博碩士論文 93223028 詳細資訊




以作者查詢圖書館館藏 以作者查詢臺灣博碩士 以作者查詢全國書目 勘誤回報 、線上人數:25 、訪客IP:3.145.93.227
姓名 林建志(CHIEN-CHIH LIN)  查詢紙本館藏   畢業系所 化學學系
論文名稱 台灣平地與高山大氣汞之監測與比較
相關論文
★ Synthesis of a Photosensitizer Containing a Benzimidazole Carbene Ligand with Highly Conjugated Branches for Dye Sensitized Solar Cell Application★ 雲凝結核計數器的製作與測試
★ 桃園地區硫沈降之觀測與模擬★ 大氣降水中多環芳香烴的定量分析
★ 亞洲沙塵暴之模擬★ 不同空氣源次微米氣溶膠活化能力之探討
★ 桃園地區降水化學特性分析★ 鄰近國家嚴重核事故之大氣長程輸送對台灣的影響評估
★ 東亞大氣汞之長程輸送研究: 雲水中汞之定量分析與指紋之建立★ 桃園地區降水化學與硫化物清除係數探討
★ 亞洲沙塵好發期間雲水化學特性分析★ 光達及太陽輻射儀之應用:2005中壢氣膠光學垂直特性及邊界層高度之變化
★ 2001年東亞硫沉降之模擬★ 亞洲生質燃燒氣膠對區域大氣輻射之衝擊及對氣象場的反饋作用
★ 鹿林山與中壢氣膠光學垂直特性之監測與比較★ 北台灣冬季層狀雲化學特性分析
檔案 [Endnote RIS 格式]    [Bibtex 格式]    [相關文章]   [文章引用]   [完整記錄]   [館藏目錄]   [檢視]  [下載]
  1. 本電子論文使用權限為同意立即開放。
  2. 已達開放權限電子全文僅授權使用者為學術研究之目的,進行個人非營利性質之檢索、閱讀、列印。
  3. 請遵守中華民國著作權法之相關規定,切勿任意重製、散佈、改作、轉貼、播送,以免觸法。

摘要(中) 汞是全球性的污染物,在歐美與的研究較早較廣,而台灣對於其的研究相對欠缺,尤其在大氣汞部分,幾無數據資料。因此本研究主要是針對台灣平地與高山之大氣汞進行監測,以瞭解其在空間及垂直分布之特性。
本研究之採樣點共有五點,分別為桃園縣內近海的新屋鄉、近都市與工業的中壢中央大學、山區的復興鄉、台北大屯山區最高之竹子山與嘉義之鹿林山。桃園縣內以中央大學之總汞濃度為最大,新屋鄉次之,復興鄉為最小,分別為4.37 ± 0.93,3.78 ± 1.44,2.90 ± 0.70 ng m-3。此外,新屋與中央大學的相關係數為0.86,表示兩者有著相同的趨勢;而復興與桃園其他兩站之變化較不具相關性。以季節分類,三個採樣點之總汞濃度皆以冬季較高。
鹿林山總汞濃度之平均值為2.56 ± 1.14 ng m-3,白天比晚上高,而秋季的總汞濃度為最高,冬季為最低。鹿林山之總汞濃度由陸域氣流傳輸為4.31 ± 0.56 ng m-3,而由海洋性氣流傳輸為2.30 ± 0.52 ng m-3,明顯較低。
若以高度排列分別為復興鄉介壽國中(高度約400 m),竹子山(高度約1100 m),鹿林山(高度約2862 m)。其總汞濃度之平均值分別為2.90 ± 0.70,2.42 ± 1.03,2.56 ± 1.14 ng m-3,變化不大,顯示垂直均勻分佈。本研究整體結果顯示台灣之總汞濃度為2.42 – 2.90 ng m-3,較其他地區來的高。
摘要(英) Mercury is a global pollutant. The research of the mercury in America and Europe has been widely conducted, but quite scare in Taiwan, especially for atmospheric mercury. In this study, we attempt to quantify the concentration of atmospheric mercury at the ground and the mountain levels in Taiwan, in order to characterize its spatial and vertical distributions.
