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請用此 Handle URI 來引用此文件: http://tdr.lib.ntu.edu.tw/jspui/handle/123456789/70522
完整後設資料紀錄
DC 欄位值語言
dc.contributor.advisor韓玉山(Yu-San Han)
dc.contributor.authorChih-Chao Yangen
dc.contributor.author楊智超zh_TW
dc.date.accessioned2021-06-17T04:30:08Z-
dc.date.available2021-08-18
dc.date.copyright2018-08-18
dc.date.issued2018
dc.date.submitted2018-08-13
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Shinoda, A., Aoyama, J., Miller, M. J., Otake, T., Mochioka, N., Watanabe, S., Minegishi, Y., Kuroki, M., Yoshinaga, T., Yokouchi, K., Fukuda, N., Sudo, R., Hagihara, S., Zenimoto, K., Suzuki, Y., Oya, M., Inagaki, T., Kimura, S., Fukui, A., Lee, T. W., & Tsukamoto, K. 2011. Evaluation of the larval distribution and migration of the Japanese eel in the western North Pacific. Reviews in Fish Biology and Fisheries, 21(3): 591-611.
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Tzeng, W.-N., Shiao, J.-C., Iizuka, Y. 2002. Use of otolith Sr: Ca ratios to study the riverine migratory behaviors of Japanese eel Anguilla japonica. Marine Ecology Progress Series, (245): 213-221.
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dc.identifier.urihttp://tdr.lib.ntu.edu.tw/jspui/handle/123456789/70522-
dc.description.abstract日本鰻屬典型的降海產卵洄游魚種,分布於西太平洋地區,在東亞地區為高經濟價值魚種。但因完全養殖成本過高,目前養殖場的鰻苗來源仍完全仰賴天然資源。然而,隨著養殖產業的蓬勃發展,日本鰻的資源量自1970年代也開始急遽下降,直至目前,資源量已經不及1970年代的10%。棲地破壞、過漁、以及全球氣候變遷皆是潛在原因。為了評估鰻魚河川棲地品質,本實驗室於2013年使用了一種全新的評估指標-棲地品質指數 (HQI),以衛星遙測技術評估日本鰻棲地的破壞程度,與過去的棲地調查方法相比,不但省下時間與成本,而且可頻繁的監控,配合水質汙染指標即可隨時做出適當的應變機制。在本篇研究中,我們利用國立中央大學太空及遙測研究中心提供的衛星影像,以及行政院環境保護署的河川汙染資料,評估2014 – 2017年全台灣共38條河川的最新棲地品質指數,每條河川在每個季節都有至少一筆的評估數據。評估結果顯示,台灣北部河川的棲地品質指數,在四個季節的變化上分別為:13.23、14.2、13.46、13.05,東部河川在四個季節的變化為:6、6.24、5.86、5.63,西南部河川在四個季節的變化為:22.87、28.08、27.03、21.63,北部與東部河川的棲地品質在四季變化間較為穩定,而西南部河川有較明顯的季節性變化,特別是在冬季與春季會有棲地品質下降的現象發生。本研究最後計算出2014 – 2017年全台灣共38條研究河川的棲地品質指數,總和為:44.97,扣除本次評估新增的12條中小規模河川所得的總和為:41.46,與本實驗室2016年的研究中所評估的2010年代全台灣共26條河川結果:38.14相比,有些微增加的趨勢,可能的原因為河川汙染程度降低,以及使用了更高解析度的衛星影像。本研究利用衛星遙測技術以及河川汙染資料,對全台共38條河川的日本鰻棲地進行棲地品質的評估,最後發現河川棲地品質會有季節性變化發生,因此各縣市政府在制訂日本鰻相關保護措施時,應該要優先選擇棲地品質指數較高且較穩定的河川以利於日本鰻的生存與保育,而本研究的評估結果可供各縣市政府做為參考依據。zh_TW
dc.description.abstractThe Japanese eel Anguilla japonica is a typical catadromous fish species that spawns in the sea and is distributed across the Western Pacific. Japanese eels are fish species of high economic value in East Asia. However, due to the high costs of complete aquaculture, currently the source of eel fry in farms still depends entirely on natural resources. Nevertheless, with the rapid development of aquaculture industry, the stock of Japanese eel has also sharply declined since 1970s, and to this day it is less than 