Please use this identifier to cite or link to this item: http://hdl.handle.net/11455/91662
DC FieldValueLanguage
dc.contributor張書奇zh_TW
dc.contributorShu-chi Changen_US
dc.contributor.authorYu-Hsiang Kuoen_US
dc.contributor.author郭昱祥zh_TW
dc.contributor.other環境工程學系所zh_TW
dc.date2015zh_TW
dc.date.accessioned2015-12-11T07:00:08Z-
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dc.identifier.urihttp://hdl.handle.net/11455/91662-
dc.description.abstract台灣因氣候及地形條件,導致民生用水相當依賴湖泊水庫。根據環保署102年環境監測年報,台灣離島28座水庫優養比例高達96%。金門縣為台灣第二大離島,島上共有11座水庫,均處於優養化狀態,且水體中存在釋放藻毒之藍綠菌(cyanobacteria),對於當地的湖庫生態與居民飲用水安全造成威脅。微囊藻毒素有強烈的肝毒性,容易誘發肝炎以及肝癌,對皮膚與黏膜有強烈刺激性,所造成的危害在世界各地層出不窮,當中不乏人類死亡的案例。 本研究以優養化湖泊金門太湖為對象,自2013年11月至2014年8月進行4次的採樣,於湖面上佈下11個採樣點,進行全湖域的水質、懸浮固體物與底泥的調查。結果顯示金門太湖地區之主要營養鹽來源為山外溪,其次為幹訓班水之排水溝,此外位於太湖湖面的光復亭小島因有大型鳥類群聚,所排泄的鳥糞亦可能為營養鹽來源。金門全年葉綠素a濃度介於8.9-118.5 µg/L,遠高於Carlson優養化單一指標7.2 µg/L之標準,藻毒濃度在四季的採樣中,2月之藻毒濃度最高,Microcystin-LR濃度為0.38 µg/L、Microcystin-RR濃度為0.13 µg/L,低於歐盟1.0 µg/L之標準,但藻毒問題仍為太湖水庫之隱憂。營養鹽部分,總磷濃度最高之月份為2月,平均濃度高159.1 µg/L,推測可能原因為太湖水位下降,使得總磷在湖水產生濃縮作用與11月至2月間湖水翻騰現象所造成。而氨氮濃度最高月份為8月,濃度平均達198.7 µg/L。營養鹽循環中,除了外部的營養鹽來源之外,底泥釋放也是營養鹽的來源之一,根據調查結果,太湖湖域沉積最嚴重之區域為小太湖,而沉積物中磷之濃度最高之區域為太湖南邊,就整體磷通量而言,小太湖區域為最高。以SEDEX分析金門太湖底泥之磷鍵結態,其中被視為較易釋放磷於水體的Ex-P與Fe-P佔總磷之比例高於50%,顯示底泥可能為太湖重要營養鹽來源之一。zh_TW
dc.description.abstractDue to climatic and topographic conditions, domestic water source in Taiwan is highly dependent on reservoirs. In recent decades, due to economic development, there are more and more human activities in catchment area. They caused eutrophication of reservoir by discharging plenty of nutrients into water body. This phenomenon is worsened at Taiwan’s isolated islands. According to Taiwan EPA, the percentage of eutrophic lake in Kinmen county is up to 96% in 2013. Thus, the water quality on this isolated island becomes a highly imperative problem. In Kinmen, Tai-Hu Reservoir (THR) is one of the major drinking water sources. THR has been seriously affected by eutrophication because it is teemed with cyanobacteria. Here we focused on the water quality monitoring results of 11 stations in THR in terms of Chlorophyll a (Chl-a), total phosphorus, ammonia nitrogen, nitrite, nitrate, microcystin-LR (MC-LR), microcystin-RR (MC-RR), phosphorus in sediment core samples, and sediment deposition rates. This research is focused on THR and finished a full-year monitoring from November in 2013 to August in 2014. Eleven sampling station was installed in the lake for whole lake monitoring in terms of water quality, suspended solids and sediments. The results indicated that the main source of nutrients is Shan-Wie Creek, and the drainage of Corporal Training Camp is the second major source. In addition, the feces of migrating birds on the Kuan-Fuh Island in the lake might be a source of phosphorus, too. The whole-year concentration of Chl-a is between 8.9 and 118.5 µg/L, which is much higher than the single-parameter eutrophic state index based on Chl-a only, i.e., 7.2 µg/L. Algal toxin level is at its highest in February with microcystin-LR