請用此 Handle URI 來引用此文件:
http://tdr.lib.ntu.edu.tw/jspui/handle/123456789/31544
完整後設資料紀錄
DC 欄位 | 值 | 語言 |
---|---|---|
dc.contributor.advisor | 曾鈞懋 | |
dc.contributor.author | An-Peng Chen | en |
dc.contributor.author | 陳安芃 | zh_TW |
dc.date.accessioned | 2021-06-13T03:14:32Z | - |
dc.date.available | 2006-08-04 | |
dc.date.copyright | 2006-08-04 | |
dc.date.issued | 2006 | |
dc.date.submitted | 2006-08-01 | |
dc.identifier.citation | (1) 氣象資料:
大台北地區降雨資料,中央氣象局 (2) 網路資料: 中央氣象局網站 http://www.cwb.gov.tw 台灣年鑑 汪中和等 http://www.gov.tw/EBOOKS/TWANNUAL/ (3) 專利資料: Tseng, C.-M., (2003) 汞物種自動超微量測定儀 (AMSA), 台灣專利, 核準字號:新型209591 Tseng, C.-M., (2003) 汞物種自動超微量測定儀 (AMSA), 大陸專利, 核準字號:ZL 03237156.X (4) 中文文獻: 楊明德 (1999) 台灣台北地區大氣Pb-210沉降通量 環保署 (2001) 空氣污染防治報告 黃譯樘 (2002) 台北都會區大氣懸浮微粒的化學特性硏究 李佳樺 (2004) 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。 (5) 英文文獻 Arimoto, R., Duce, R.A., Ray, B.J., 1989. Concentrations, Source and air-sea exchange of trace elements in the atmospheric over the Pacific Ocean. Chemical Oceanography 10, 107-149 Burke, J., Hoyer, M., Keeler, G.J., Scherbatskoy, T., 1995. Wet deposition of mercury and ambient mercury concentrations at a site in the Lake Champlain basin. Water, Air and Soil Pollution 80, 169-178 Chester, R., Berry, A. S., Murphy, J. T., 1990. The Distributions of particulate atmospheric trace metals and mineral aerosols over the Indian Ocean. Marine Chemistry 34, 261-290 Dastoor, A.P., Larocque, Y., 2004. Global circulation of atmospheric mercury: A modeling study. Atmospheric Environment 38, 147-161 Dvonch, J.T., Vette, A.F., Keeler, G.J., Evans, G., Stevens, R., 1995. An intensive multi-site pilot study investigating atmospheric mercury in Broward County, Florida. Water, Air and Soil Pollution 80, 169-178 Fang, F., Wang, Q., Li, J., 2004. Urban Environmental Mercury in Changchun, a Metropolitan City in Northeastern China: Source, Cycle, and Fate. The Science of Total Environment 330, 159–170 Fitzgerald, W.F, Gill, G.A., 1979. Subnanogram determination of mercury by two-stage gold amalgamation applied to atmospheric analysis. Analyze Chemistry 51, 1714-1720. Fitzgerald, W.F., Vandal, G.M., Mason, R.P., 1991. Atmospheric cycling and air-water exchange of Hg over mid-continental lacustrine regions. Water, Air and Soil Pollution 56, 745-767. Fitzgerald, W.F., Engstrom, D.R., Mason, R.P., Nater, E.A., 1998. The case for atmospheric mercury contamination in remote areas. Environment Science and Technology 32, 1-7. Fogg, T.R., Fizgerald, W.F., 1979. Mercury in southern New England rains. Journal of Geophysics Research 