝
Tsai, Perng-Jy
學位類別: 碩士
Master
系所名稱: 醫學院 - 環境醫學研究所
Department of Environmental and Occupational Health
論文出版年: 2020
畢業學年度: 108
語文別: 中文
論文頁數: 84
中文關鍵詞: 揮發性有機化合物臭味強度光游離偵檢器暴露評估管制方法
外文關鍵詞: VOCs, odor intensity, PID, exposure assessment, control method
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  • 台灣光電產業發達,在作業場所中使用大量有機溶劑作為清洗用途,其造成勞工之暴露濃度雖可能低於容許濃度,但衍生之臭味則仍可能造成不適。截至目前為止,針對作業場所臭味的研究仍相當有限,於其評估與管制技術方面更是匱乏。有鑑於直讀式儀器具即時量測及特別是對簡易操作之優點,本研究乃以光游離偵檢器(Photo Ionization Detector,PID)進行作業場所臭味及暴露濃度之現場評估及管制技術開發。本研究以某光電廠作為研究場所,選取共10個製程,利用不銹鋼採樣桶進行全空氣採樣,再送至認證實驗室以GC/MS分析環境中揮發性有機化合物種類及濃度,並利用臭味活性值(Odor Activity Value,OAV)之計算找出環境主要致臭物。另外,本研究選定兩製程,並以其作業環境空氣中總和濃度TE (Total Exposure)之5、10、15、20、25、30、40、50、60、70、80、90、100倍及十分之一暴露容許濃度製備嗅袋,每個嗅袋皆以PID量測其揮發性有機化合物之總濃度(PIDR)及臭味強度 OI (Odor Intensity),以瞭解二者之關係。研究結果顯示光電廠主要致臭物為異丙醇、丙酮、乙醇、甲苯、苯乙烯、醋酸丁酯、丙二醇甲醚及丙二醇甲醚乙酸酯。以這8種主要致臭物配製嗅袋,發現依各製程濃度之嗅袋其OI測定結果皆小於0.04 (1 ppm參考氣體正丁醇)。另本研究選定的兩製程(Oven製程及Photo製程)製備5~100倍濃度及1/10 PEL-TWA之嗅袋,結果發現OI與TE濃度之間在前述選定的兩製程均有良好相關性,其R2分別為0.97及0.99,而PIDR與濃度之間也具備高度相關性,其分別為0.99及0.97。本研究將作業場所之OI管制在0.5之下,並將PIDR警戒值設定在1/10 PEL-TWA濃度下,研究結果顯示當OI為0.5時,PIDR警戒值對Oven製程及Photo製程分別為72.77及36.18 ppm;而當濃度為1/10 PEL-TWA時,PIDR之警戒值則分別為23.39及22.56 ppm。以上結果顯示以濃度為1/10 PEL-TWA時之PIDR警戒值可同時達到作業場所臭味及暴露濃度之管制目的。

    The optoelectronic industries are blooming in Taiwan. Though lots of organic solvents are being used as cleaning materials in the workplace, the exposure concentration is still much lower than that regulated by the law. However, odors derived from the above chemicals might cause uncomforted on humans. But studies related to workplace odor are still very limited, especially for those associated with odor evaluation and control. Considering the advantages of providing real-time reading data and easy operability of the direct reading instrument, this study aims to develop control methods for the odor and exposure concentration in workplaces by using a photoionization detector (PID). The present study selected 10 processes of a optoelectronics industry and used canister to collect gas samples. Odor activity value (OAV) is used to find out the main odorants. Preparing the chemical mixtures based on the total exposure concentration (TE) collected at field in bags (including 5, 10, 15, 20, 25, 30, 40, 50, 60, 70, 80, 90, 100 field collected TE concentrations, and 1/10 PEL-TWA), and the panels were used to judge the odor intensity (OI). PID was used to measure the concentration of total volatile organic compounds (PIDR) of each bag. Relationships were established between OI and TE concentration and between PIDR and TE concentration for selecting suitable PID alarm limited values (PIDAlarm). Results show that odor intensity of the concentration at field in bags are constantly lower than 0.04 (1 ppm by reference to the odorant n-butanol). The isopropanol (IPA), acetone, ethanol, styrene, toluene, propylene glycol methyl ether (PGME), propylene glycol methyl ether acetate (PGMEA), butyl acetate were found to be the chemicals the main odorants. The correlations of two selected processes (i.e., the Oven and Photo process) between OI and TE concentration, and PIDR and TE concentration are excellent (R2 = 0.97 and 0.99, and 0.99 and 0.97, respectively). Results show that if OI is set at 0.5, the PIDAlarm is found to be 72.77 and 36.18 ppm; and if the exposure concentration is set at 0.1 TE, the PIDAlarm is 23.39 and 22.56 ppm for the selected two processes of the Oven and Photo, respectively. The above results suggest that the PIDAlarm set as 0.1 TE would be more feasible for simultaneously controlling exposure concentrations and odors in the above two processes.