10% of that observed in 1970. Habitat destruction, overfishing, and global climate change are all potential causes. In order to evaluate the habitat quality of the Japanese eel, our lab (2013) employed a new assessment indicator-Habitat Quality Index (HQI) that uses satellite remote sensing technology to assess the level of destruction of the Japanese eel habitats. Compared to past habitat survey methods, this method not only saves time and costs, but it also allows frequent monitoring and acts in concert with water quality indicators to implement appropriate response mechanism at any time. In this study, we use the satellite images provided by the Center for Space and Remote Sensing Research of the National Central University, as well as the information on river pollution from the Environmental Protection Administration, Executive Yuan of Taiwan, to evaluate the newest data of the HQI of a total of 38 rivers in Taiwan from 2014-2017. Every river has at least one assessment data for each season. The results showed that the HQI of rivers in the northern part of Taiwan across the four seasons were 13.23, 14.2, 13.46, 13.05; in the eastern part were 6, 6.24, 5.86, 5.63; and in southwestern rivers were 22.87, 28.08, 27.03, 21.63. The habitat quality of northern and eastern rivers is relatively stable across the four seasons, while there is noticeable seasonal variability in southwestern rivers in which the habitat quality declines especially during the winter and spring. Finally, this study calculated the HQIs of a total of 38 studied rivers in Taiwan from 2014-2017, and the sum was 44.97. After deducting the HQI of 12 small and medium sized rivers newly added to the assessment, the value obtained was 41.46. There is a trend of slight increase compared to our lab research (2016) of 38.14 obtained by evaluating a total of 26 rivers in Taiwan in the 2010s. Possible reasons for this trend may be a decrease of the levels of river pollution, and the use of higher-resolution satellite imagery. This study uses satellite imagery and river pollution data to assess the habitat quality of Japanese eel in a total of 38 rivers in Taiwan. The results said that the difference of HQI of rivers depended on the seasons in Taiwan. Therefore, in order to facilitate the conservation of Japanese eel, the governments should choose the rivers that have higher and more stable HQI as the priority selection of rivers to formulate the protective standard.The final assessment results can serve as a reference by county and city governments for developing Japanese eel protection measures.en
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dc.description.tableofcontents目錄
致謝 ……….………………………………………………………………….. i