84, 6987-6988. Gill, G.A., Guentzel, J.L., Landing, W.M., Pollman, C.D., 1995. Total gaseous mercury measurements in Florida: The FAMS project (1992-1994). Water, Air and Soil Pollution 80, 235-244. Guentzel, J.L., Landing, W.M., Gill, G.A., Pollman.C.D., 1995. Atmospheric deposition of mercury in Florida: The FAMS Project (1992-1994). Water, Air and Soil Pollution 80, 393-402. Hoyer, M., Burke,J., Keeler, G.J., 1995. Atmospheric sources, transport and deposition of mercury in Michigan: Two years of event precipitation. Water, Air and Soil Pollution 80, 199-208. Iverfeldt, A., 1991. Mercury in Swedish forest soils and waters - assessment of critical load. Water, Air and Soil Pollution 56, 267-281 Iverfeldt, A., 1991. Mercury in forest canopy throughfall water and its relation to atmospheric deposition. Water, Air and Soil Pollution 56, 553–564. Keeler, G.J., Glinsorn, G., Pirrone, N., 1995. Particulate mercury in the atmosphere: Its significance, transport, transformation and sources. Water, Air and Soil Pollution 80, 159-168 Lamborg, C.H., Fitzgerald, W.F., Vandal G.M., Rolfhus, K.R., 1995. Atmospheric mercury in northern Wisconsin: speciation and sources. Water, Air and Soil Pollution 80, 189-198 Lamborg, C.H., Fitzgerald, W.F., O'Donnell, J., Torgersen, T., 2002. A non-steady state compartmental model of global-scale mercury biogeochemistry with interhemispheric atmospheric gradients. Geochimica et Cosmochimica Acta 66, 1-14 Laurier, F.J.G., Mason, R.P., Gill, G.A., Whalin, L., 2004. Mercury distributions in the North Pacific Ocean—20 years of observations. Marine Chemistry 90, 3-19 Lawson, N.M., Mason, R.P., Laporte, J.M., 2001. The fate and transport of mercury, methylmercury, and other trace metals in chesapeake bay tributaries. Water Research 35, 501-515 Lin, N.H., Peng, C.M., 1999. Estimate of contribution of below-cloud scavenging to the pollutant loading of rain in Taipei, Taiwan. TAO 10, 693-704 Lindqvist, O., 1991. Mercury in the Swedish Environment. Water, Air and Soil Pollution 55, 23–33 Liu, S., Farhad N., Perkins, C., Carley, R.J., Hoag, G.E., Lin, Y., Chen, L., 2002. Atmospheric mercury monitoring survey in Beijing, China. Chemosphere 48, 97-107 Lodenius, M., 1998. Dry and wet deposition of mercury near a chlor-alkali plant. The Science of Total Environment 213, 53-56 Mason, R.P., Fitzgerald W.F., Vandal G.M., 1992. The sources and composition of mercury in Pacific Ocean rain. Journal of Atmospheric Chemistry 14, 489-500 Mason, R.P., Fitzgerald W.F., Morel, F.M.M., 1994. Aquatic biogeochemical cycling of elemental