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DC 欄位 | 值 | 語言 |
---|---|---|
dc.contributor.advisor | 侯文祥(Wen-Shang Hou) | |
dc.contributor.author | Chieh Wang | en |
dc.contributor.author | 王婕 | zh_TW |
dc.date.accessioned | 2021-06-16T03:40:07Z | - |
dc.date.available | 2018-03-16 | |
dc.date.copyright | 2015-03-16 | |
dc.date.issued | 2015 | |
dc.date.submitted | 2015-02-14 | |
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Canadian Journal of Fisheries and Aquatic Sciences, 37(9), 1421-1425. Porter, C., Krom, M., Robbins, M., Brickell, L., & Davidson, A. (1987). Ammonia excretion and total N budget for gilthead seabream (Sparus aurata) and its effect on water quality conditions. Aquaculture, 66(3), 287-297. Poxton, M., & Allouse, S. (1987). Cyclical fluctuations in ammonia and nitrite-nitrogen resulting from the feeding of turbot, scophthalmus maximus (L.), in recirculating systems. Aquacultural Engineering, 6(4), 301-322. Ramnarine, I., Pirie, J., Johnstone, A., & Smith, G. (1987). The influence of ration size and feeding frequency on ammonia excretion by juvenile Atlantic cod, Gadus morhua L. Journal of Fish Biology, 31(4), 545-559. Randall, D., & Tsui, T. (2002). Ammonia toxicity in fish. Mar Pollut Bull, 45(1), 17-23. Randall, D. J., & Wright, P. A. (1987). Ammonia Distribution and Excretion in Fish. Fish Physiology and Biochemistry, 3(3), 107-120. doi: Doi 10.1007/Bf02180412 Ruyet, J., Chartois, H., & Quemener, L. (1995). Comparative acute ammonia toxicity in marine fish and plasma ammonia response. Aquaculture, 136(1), 181-194. Ruyet, J., Galland, R., Le Roux, A., & Chartois, H. (1997). Chronic ammonia toxicity in juvenile turbot (Scophthalmus maximus). Aquaculture, 154(2), 155-171. Rychly, J. (1980). Nitrogen balance in trout: II. Nitrogen excretion and retention after feeding diets with varying protein and carbohydrate levels. Aquaculture, 20(4), 343-350. Sayer, M., & Davenport, J. (1987). The relative importance of the gills to ammonia and urea excretion in five seawater and one freshwater teleost species. Journal of Fish Biology, 31(4), 561-570. Shumway, S. E. (1990). A review of the effects of algal blooms on shellfish and aquaculture. Journal of the World Aquaculture Society, 21(2), 65-104. Smart, G. (1976). The effect of ammonia exposure on gill structure of the rainbow trout (Salmo gairdneri). Journal of Fish Biology, 8(6), 471-475. Soderberg, R. W., McGee, M., Grizzle, J., & Boyd, C. (1984). Comparative histology of rainbow trout and channel catfish grown in intensive static water aquaculture. The Progressive Fish-Culturist, 46(3), 195-199. Soderberg, R. W., & Meade, J. W. (1991). The effects of ionic strength on un-ionized ammonia concentration. The Progressive Fish-Culturist, 53(2), 118-120. Wagner, E. I., Miller, S. A., & Bosakowski, T. (1995). Ammonia excretion by rainbow trout over a 24-hour period at two densities during oxygen injection. The Progressive Fish-Culturist, 57(3), 199-205. Wajsbrot, N., Gasith, A., Krom, M. D., & Popper, D. M. (1991). Acute toxicity of ammonia to juvenile gilthead seabream Sparus aurata under reduced oxygen levels. Aquaculture, 92, 277-288. Wood, J. (1958). Nitrogen excretion in some marine teleosts. Canadian journal of biochemistry and physiology, 36(12), 1237-1242. Wu, R. (1988). Marine pollution in Hong Kong: a review. Asian Marine Biology, 5(1). Wu, R. (1995). The environmental impact of marine fish culture: towards a sustainable future. Mar Pollut Bull, 31(4-12), 159-166. Yager, T. K., & Summerfelt, R. C. (1993). Effects of fish size and feeding frequency on metabolism of juvenile walleye. Aquacultural Engineering, 12(1), 19-36. 行政院環境保護署環境檢驗所水中污染檢驗方法之開發及驗證(1996) - 水中總氮檢驗方法,EPA-85-E3S3-9 -03。 侯文祥. (1999). 行政院國家科學委員會專題計畫成果報告: 應用氣泡柱去除循 環養殖水中固形物氮化合物之聯控設計。 陳建初. (1983). 水質分析:九大圖書公司。 廖永豊. (2010). 養殖池排污方式與流場分布之關係研究, 臺灣大學生物環境系 統工程學系碩士論文。 鄭樂云.(2012). 氨氮和亞硝酸鹽對斜帶石斑魚苗的急性毒性效應,海洋科學,36 (5) :19 -22. 蔡子健. (2013).點帶石斑魚和龍膽石斑魚之氮排放速率研究, 臺灣大學漁業科學 所碩士論文。 | |