    摘要 I 總目錄 VI 表目錄 VIII 圖目錄 IX 第一章 前言 1 1-1 研究背景 1 1-2 研究目的 2 第二章 文獻回顧 3 2-1 薄膜電晶體液晶顯示器(TFT-LCD)產業 3 2-1-1 薄膜電晶體液晶顯示器(TFT-LCD)的生產流程介紹 3 2-1-1-1 光電產業薄膜電晶體Array製程 4 2-1-1-2 光電薄膜電晶體Cell製程 6 2-1-1-3 光電薄膜電晶體Module製程 7 2-1-2 TFT-LCD揮發性有機化合物種類及其危害 8 2-1-3 TFT-LCD業之法令規範 9 2-1-3-1 各國對光電相關產業空氣汙染之法令規範 9 2-1-3-2 我國光電產業空氣污染及排放標準 11 2-2 揮發性有機化合物 13 2-2-1 揮發性有機化合物偵測方式 14 2-2-2 直讀式光游離偵檢器 17 2-2-3 直讀式光游離偵檢器於揮發性有機化合物作業場所之應用 18 2-3 臭味(異味) 20 2-3-1 臭味特徵 21 2-3-2 臭味來源 27 2-3-3 臭味測定及評估方法 28 2-3-4 臭味法規規範 31 2-3-4-1 各國針對臭味之法令規範 31 2-3-4-2 我國針對臭味之法令規範 32 2-3-5 臭味評估方式之應用 33 2-3-6 光游離偵檢器評估臭味之應用 34 第三章 研究方法與設備 35 3-1 研究架構 35 3-2 現場暴露濃度調查 37 3-2-1 研究區域 37 3-2-2 採樣策略 38 3-2-3 揮發性有機化合物空氣採樣 38 3-3 分析主要致臭物 41 3-3-1 臭味活性值 41 3-3-2 主要致臭物之暴露容許濃度總和 41 3-4 臭味強度判定 42 3-4-1 臭味強度測定員選擇 43 3-4-2 臭味強度測定法選擇 44 3-4-3 嗅袋製備 47 3-4-3-1 嗅袋清洗 47 3-4-3-2 嗅袋內氣體濃度配製 47 3-5 光游離偵檢器 48 第四章 結果與討論 49 4-1 現場暴露濃度調查 49 4-2 主要致臭物 51 4-2-1 臭味活性值之計算結果 51 4-2-2 主要致臭物暴露容許濃度總和之推估 51 4-3 臭味強度測定結果 54 4-3-1 嗅袋濃度選擇 54 4-3-2 臭味強度測定結果 54 4-4 光游離偵檢器之量測結果 57 4-4-1 嗅袋濃度之PIDR值 57 4-4-2 光游離偵檢器之警戒值PIDAlarm訂定 57 第五章 結論與建議 60 5-1 結論 60 5-2 建議 61 5-3 研究限制 61 第六章 參考文獻 62 第七章 附錄 66

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