mercury: anthropogenic influence. Geochimica et Cosmochimica Acta 58, 3191-3198 Munthe, J., Hultberg, H., Iverfeldt, A., 1995. Mechanisms of deposition of methylmercury and mercury to coniferous forests. Water, Air and Soil Pollution 80, 363-371 Pacyna, E.G., Pacyna, J.M., 2002. Global Emissions of Mercury from Anthropogenic Sources in 1995. Water, Air and Soil Pollution 137, 149-165 Pacyna, J.M., Pacyna, E.G., Steenhuisenb, F., Wilson, S., 2003. Mapping 1995 global anthropogenic emission of Mercury. Atmospheric Environment 37, 109-117 Rea, A.W., Keeler, G.J., Scherbatskoy, T., 1996. The deposition of mercury in throughfall and litterfall in. the Lake Champlain watershed: a short-term study. Atmospheric Environment 30, 3257-3263 Pirrone, N., Keeler, G.J., Nriagu, J., 1996. Regional differences in worldwide emissions of mercury to the atmosphere. Atmospheric Environment 30, 2981-2987 Poissant, L., Pilote, M., 1998. Mercury concentrations in single event precipitation in southern Québec. The Science of the Total Environment 213, 65-72 Sakata, M., Marumoto, K., 2005. Wet and dry deposition fluxes of mercury in Japan. Atmospheric Environment 39, 3139-3146 Schroeder, W.H., Munthe, J., 1998. Atmospheric mercury: An overview. Atmospheric Environment 32, 809-822 Tan, H., He, J.L., Liang, L., Lazoff, S., Sommer, J., Xiao, Z.F., Lindqvist, O., 2000. Atmospheric mercury deposition in Guizhou, China. The Science of the Total Environment 259, 223-230 Wang, Q., Shen, W., Ma, Z., 2000. Estimation of Mercury Emission from Coal Combustion in China. Environment Science and Technology 34, 2711-2713 Wang, Z., Zhang, X., Chen, Z., Zhang, Y., 2006. Mercury concentrations in size-fractionated airborne particles at urban and suburban sites in Beijing, China. Atmospheric Environment 40, 2194-2201 Xiu, G.L., Jin, Q., Zhang, D., Shi, S., Huang, X., Zhang, W., 2005. Characterization of size-fractionated particulate mercury in Shanghai ambient air. Atmospheric Environment 39, 419-427 | |
dc.identifier.uri | http://tdr.lib.ntu.edu.tw/jspui/handle/123456789/31544 | - |
dc.description.abstract | 本研究主要探討在2004/10~2005/12期間大台北地區大氣汞濕沉降通量的時序變化。以超純淨鍍鐵弗龍的自動集雨器採集雨水,共採集65個降雨事件,包括颱風、沙塵暴和梅雨。使用冷蒸汽原子螢光法測定雨水中汞金屬總量,部分樣品則測定溶解態、顆粒態以及活性態的汞。總汞濃度範圍1~65 ng/L,權重平均濃度為7±11 ng/L (n = 65),溶解態、顆粒態以及活性態分別為4±8 ng/L (n = 23)、 3±2 ng/L (n = 30)、0.4±1.4 ng/L (n = 9),雨水中以溶解態所佔比例最高,達63%。不論一般或是特殊氣象事件之降雨,濃度跟降雨量皆呈現負相關,表示有明顯的清除現象。從總汞濃度與沉降通量的時序變化中,發現有明顯的季節性變化,總汞濃度有冬高 (12±18 ng/L,n =18 )、夏低 (4±2 ng/L,n =22)的趨勢,冬季高值主要原因為東北季風所帶之中國陸源性及污染性物質,夏季濃度較低則因降雨量增加而稀釋減少。沉降通量高值則集中在夏、秋之際,因來自海源的颱風事件在短時內挾帶大量降雨所造成。總汞之濕沉降通量約21.7μg/m2/yr,高於東亞地區其他國家如日本,因本地降雨量較高所致。沙塵暴、梅雨以及颱風等特殊事件所帶來的雨水總汞分別為65 ng/L (n = 1)、2±3 ng/L (n = 20)、8±3 ng/L (n = 6),以沙塵暴為最高;但其沉降通量所佔總通量比例,颱風便高達40%,梅雨次之為10%,沙塵暴僅佔0.1%。 | zh_TW |