dc.identifier.uri | http://tdr.lib.ntu.edu.tw/jspui/handle/123456789/54861 | - |
dc.description.abstract | 點帶石斑魚是台灣常見的養殖魚種,不但具有高經濟價值的特性,也深受國人喜愛。目前台灣養殖石斑魚用水的方式主要為以馬達抽取沿岸海水的大量換水方式,為了減少抽水用電的耗能支出,且降低水源污染風險,考慮設計適宜的循環水系統與水處理設備,而瞭解養殖魚的氮排放速率是首要目標。本實驗以8吋(約300克)的點帶石斑魚作為實驗魚種,實驗地點於宜蘭石斑養殖場,池水量約11公噸。在實驗進行前,先將石斑魚停止餵食兩天後,開始進行空腹6小時的總氮排放速率實驗,實驗開始每1.5小時取池中三位置的水樣與收集固形物,實驗過程不開流水。空腹實驗結束後隔天,開始餵食後24小時的總氮排放速率實驗,實驗過程保持流水狀態,每4小時取樣一次,取池中三位置的水樣與收集固形物。
結果顯示,實驗前,停餵兩天後的池水總氮濃度約6.38±0.45 mg TN/L;其中固態氮1.06±0.28 mg TN/L,液態氮5.77±0.42 mg TAN/L。可知液態氮約為固態氮的5倍,液態氮占84%,固態氮占16%。 點帶石斑魚空腹之平均每小時每公斤的總氮排放速率為36.90 mg TN/kg/h,其固液態氮比例約1.08。而在餵食後24小時實驗,平均每小時每公斤魚重總氮排放速率為22.79 mg TN/kg/h。餵食後的最大的總氮排放速率出現在第4~8個小時。餵食後至少8小時後,總氮累積排放速度才又趨於平緩。而在日夜間的總氮排放速率,在日間的平均總氮濃度變化為1.31 mg TN/kg/h,在夜間的平均總氮排放速率為0.38 mg TN/kg/h,日夜間的排放速率差異約為4倍。可知在日間有光環境點帶石斑魚的總氮排放速率比夜間高,可應用在活魚運輸時,黑暗環境有助於減緩運送過程造成水質惡化。 | zh_TW |
dc.description.abstract | Grouper are common aquaculture species in Taiwan, not only has the characteristics of high economic value, but also by the people loved. At present, the main way to keep the water clean is to pump a large number of water from coastal waters, in order to reduce pumping electricity energy expenditure and reduce the risk of water pollution, the design of a suitable system and circulating water treatment equipment, and understand the cultured fish nitrogen emission rate is the primary goal.
In this experiment, we use 8 inches (about 300 grams) of grouper fish as experimental. After feeding stop for two days, the fast of total nitrogen excretion includes total ammonia nitrogen (TAN) and total ammonia. The results show, the average of nitrogen excretion rate of fast was 7.16 ± 0.45 mg L-1; wherein the solid nitrogen is 1.06 ± 0.28 mg L-1, liquid nitrogen was 6.09 ± 0.73 mg L-1. the concentrate of solid nitrogen is about 6 times more than liquid nitrogen (TAN), accounting for 85.1% of liquid nitrogen, solid nitrogen 14.9%. The average of TN emission rate for the fasting is 96.80 mg kg-1h-1, its solid-liquid ratio of 13.38. And 24 hours after the feeding experiments, the average emission rate of total nitrogen was 104.23 ± 82.62 mg kg-1h-1. The maximum emission rate of total nitrogen after feeding occurs in the first 0-4 hours. At least 8 hours after the total nitrogen discharge rate after feeding was also leveled off. Compare the light phase and dark phase, the total nitrogen emission rate of light phase is higher than dark phase, the average total ammonia emission rate of light phase is 4.85 mg L-1 h-1,and the average rate of total ammonia emissions in dark phase is 1.22 mg L-1 h-1. It can be applied when the transport of live fish, dark environment helps slow the delivery process caused by the deterioration of water quality. In this experiment, the trap as a tool to capture the solids are not only captured feces but also contains mucus from grouper, although it will not be leaving the ammonia dissolved in water concentration increased in short-term, but it is a good breeding place for bacteria and many viruses, so it’s better to remove solid particles effectively, to avoid the breeding of pathogens in water to provide a future reference design and optimization of farming systems. | en |
