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研究生: 蔡政男
Tsai, Cheng-Nan
論文名稱: 拜香燃煙中PAHs與Nitro-PAHs之基因毒性探討
Genotoxicity of PAHs and Nitro-PAHs from Incenses Burning
指導教授: 林達昌
Lin, Ta-Chang
學位類別: 碩士
Master
系所名稱: 工學院 - 環境工程學系
Department of Environmental Engineering
論文出版年: 2005
畢業學年度: 93
語文別: 中文
論文頁數: 142
中文關鍵詞: 基因毒性PAHsNitro-PAHs沙門氏菌Ames Test毒性測試
外文關鍵詞: genotoxicity, PAHs, Nitro-PAHs, Ames Test
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  •   燃香拜拜是國人傳統活動行為,但拜香燃燒時產生的懸浮微粒可能附著PAHs及Nitro-PAHs,影響人體健康,一般寺廟中的工作人員、寺廟附近的居民或家中長期燃香的民眾都會接觸這些污染物質而影響健康。

      本研究為探討不同種類之拜香燃煙所產生之PAHs與Nitro-PAHs,選用了市面上常見九種不同配方和產地的拜香。由於考慮到國人使用拜香的習慣為一次使用三根,所以,本研究中也一次點燃三根拜香,並利用自行設計的採樣器進行採樣,採樣後之濾紙經過萃取、層析、濃縮後以GC-MS分析其中之16種PAHs以及6種Nitro-PAHs,並以元素分析儀得知拜香本身之碳、氫、氧、氮元素含量,最後以Ames Test之沙門桿菌變異種TA98與TA100進行毒性測試比較各種拜香所可能產生的基因毒性。

      結果顯示拜香燃煙中並不含有Nitro-PAHs,而每種拜香燃燒後所產生的PAHs其特徵差別不大,主要都是3環以上的PAHs為主;其中又以Pa、FL、Pry、CHR為主要(71.9 % ~ 50.4 %)。進行毒性試驗後,結果不添加S9皆無反應,但是,添加S9為皆呈現正反應,顯示不同拜香燃煙的萃取物皆會對人體產生基因毒性。而其毒性大小,以TA98而言,毒性大小為新山香(台)>新山香(中)>老山香(台)>料香(台)>沉香(台)>沉香(中)>檜香(中)>老山香(中)>料香(中)。TA100而言,毒性大小為新山香(台)>新山香(中)>老山香(台)>沉香(台)>老山香(中)>沉香(中)>料香(台)>料香(中)> 檜香(中)。由上述可以得知同一種香而言台灣產的拜香毒性皆大於中國製。因子分析中可以發現,影響拜香燃煙所可能產生毒性的主要因子為燃燒時間。元素組成雖然對於毒性大小並無明顯的相關性,但是同一類拜香中含碳量越高者其排放燃煙之毒性也會越高。

     In this study the Ames Test, which offers reduced variability among experiments, requires smaller quantities of test chemicals and eliminate interactive systematic effects, was used to assess genotoxicity of the incense smoke.

     Nine different types of commercially available incenses were selected for this study. During the sampling period, three sticks were burned at the same time and the suspended particulates collected by a custom-designed sampler. Each sample filter was solvent extracted, fractionated, concentrated, and then analyzed by a GC/MS for PAHs and Nitro-PAHs. Elemental analyses on selected elements, including C, H, O, and N, were also performed for each sample. The concentrated extract from each sample was then tested with Ames Test for its genotoxicity. And the genotoxicity of PAHs and Nitro-PAHs from different incenses were measured.

     The results show that nitro-PAHs were not detected in any incense sample. And the composing of PAHs is alike, 3- or higher rings are major compounds. Especially, Pa, FL, Pry, CHR had the highest contributions (71.9 % ~ 50.4 %). The results of Ames test show that all incences exhibited mutagenic reaction only after adding the S9 liver homogenate. The relative genotoxicity of different incences is Hsing Shan (tw)> Hsing Shan (cn)> Lao Shan (tw)> Liao (tw)> Chen (tw)> Chen (cn)> Gui (cn)> Lao Shan (cn)> Liao (cn) as TA98, and Hsing Shan (tw)> Hsing Shan (cn)> Lao Shan (tw)> Chen (tw)> Lao Shan (cn)> Chen (cn)> Liao (tw)> Liao (cn)> Gui (cn) as TA100. For incenses of similar raw materials, Taiwanese incense had higher toxicity then the corresponding Chinese incense.
     