dc.description.abstract | Abstract
Temporal variation of wet deposition flux of mercury (Hg) in metropolitan Taipei, Taiwan was investigated from October 2004 to December 2005. A total of 65 individual events, including typhoon, Asian dust and plum rain events, was collected by automatic Teflon-coated rain collector. Total Hg concentration was measured by Cold Vapor Atomic Fluorescence Spectrophotometry (CVAFS) for all rain samples and dissolve-, particle- and operation-defined reactive-phases Hg were measured in some selected events as well. Total Hg concentration ranged from 1~65 ng/L with a volume-weighted mean of 7±11 ng/L (n = 65). Dissolve-phase Hg averaged 4±8 ng/L (n = 23) about 63% of total Hg while particle-phase and reactive Hg were 3±2 ng/L (n = 30) and 0.4±1.4 ng/L (n = 9), respectively. A negative relationship between total Hg concentration and precipitation amount was observed in all precipitation events, signifying the scavenging of atmospheric particulates and colloids bearing Hg. A significant seasonal variation in total Hg showed the highest concentration in the winter (12±18 ng/L,n =18 ) as result of terrestrial and anthropogenic matters from mainland China during northeast monsoon and lowest in summer (4±2 ng/L,n =22) due to a dilution effect caused by a huge of precipitation. There was additionally a maximum of wet Hg deposition flux the in summer and fall mainly associated with typhoon-induced rainfalls of marine materials. The annual total Hg deposition flux was about 21.7μg/m2 positively correlation with the precipitation amount which was much higher in Japan. The highest concentration was observed in Asian dust event about 65 ng/L (n = 1) relative to those in plum rain (2±3 ng/L, n = 20) and typhoon events (8±3 ng/L , n = 6). Further, typhoon events accounted for 40% of total Hg deposition flux, plum rain for 10% and Asian dust only for 0.1%. | en |
dc.description.provenance | Made available in DSpace on 2021-06-13T03:14:32Z (GMT). No. of bitstreams: 1 ntu-95-R92241405-1.pdf: 1369662 bytes, checksum: 7c8f8657569359c49704080ed834ac93 (MD5) Previous issue date: 2006 | en |
dc.description.tableofcontents | 第一章 序論 1