Five sampling sites were operated from coast to mountain area. In Tao-yuan, the highest total gaseous mercury (TGM) concentration was measured at the NCU (4.37 ± 0.93 ng m-3), followed by Hsin-Wu (3.78 ± 1.44 ng m-3) and Fu-Hsin (2.90 ± 0.70 ng m-3). Besides, the correlation coefficient between the NCU and Hsin-Wu is 0.86, indicating that both sites have the same tendency. However, Fu-Hsin has not the same tendency as the other sites in Tao-yuan. The highest TGM concentration was observed in winter for three these sites.
In Lu-lin Mt., mean TGM concentration was 2.56 ± 1.14 ng m-3. It’s daytime value was higher than nighttime value, and the highest in fall and the lowest in winter. The mean TGM concentration associated with the airflow from Asian continent was 4.31 ± 0.56 ng m-3. In contrast, it was 2.30 ± 0.52 ng m-3 for the airflow from the ocean.
With respect to the altitude, the TGM concentration was 2.90 ± 0.70, 2.42 ± 1.03 and 2.56 ± 1.14 ng m-3 were at Fu-Hsin(400 m MSL), Bamboo Mt.(1100 m MSL) and Lu-Lin Mt.(2862 m MSL), respectively. We can see a stable distribution, indicating the vertical TGM concentration was well mixed. In our study, the TGM concentration was ranged in 2.42 – 2.90 ng m-3, lower than other areas.
關鍵字(中) ★ 大氣汞
★ 汞
關鍵字(英) ★ Mercury
★ TGM
論文目次 中文摘要…………………………………………………Ⅰ
英文摘要…………………………………………………Ⅱ
致謝辭……………………………………………………Ⅲ
目錄……………………..………………………………Ⅳ
表目錄…………………………………………………………………………Ⅶ
圖目錄…………………………………………………………………………Ⅸ
第一章 緒論…………………………………………………………………...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 汞的基本性質、來源與其危害性…………………………………..….3
2.1.1 汞的基本性質…………………………………………….…..3
2.1.2 汞之大氣化學………………………………………………...4
2.1.3 汞之來源……………………………………………………...4
2.1.4 汞之危害………………………………………………….…..7
2.2 大氣汞沈降與長程傳輸………………………………………….….9
2.3 汞分析相關研究之回顧…………………………………………...10
第三章 實驗步驟與樣品分析………………………………………………..12
3.1 採樣點之介紹……………………………………………………...12
3.1.1 新屋鄉農業改良場……………………………………….……12
3.1.2 中壢中央大學…………………………………………….……12
3.1.3 復興鄉介壽國中…………………………………………….…13
3.1.4 竹子山中繼站………………………………………….………13
3.1.5 鹿林山…………………………………..…………...………13
3.2 實驗用品與儀器設備………………………………………….……14
3.2.1 實驗用品…………………………...………………………..14
3.2.2 儀器設備………………………………………...…………..14
3.3 採樣方法………………………………………………….………...15
3.3.1 相關實驗器具之準備…………………………………….…15
3.3.2 採樣儀器之介紹………………………….…………………18
3.3.3 採樣儀器之測試……………………………...……..………20
3.4 分析方法…………………………………………………….……...21
3.4.1 儀器分析原理……………………………………………….21
3.4.2 檢量線之建立………………………………………….……23
3.4.3 數據處理………………………………….…………………23
第四章 結果與討論…………………………………………………………...25
4.1 各採樣站之分析結果……………………….………………………..25
4.1.1 新屋鄉(農業改良場)…………………………………..…25
4.1.2 中壢(中央大學)……………………………………………26
4.1.3 復興鄉(介壽國中)………………………………………….26
4.1.4 竹子山中繼站…………………………………………….…26
4.1.5 鹿林山…………………………………………………….…29
4.2 各採樣站之互相比較…………………………………………….…..33
4.2.1 桃園地區之比較………………………………………….…33
4.2.2 大氣汞垂直變化…………………………………………….34
4.2.3 全部採樣站之比較………………………………………….35
4.3 中央大學採樣站與其他污染物之比較………………………..…….35
4.4 與其他國家之比較………………………………………………..….36
第五章 結論與展望…………………………………………………………...38
5.1 結論………………………………………………………………….38
5.2 建議與展望………………………………………………………….39
參考文獻………………………………………………………………………41
附錄一…………………………………………………………………………88
參考文獻 林德賢 (1998), 勞工生物檢體汞物種偵測標準方法研究,行政院勞工委員會勞工安全衛生研究所。
Ebinghaus, R., Slemr, F.(2000). Aircraft measurements of atmospheric mercury over southern and eastern Germany. Atmospheric Environment 34, 895-903.