中文摘要 ……………………………………………………………….…...... ii
Abstract ……………………………………………………………….…….. iv
一、前言 ……………………………………………………..……………… 1
1.日本鰻生活史 ………………………………………….……………… 1
2.資源量下降與可能原因 ……………………………….……………… 1
3.台灣河川類型與日本鰻分佈情形 …………………….……………… 2
4.棲地環境與影響 ……………………………………….……………… 2
5.棲地調查方法 ………………………………………………….……… 3
6.本實驗室過去研究 ……………………………………………….…… 4
7.研究目的 …………………………………………………………….… 4
二、材料與方法 …………………………………………..………………… 5
1.研究河川 ……………………………………………. ……...………… 5
2.棲地品質指數 …………………………………………………….…… 5
2.1.衛星影像的取得與處理 …………………………………..……… 6
2.2.汙染指數的取得與加權處理 ………………………………..…… 6
2.3.衛星影像判釋 ………………………………………………..…… 7
2.4.計算流程 ……………………………………………………..…… 7
3.鰻魚資源量的取得 ……………………………………………….…… 7
4.估算研究河川中目前的鰻魚資源量 ……………………...…………… 8
三、結果 ……………………………………………………………………… 9
1.全台灣共38條河川的評估結果 …………………….………………… 9
2.整體季節性變化 ………………………………………….…………… 17
3.日本鰻資源量的估算 ………………………………….……………… 17
四、討論 …………………………………………………………………..… 19
1.棲地品質指數的長期變遷 ……………………………………….…… 19
2.棲地品質指數上升原因 ……………………………………….……… 19
2.1.河川棲地面積增加原因 ……………………………………..…… 19
2.2.河川汙染程度下降可能原因 ……………………………….….… 20
3.河川棲地水深無法列入評估 …………………………………….…… 20
4.水泥橫向構造物對日本鰻及其他生物造成的影響 …………….…… 20
5.以各河川全年最低的HQI作為評估標準 …………………………… 21
6.河川棲地生態調查與HQI評估法的比較 …………………………… 22
7.日本鰻資源量的估算 ……………………………………………….… 23
8.日本鰻上溯終點的判定 ………………………………………………. 23
五、結論 ……………………………………………………………..……… 24
六、引用文獻 ……………………………………………………………..… 25
圖 …………………………………………………………………………..… 30
表 …………………………………………………………………………….. 85
圖
圖一、全台研究河川共三十八條 ………………………………………..… 30
圖二、波段調整示意圖 …………………………………………………..… 31
圖三、鳳山溪2016年春季 ………………………………………………… 31
圖四、淡水河的棲地圈繪範圍依季節呈現 ……………………………….. 32
圖五、老街溪的棲地圈繪範圍依季節呈現 ……………………………….. 34
圖六、社子溪的棲地圈繪範圍依季節呈現 ……………………………….. 36
圖七、鳳山溪、頭前溪、客雅溪的棲地圈繪範圍依季節呈現 ………….. 38
圖八、中港溪的棲地圈繪範圍依季節呈現 ……………………………….. 40
圖九、後龍溪的棲地圈繪範圍依季節呈現 ……………………………….. 42
圖十、大安溪、大甲溪的棲地圈繪範圍依季節呈現 …………………….. 44
圖十一、烏溪的棲地圈繪範圍依季節呈現 ……………………………….. 46
圖十二、濁水溪、北港溪、朴子溪的棲地圈繪範圍依季節呈現 ……….. 48
圖十三、八掌溪、急水溪的棲地圈繪範圍依季節呈現 ………………….. 50
圖十四、曾文溪、鹽水溪的棲地圈繪範圍依季節呈現 ………………….. 52
圖十五、二仁溪、阿公店溪的棲地圈繪範圍依季節呈現 ……………….. 54
圖十六、高屏溪、東港溪、林邊溪的棲地圈繪範圍依季節呈現 ……….. 56
圖十七、枋山溪、楓港溪的棲地圈繪範圍依季節呈現 ………………….. 58
圖十八、卑南溪、知本溪的棲地圈繪範圍依季節呈現 ………………….. 60
圖十九、秀姑巒溪的棲地圈繪範圍依季節呈現 ………………………….. 62
圖二十、花蓮溪的棲地圈繪範圍依季節呈現 …………………………….. 64
圖二十一、立霧溪的棲地圈繪範圍依季節呈現 ………………………….. 66
圖二十二、和平溪的棲地圈繪範圍依季節呈現 ………………………….. 68
圖二十三、南澳溪的棲地圈繪範圍依季節呈現 ………………………….. 70
圖二十四、蘭陽溪 (含宜蘭河) 與新城溪的棲地圈繪範圍依季節呈現 ... 72
圖二十五、得子口溪的棲地圈繪範圍依季節呈現 ………………………… 74
圖二十六、雙溪的棲地圈繪範圍依季節呈現 …………………………….. 76
圖二十七、磺溪的棲地圈繪範圍依季節呈現 …………………………….. 78
圖二十八、HQI長期變化趨勢 …………………………………………….. 80
圖二十九、全台河川的HQI值與季節的對照 …………………………..... 80
圖三十、北部河川的HQI值與季節的對照 ……………………………..... 81
圖三十一、西南部河川的HQI值與季節的對照 …………………...…….. 81
圖三十二、東部河川的HQI值與季節的對照 …………………………..... 82
圖三十三、鰻魚資源量與HQI值的迴歸 ………………………………..... 82
圖三十四、雙溪公館大橋下方河段 ……………………………………….. 83
圖三十五、全台日本鰻與鱸鰻捕獲位置分佈圖 …………………...……... 85