1-1 汞的來源與循環 1 1-2 大氣汞的排放 2 1-3 汞之沉降特性 3 1-4 全球大氣汞濕沉降相關研究 3 1-5 台灣之降雨特性 6 1-6 研究動機與目的 7 第二章 採樣及分析方法 8 2-1 採樣方法 8 2-2 前處理 9 2-3 雨水樣品分析 10 2-3-1 藥品與試劑 10 2-3-2 樣品分析 11 2-4 氣象資料 13 第三章 資料品保/品管 (QA/QC) 14 3-1 降雨量之驗證 14 3-2 集雨器之比較 17 3-3 總汞和顆粒態以及溶解態的總和之比較 19 第四章 結果與討論 20 4-1 雨水中汞之濃度分佈 20 4-1-1 總汞 20 4-1-2 溶解、顆粒以及活性態汞 21 4-1-3 各相態汞與總汞之關係 23 4-2 汞沉降通量之時序變化 24 4-2-1 總汞沉降通量之單一降雨事件變化 25 4-2-2 總汞沉降通量之週變化 27 4-2-3 總汞沉降通量之月變化 30 4-2-4 總汞沉降通量之季變化 31 4-2-5 總汞沉降通量之年變化與東亞地區之比較 33 4-3 汞金屬的來源 34 4-3-1 主要來源因子 34 4-3-2 結論 38 第五章 特殊氣象事件 39 5-1 颱風事件 39 5-2 東亞沙塵暴 45 5-2-1 東亞沙塵暴期間之雨水樣品與前後之比較 45 5-3 梅雨 47 5-3-1 梅雨期間之雨水樣品數值比較 47 5-3-2 梅雨期間之特殊性 49 5-4 特殊氣象事件之總結 50 第六章 結論 53 資料來源與參考文獻 55 圖目錄 圖3.1.11 國家海洋科學中心與中央氣象局公館測站相對雨量圖 14 圖3.1.21 歷年平均值與2005年之月平均降雨量月份分佈圖…………………16 圖3.2.11 人工集雨器與自動集雨器之總汞濃度比較圖 17 圖3.2.21 人工集雨器與自動集雨器之活性汞濃度比較圖 18 圖3.3.11 顆粒態及溶解態總和與總汞濃度比較圖 19 圖4.1.11 總汞與每單一事件雨量關係相對圖 20 圖4.1.21 溶解態總汞與雨量關係相對圖 21 圖4.1.31 雨量與顆粒態總汞關係相對圖 22 圖4.1.41 各相態汞比例分佈圖 24 圖4.2.11 單一降雨事件之總汞濃度時序變化圖 25 圖4.2.21 單一降雨事件之總汞沉降通量與降雨量時序變化圖 26 圖4.2.31 單一降雨事件之總汞沉降通量與降雨量關係圖 27 圖4.2.41 每週總汞濃度時序變化圖 28 圖4.2.51 每週總汞沉降通量及降雨量時序變化圖 29 圖4.2.61 每週總汞沉降通量與降雨量之關係圖 29 圖4.2.71 每月總汞沉降通量及降雨量時序變化圖 30 圖4.2.81 各月份總汞沉降通量與降雨量關係圖 31 圖4.2.91 總汞濃度與沉降通量季節時序變化圖 32 圖4.2.10 沉降通量與總汞濃度季節時序變化圖 (排除特殊氣象事件) 32 圖4.2.11 東亞地區總汞年沉降通量與降雨量關係圖 33 圖4.3.11 總汞濃度與海源因子季變化關係圖 35 圖4.3.21 總汞濃度與陸源因子季變化關係圖 36 圖4.3.31 總汞濃度與人為因子季變化關係圖 37 圖5.1.11 納坦颱風之總汞濃度、沉降通量及降雨量時序變化圖 39 圖5.1.21 南瑪都颱風之總汞濃度、沉降通量及降雨量時序變化圖 40 圖5.1.31 海棠颱風之總汞濃度、沉降通量及降雨量時序變化圖 40 圖5.1.41 馬莎颱風之總汞濃度、沉降通量及降雨量時序變化圖 41 圖5.1.51 泰利颱風之總汞濃度、沉降通量及降雨量時序變化圖 41 圖5.1.61 龍王颱風之總汞濃度、沉降通量及降雨量時序變化圖 42 圖5.1.71 颱風事件總汞濃度與降雨量關係圖 44 圖5.1.81 颱風事件總汞沉降通量與降雨量關係圖 44 圖5.2.11 2005年4月份總汞濃度與降雨量相關圖 46 圖5.2.21 2005年4月份總汞沉降通量與降雨量相關圖 47 圖5.3.11 梅雨季節總汞濃度時序變化圖 48 圖5.3.21 梅雨季節總汞沉降通量與降雨量時序變化圖 48 圖5.3.31 梅雨季節總汞濃度與降雨量關係圖 49 圖5.3.41 梅雨季節總汞沉降通量與降雨量關係圖 50 圖5.4.11 各降雨事件沉降通量比例圖 51 圖5.4.21 特殊氣象事件沉降通量與降雨量關係圖 52 表目錄 表1.1.1 各地區大氣汞濕沉降濃度分佈表 4 表1.2.1 各地區大氣汞濕沉降通量分佈表 5 表1.3.1 大臺北地區平均降雨量以及降雨天數 6 表4.1.1 顆粒態汞之所佔比例與北美地區比較表 23 表5.1.1 颱風事件總汞濃度及沉降通量 43 表5.2.1 2005年4月份降雨事件一覽表 45 表5.4.1 特殊氣象事件一覽表 51 | |
dc.language.iso | zh-TW | |
dc.title | 大台北地區大氣汞濕沉降之時序變化 | zh_TW |
dc.title | Temporal Variation of Wet Deposition of Atmospheric Mercury in Metropolitan Taipei | en |
dc.type | Thesis | |
dc.date.schoolyear | 94-2 | |
dc.description.degree | 碩士 | |
dc.contributor.oralexamcommittee | 魏慶琳,陳宏瑜,許世傑 | |
dc.subject.keyword | 汞,降雨,大氣汞,沉降通量,颱風,梅雨,沙塵暴, | zh_TW |
dc.subject.keyword | mercury,wet deposition flux,typhoon,plum rain,Asian Dust, | en |
dc.relation.page | 59 | |
dc.rights.note | 有償授權 | |
dc.date.accepted | 2006-08-02 | |
dc.contributor.author-college | 理學院 | zh_TW |
dc.contributor.author-dept | 海洋研究所 | zh_TW |
顯示於系所單位: | 海洋研究所 |
文件中的檔案:
檔案 | 大小 | 格式 | |
---|---|---|---|
ntu-95-1.pdf 目前未授權公開取用 | 1.34 MB | Adobe PDF |
系統中的文件,除了特別指名其著作權條款之外,均受到著作權保護,並且保留所有的權利。