Ebinghaus, R., Jennings, S., Schroeder, W. H., Berg, T., Donaghy, T., Guentzel, J., Kenny, C., Kock, H. H., Kvietkus, K., Landing, W., Muhleck, T., Munthe, J., Prestbo, E. M., Schneeberger, D., Slemr, F., Sommar, J., Urba, A., Wallschlager, D., Xiao, Z. (1999). International Field Intercomparison Measurements of Atmospheric Merucry Species at Mace head, Ireland. Atmospheric Environment 33, 3063-3073.
Feng, X., Tang, S., Shang, L., Yan, H., Sommar, J., Lindqvist, O.(2003). Total gaseous mercury in the atmosphere of Guiyang, PR China. The Science of the Total Environment 304, 61-72.
Friedli, H. R., Radke, L. F., Prescott, R., Li, P., Woo, J-H., Carmichael, G. R. (2004).Merucry in the atmosphere around Japan, Korea, and China as observed during the 2001 ACE-Asia field campaign: Measurements, distributions, sources, and implications. Journal of Geophysical Research 109, D19S25.
Gabriel, M. C., Williamson, D. G., Brooks, S., Lindberg, S.(2005). Atmospheric speciation of mercury in two contrasting Southeastern US airsheds. Atmospheric Environment 39, 4947–4958.
Han, Y. Ji., Holsen, T. M., Lai, S. O., Hopke, P. K., Yi, S. M., Liu, W., Pagano, J., Falanga, L., Milligan, M., Andolina, C. (2004). Atmospheric gaseous mercury concentrations in New York State: relationships with meteorological data and other pollutants. Atmospheric Environment 38, 6431–6446.
Hylander, L. D., Meili, M. (2003). 500 years of mercury production: global annual inventory by region until 2000 and associated emissions The Science of the Total Environment 304, 13-27.
Kellerhals, M., Beauchamp, S., Belzer, W., Blanchard, P., Froude, F., Harvey, B., McDonald, K., Pilote, M., Poissant, L., Puckett, K., Schroeder, B., Steffen, A., Tordonb, R. (2003). Temporal and spatial variability of total gaseous mercury in Canada: results from the Canadian Atmospheric Mercury Measurement Network (CAMNet). Atmospheric Environment 37, 1003–1011.
Kim, K-H., Kim, M-Y. (2002). A decadal shift in total gaseous mercury concentration levels in Seoul,Korea: changes between the late 1980s and the late 1990s. Atmospheric Environment 36, 663–675.
Kim, K-H., Kim M-Y., Kim, J., Lee, G. (2002). the Concentrations and Fluxes of Total Gaseous Mercury in a Western Coastal Area of Korea during late March 2001. Atmospheric Environment 36, 3413-3427.
Lee, D.S., Dollard, G. J., Pepler, S. (1998). Gas-Phase Mercury in the Atmosphere of the United Kingdom. Atmospheric Environment 32(5), 855-864.
Lin, C. J., and Pehkonen, S. O. (1999). The Chemistry of Atmospheric Mercury: a Review. Atmospheric Environment 33, 2067-2079.
Lindberg, S. E., and Stratton, W. J. (1998). Atmospheric Mercury Speciation: Concentration and Behavior of Reactive Gaseous Mercury in Ambient Air. Atmospheric Environment 32, 49-57.