concentration at 0.38 µg/L and microcystin-RR concentration at 0.13 µg/L. Microcystin-LR concentration is below EU standard at 1.0 µg/L. However, algal toxin is still an impending problem. For the nutrients, total phosphorus is highest in February with an average concentration at 159.1 µg/L probably because the reversing of water stratification and concentrating effects brought about by lowered water level or decreased water volume in winter season. The highest ammonium-nitrogen concentration falls in August at as high as 198.7 µg/L. In the nutrient cycle, apart from the external source for phosphorus, the lake sediment may also be a significant source. According to the results, the Small Tai-Hu Lake (at the west side of THR) is the area that has the highest deposition of sediments but the highest phosphorus concentration is at the south side of THR. For the flux of phosphorus, the Small Tai-Hu Lake is still at the top. According to the results by a sequential extraction method (SEDEX) exhibits that bioavailable phosphorus portion is higher than 50% indicated that the lake sediment could be a major source of phosphorus in THR.en_US
dc.description.tableofcontents摘要 I Abstract I 圖目錄 VII 表目錄 X 第一章 前言 1 1-1 研究源起 1 1-2研究目的 3 第二章 文獻回顧 4 2-1 優養化 4 2-1-1 優養化成因 4 2-1-2 優養化之影響 6 2-1-3 水體優養化評估方法 8 2-1-4 優養化整治技術 12 2-2 營養鹽 15 2-2-1 營養鹽來源 15 2-2-3 底泥中不同的磷型態 18 2-2-4 連續萃取法 21 2-3 台灣水資源與優養化情形 21 2-3-1台灣水資源概況 21 2-3-2 台灣水庫湖泊優養化情形 23 2-3-3 研究場址介紹 28 2-3-3-1 金門地區水資源概況 28 2-3-3-2 金門地區水文與氣候 30 2-3-3-3 金門地區水庫優養化情形 33 2-4 藍綠菌及其毒素 34 2-4-1 藍綠菌 34 2-4-2 微囊藻與微囊藻毒 41 第三章 研究方法 46 3-1 實驗設備 46 3-2 實驗藥品 47 3-3 實驗架構 48 3-4 採樣計畫與方法 49 3-4-1 採樣空間與時間分布 49 3-4-2 採樣方法 51 3-4-3 底泥採樣 51 3-4-4 沉積物採樣 52 3-5 水質檢驗 53 3-5-1 葉綠素a 53 3-5-2亞硝酸鹽氮 55 3-5-3硝酸鹽氮 56 3-5-4氨氮 57 3-6 磷分析 58 3-6-1 水中總磷檢測 58 3-7 感應耦合電漿發射光譜儀(ICP/OES) 59 3-7-1 底泥消化方法 59 3-7-2 水樣消化方法 60 3-8 底泥磷鍵結態分析方法 60 3-8-1 連續萃取法- SEDEX 60 3-10 太湖水庫磷通量分析 63 3-11 微囊藻毒分析方法 64 3-11-1 固相萃取技術 64 3-11-2 液相層析串聯質譜儀 65 第四章 結果與討論 67 4-1 金門太湖監測背景說明 67 4-2 太湖周邊監測點之水質分析 80 4-2-1 監測點葉綠素a 80 4-2-2 監測點營養鹽 81 4-3 湖中監測點之水質分析 83 4-3-1 葉綠素a 83 4-3-2 氨氮 88 4-3-3 亞硝酸鹽氮與硝酸鹽氮 91 4-3-4 總磷 93 4-3-5 藻毒 95 4-4 底泥磷鍵結態分析 98 4-5 太湖磷通量分析 104 4-5-1 沉積速率 108 4-5-2 沉積物磷濃度分析 112 4-5-3 磷通量分析 114 第五章 結論與建議 117 5-1結論 117 5-2 建議 119 參考資料 120 附錄 129zh_TW
dc.language.isozh_TWzh_TW
dc.rights同意授權瀏覽/列印電子全文服務,2016-07-31起公開。zh_TW
dc.subject優養化zh_TW
dc.subject金門太湖zh_TW
dc.subject監測zh_TW
dc.subject藻毒zh_TW
dc.subjecteutrophicationen_US
dc.subjectTai-Hu resevoiren_US
dc.subjectmonitoringen_US
dc.subjectalgal toxinen_US
dc.title優養化湖泊環境監測-以金門太湖為例zh_TW
dc.titleEnvironmental monitoring for eutrophic Lake Tai-Hu in Kinmen County in Taiwanen_US
dc.typeThesis and Dissertationen_US
dc.date.paperformatopenaccess2016-07-31zh_TW
dc.date.openaccess2016-07-31-
item.openairetypeThesis and Dissertation-
item.openairecristypehttp://purl.org/coar/resource_type/c_18cf-
item.languageiso639-1zh_TW-
item.grantfulltextrestricted-
item.fulltextwith fulltext-
item.cerifentitytypePublications-
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