表
表1、鳳山溪春季的HQI值計算表 ……………………………...………….. 85
表2、全台灣各縣市共38條河川的評估結果 ………………....………….... 85
表3、淡水河四季的計算結果 ……………………………...……………….. 86
表4、老街溪四季的計算結果 ……………………………...……………….. 89
表5、社子溪四季的計算結果 ……………………………...……………….. 90
表6、鳳山溪四季的計算結果 ……………………………...……………….. 91
表7、頭前溪四季的計算結果 ……………………………...……………….. 92
表8、客雅溪四季的計算結果 ……………………………...……………….. 93
表9、中港溪四季的計算結果 ……………………………...……………….. 93
表10、後龍溪四季的計算結果 ……………………………...…………….... 94
表11、大安溪四季的計算結果 ……………………………...…………….... 95
表12、大甲溪四季的計算結果 ……………………………...…………….... 96
表13、烏溪四季的計算結果 ……………………………...……………........ 97
表14、濁水溪四季的計算結果 ……………………………...…………….... 98
表15、北港溪四季的計算結果 ……………………………...…………….... 99
表16、朴子溪四季的計算結果 ……………………………...………….... 100
表17、八掌溪四季的計算結果 ……………………………...……………… 101
表18、急水溪四季的計算結果 ……………………………...……………… 102
表19、曾文溪四季的計算結果 ……………………………...……………… 103
表20、鹽水溪四季的計算結果 ……………………………...……………… 105
表21、二仁溪四季的計算結果 ……………………………...……………… 106
表22、阿公店溪四季的計算結果 ……………………………...…………… 107
表23、高屏溪四季的計算結果 ……………………………...……………… 108
表24、東港溪四季的計算結果 ……………………………...……………… 109
表25、林邊溪四季的計算結果 ……………………………...……………… 110
表26、枋山溪四季的計算結果 ……………………………...……………… 111
表27、楓港溪四季的計算結果 ……………………………...……………… 111
表28、知本溪四季的計算結果 ……………………………...……………… 112
表29、卑南溪四季的計算結果 ……………………………...……………… 113
表30、秀姑巒溪四季的計算結果 ……………………………...…………… 114
表31、花蓮溪四季的計算結果 ……………………………...……………… 114
表32、立霧溪四季的計算結果 ……………………………...……………… 115
表33、和平溪四季的計算結果 ……………………………...……………… 116
表34、南澳溪四季的計算結果 ……………………………...……………… 116
表35、新城溪四季的計算結果 ……………………………...……………… 117
表36、蘭陽溪四季的計算結果 ……………………………...……………… 118
表37、宜蘭河四季的計算結果 ……………………………...……………… 119
表38、得子口溪四季的計算結果 ……………………………...…………… 119
表39、雙溪四季的計算結果 ……………………………...……………….... 120
表40、磺溪四季的計算結果 ……………………………...………………… 121
表41、利用標示再捕法計算出的鳳山溪、高屏溪、宜蘭河日本鰻資源量 ... 122
dc.language.isozh-TW
dc.subject棲地破壞zh_TW
dc.subject日本鰻zh_TW
dc.subject棲地品質指數zh_TW
dc.subject衛星遙測技術zh_TW
dc.subject有效棲地面積zh_TW
dc.subjectJapanese eelen
dc.subjecthabitat destructionen
dc.subjectHabitat Quality Indexen
dc.subjectSatellite Remote Sensing Technologyen
dc.subjecteffective habitat areaen
dc.title以衛星遙測技術評估台灣主要河川日本鰻棲地品質現況zh_TW
dc.titleAssessment of present habitat quality of main rivers in Taiwan for the Japanese eel (Anguilla japonica)en
dc.typeThesis
dc.date.schoolyear106-2
dc.description.degree碩士
dc.contributor.coadvisor柯佳吟(Chia-Ying Ko)
dc.contributor.oralexamcommittee吳書平,曾晴賢
dc.subject.keyword日本鰻,棲地破壞,棲地品質指數,衛星遙測技術,有效棲地面積,zh_TW
dc.subject.keywordJapanese eel,habitat destruction,Habitat Quality Index,Satellite Remote Sensing Technology,effective habitat area,en
dc.relation.page122
dc.identifier.doi10.6342/NTU201802566
dc.rights.note有償授權
dc.date.accepted2018-08-13
dc.contributor.author-college生命科學院zh_TW
dc.contributor.author-dept漁業科學研究所zh_TW
顯示於系所單位:漁業科學研究所

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