Lindqvist, O., and Rodhe, H. (1985). Atmospheric Merucry-a review. Tellus 27B, 136-159.
Liu, S., Nadim, F., Perkins, C., Carley, R. J., Hoag, G. H., Lin, Y., Chen, L. (2002). Atmospheric Mercury Monitoring Survey in Beijing, China. Chemosphere 48, 97-107.
Mason, R.P., Fitzgerald, W. F., and Morel. M. M. (1994). the Biogeochemical Cycling of Elemental Mercury: Anthropogenic Influences. Geochim. Cosmochim. Acta 58, 3191-3198.
Munthe, J., Angberg, I. W., Pirrone, N., Iverfeldt, Å., Ferrara, R., Ebinghaus, R., Feng, X., Gårdfeldt, K., Lanzillotta, G. K. E., Lindberg, S.E., Lu, J., Mamane, Y., Prestbo, E., Schmolke, S., Schroeder, W. H., Sommarer, J., Sprovieri, F., Stevens, R.K., Stratton, W., Tuncel, G., Urba, A. (2001). Intercomparison of methods for sampling and analysis of atmospheric mercury species. Atmospheric Environment 35, 3007–3017.
Nakagawa, R., and Hiromoto, M. (1997). Geographical Distribution and Background Levels of Total Merucry in Air in Japan and eighbouring Countries. Chemosphere 314, 801-806.
Pacyna, E. G. and Pacyna, J. M. (2002). Blobal emission of mercury from anthropogenic sources in 1995. Water, Air, Soil Pollutant 137, 149-165.
Poissant, L. (2000). Total gaseous mercury in Quebec Canada in 1998. The Science of the Total Environment 259, 191 – 201.
Poissant, L. (1999). Potential sources of atmospheric total gaseous mercury in the St. Lawrence River valley. Atmospheric environment 33, 2537-2547.
Schroeder, W. H., Munthe, J. (1998). Atmospheric Mercury – an Overview, Atmospheric Environment 32, 809-822.
Seigneur, C., Vijayaraghavan, K., Lohman, K., Courtneyscott. (2004). Global Source Attribution for Mercury Deposition in the United States. Environmental Science and Technology 38, 555-569.
Seigneur, C., Lohman, K., Vijayaraghavan, K., Shia, R. (2003). Contributions of global and regional sources to mercury deposition in New York State. Environmental Pollution 123, 365–373.
Slemr, F., Langer, E. (1992). Increase in global atmospheric concentrations of mercury inferred from measurements over the Atlantic Ocean. Nature 355, 434-437.
Slemr, F., Schuster, G., Seiler, W. (1985). Distribution, Speciation and Budget of Atmospheric Mercury. Journal of Atmosperic Chemistry 3, 407-434.
Tomiyasu, T.; Nagano, A., Sakamoto, H., yonehara, N. (2000). Background Levels of Atmospheric Merucry in Kagoshima City, and Influence of Merucry Emission from Sakurajima Volcano, Southern Kyushu, Japan. The Science of the Total Environment 259, 231-237.
U.S. Environmental Protection Agency, Merucry Study Report to Congress, EPA-452/R-97-004; Office of Air Quality and Standards, Office of Research and Development, U.S. Government Printing Office. Washington, DC, 1997.
Vermette, S.; Lindberg, S., Bloom, N. (1995). Field Tests for a Regional Mercury Deposition Network-Sampling Design and Preliminary Test Result. Atmospheric Environment 29, 1247-1251.
指導教授 林能暉(Neng-Huei Lin) 審核日期 2006-7-23
推文 facebook   plurk   twitter   funp   google   live   udn   HD   myshare   reddit   netvibes   friend   youpush   delicious   baidu   
網路書籤 Google bookmarks   del.icio.us   hemidemi   myshare   

若有論文相關問題,請聯絡國立中央大學圖書館推廣服務組 TEL:(03)422-7151轉57407,或E-mail聯絡  - 隱私權政策聲明