dc.description.provenance | Made available in DSpace on 2021-06-16T03:40:07Z (GMT). No. of bitstreams: 1 ntu-104-R01b45009-1.pdf: 7572477 bytes, checksum: bc5cc9843989f95e0f0d753016a98ab7 (MD5) Previous issue date: 2015 | en |
dc.description.tableofcontents | 目 錄
口試委員會審定書………………………………………………….……I 誌謝………...…………………………………….………………….….…II 中文摘要……………………...……………………………………..…...III 英文摘要…………….…………………......…………………………….IV 目錄……………………….……………………………….........................1 圖目錄……...……...………………….…………………….......................4 表目錄…..…………...………….……………………….................……...5 第一章、前言 1.1背景…………………………………................………………….6 1.2研究動機…………………………………………...............……..7 1.3研究目的…………………………………………..…...................8 1.4本文架構……………………….……..…………...…...................9 第二章、文獻回顧 2.1石斑魚養殖現況…………………………………......………….10 2.2 氨氮毒性對魚的影響……..…………………………….……...11 2.3 固形物收集裝置原理………....……………………………..…12 2.4不同條件之氮排放速率………………………………………..13 2.4.1空腹和餵食後的影響…………………………..……….13 2.4.2 體重的影響…………………………………....………….14 2.4.3 餵食量的影響………………………………………..…...14 2.4.4 日夜變化的影響…………………………………...……..15 2.4.5 餵食頻率的影響………………………………………….15 2.4.6不同魚種的影響……………….………………………….15 2.4.7 水溫的影響……………………………...………………..16 2.5 氮排放速率之應用………………………...……....…………...17 2.5.1 循環水養殖系統之工程設計……………….....................17 2.5.2 複合式養殖技術…………………………...……..............17 第三章、材料與方法 3.1 石斑魚的實驗現場……………...………...………….............19 3.2 飼料與飼養……………………………………………...….....20 3.3 實驗流程………………………….…………………………...21 3.3.1實驗材料……………….…………………………….......21 3.3.2空腹之氮排放速率實驗…………………………………22 3.3.3餵食後之氮排放速率實驗……………………….……...23 3.3.4水質量測……………………………………….………...25 3.4 資料整理………...……………..……………….…..................27 3.5 統計分析……………………...……………….……………....29 第四章、結果與討論 4.1 空腹在t0=0時間之池內固液態氮比例及總氮濃度分布.…….30 4.2 空腹狀態池內總氮的濃度變化及累積排放速率………….….31 4.3. 空腹狀態池內無流水的總氮排放速率….…………..………..32 4.4 攝食後單位魚重之固液態氮排放速率…………….……....….33 4.5 攝食後日夜間之固液態氮排放速率………….....…………….35 4.6空腹和餵食後之固液態氮排放速率………………………...…36 4.7 氮收支……………………………………….………...….…….37 第五章、結論與建議 5.1 結論…………………….…….………………........……………38 5.2 建議……………………………….………….........……………38 參考文獻…...……………………………………..…...…..……………..39 附錄……………………………………………………….………….…..44 圖目錄 圖3.1室外養殖池(戶外有遮雨棚)……………...…..….…………...…..19 圖3.2固形物收集器放置魚池位置: (A)池內出水口附近 (B)水池內中央偏旁處 (C)池內出水口附近………………..……….………...21 圖3.3自製蜂巢型結構的固形物收集器………………..………...….….22 表目錄 表2.1 不同魚種之最大的液態氮排放時間……..…………..………….15 表3.1不同規格固形物收集器預備試驗結果…...………………..……..22 表4.1空腹兩日後,實驗前(T0=0)於池內三處水體之固液態氮比例及 濃度分布…………………………………………………………...30 表4.2空腹固液態氮排放速率………………………...…………….…...31 表4.3空腹無流水實驗6小時間,全池內固液態氮總量變化………..…32 表4.4餵食後之固液態氮排放速率……………………………………...33 表4.5餵食後流水實驗24小時間,全池內固液態氮總量變化……….33 表4.6 餵食後24小時實驗,不同時間間隔的池內固液態總氮累積濃度 變化….…………………………………………………………....35 表4.7 餵食後24小時實驗,每4小時間隔池內總氮濃度變化……..…35 | |
dc.language.iso | zh-TW | |
dc.title | 點帶石斑魚養殖池固液態氮排放之研究 | zh_TW |
dc.title | Nitrogen Excretion of Epinephelus coioides
in Aquaculture pond | en |
dc.type | Thesis | |
dc.date.schoolyear | 103-1 | |
dc.description.degree | 碩士 | |
dc.contributor.oralexamcommittee | 廖文亮,張繼堯,謝正義,喻新 | |
dc.subject.keyword | 液態氮,排放速率,氨,點帶石斑魚,固態氮, | zh_TW |
dc.subject.keyword | ammonia,excretion rates,nitrogen,Epinephelus coioides,aquaculture, | en |
dc.relation.page | 45 | |
dc.rights.note | 有償授權 | |
dc.date.accepted | 2015-02-15 | |
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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