     Major factors affecting toxicity among different incenses include carbon content and combustion duration. It is imortant to note that incenses with higher carbon content generate smoke with higher genotoxicity.

    第一章 前言                 1 1-1 研究動機                1 1-2 研究目的                2 第二章 文獻回顧               3 2-1 拜香的介紹               3 2-1.1 香的種類               3 2-1.2 線香的組成              3 2-1.3 線香的種類              4 2-1.4 有關拜香燃燒之研究          5 2-2 PAHs                  7 2-2.1 PAHs的定義              7 2-2.2 PAHs的形成機制            11 2-2.3 PAHs對人體的危害           13 2-2.4 PAHs毒性評估指標BaPeq         15 2-3 Nitro-PAHs               17 2-3.1 Nitro-PAHs的定義           17 2-3.2 Nitro-PAHs的形成機制         19 2-3.3 Nitro-PAHs對人體的危害        22 2-4安姆氏試驗應用在空氣污染物致突變性之測試 27 2-4.1 安姆氏試驗測試原理          27 2-4.2 安姆氏試驗之優點           30 第三章 實驗方法與步驟            31 3-1 實驗設計                31 3-2 採樣設計                34 3-2.1 採樣設計與規劃            34 3-2.2 採樣設備設計             34 3.2.3 採樣地點               35 3-3 採樣前之準備              36 3-3.1 採樣設備之清理            36 3-3.2 流量校正               36 3-3.3 濾紙的前處理             37 3-3.4 矽膠與無水硫酸鈉之前處理       38 3-4 樣本分析                38 3-4.1 萃取                 38 3-4.2 濃縮                 39 3-4.3 層析(Fractionation)          39 3-4.4 再濃縮與溶劑的轉置          40 3-4.5 GC/MS分析               41 3-4.6 元素分析               42 3-4.7 水份、灰份、可燃份分析        43 3-5 AMES TEST 毒性測試           44 3-5.1 試驗流程               44 3-5.2 基本需求之設備            45 3-5.3 試驗之配藥與菌種培養         47 3-5.4 S9混合液之製備            49 3-5.5 S9試驗程序              51 3-5.6 試驗之數據與毒性判定         54 第四章 數據分析之品質保證及品質控制     56 4-1 空白試驗                56 4-1.1 溶劑空白試驗             56 4-1.2 程序空白試驗             56 4-1.3 毒性空白試驗             56 4-2 標準品回收率測試            60 4-3 標準品檢量線之建立           61 4-4 重複分析                63 第五章 實驗結果與討論            66 5-1 各類拜香的物理特徵           66 5-1.1 元素組成               66 5-1.2燃燒時間、燃燒重量以及產生的總固體懸浮物69 5-1.3 水份、灰份、可燃份          72 5-2 各類拜香所產生的PAHs及Nitro-PAHs    76 5-2.1 PAHs分布               76 5-2.2 Nitro-PAHs分布            82 5-2.3 BaPeq                 82 5-3 元素分析與各參數之相關性分析      89 5-3.1 元素分析與燃燒拜香的物理特徵     90 5-3.2 元素分析與燃燒拜香產生的PAHs     91 5-3.3 元素分析與燃燒拜香產生的PAHs之BaPeq  92 5-4 Ames毒性測試結果            94 5-5 綜合毒性分析              100 5-5.1 元素分析與毒性試驗結果相關性分析   101 5-5.2 物理燃燒狀況與毒性試驗結果相關性分析 102 5-5.3 PAHs與毒性試驗結果相關性分析     104 第六章 結論與建議              105 6-1 結論                   105 6-2 建議                   107 參考文獻                   109 附錄一 十六種PAHs與六種Nitro-PAHs之離子選擇 119 附錄二 十六種PAHs之檢量線          120 附錄三 六種Nitro-PAHs的檢量線        136 附錄四 GC/MS之偵測極限           138 附錄五 各種拜香燃煙所產生的PAHs       139 自述                     142

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