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完整後設資料紀錄
DC 欄位 | 值 | 語言 |
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dc.contributor.author | 黃蒨菡 | zh_TW |
dc.date.accessioned | 2021-07-01T08:16:09Z | - |
dc.date.available | 2021-07-01T08:16:09Z | - |
dc.date.issued | 1992 | |
dc.identifier.citation | 吳俊宗、王怡文,1988.翡翠水庫藻類相調查及水質優養檢測系統之建立,研究報告,中央研究院植物研究所 翡翠水庫優養調查計劃研究報告,1988,臺北自來水事業處 1986. Standard Methods for the Examination of water and wastewater. American Public Health Association. Washington,DC.,pp117-178 Aziz, K.M.S. 1974. Diarrhea toxin obtained from a water bloom-producing species Microcystis aeruginosa K?tzing. Science 183:1206-1207 Booker, M.J. and Walsby, A.E. 1981. Bloom formation and stratification by a planktonic blue-green alga in an experimental water column. Br.Phycol.J. 16:1-11 Carmichael, W.W., Jones, C.L.A., Mahmood, N.A., Theiss, W.C. 1985. Algal toxins and water-based diseases, In Straub,C.R. (ed.) Critical Review in Enviromental centrol, 15:275-313, CRC Press, Inc, Boca Raton, Florida. Colman, J.A.and Santha, C.R. 1988.Criticle concentratuons of tissue nitrogen and phosphorus for growth rate and yieid of the freshwater blue-green alga Microcystis aeruginosa K?tz in the tropics. Aquatic Botany 32: 167-177 Darley, W.M. 1982.Algal biology: a physiological approach. In Wilkinson, J.F. (ed.) Basic Microbiology 9:34-39 Dugdale, R.C. and Goering, J.J. 1967. Uptake of neco and generated forms of nitrogen in primary productivity. Limnol. Oceanogr. 12:196-206 Fallon, R.D. and Brock, T.D. 1981. Overwintering of Microcystis in lake Mendota. Freshwater Biol. 11:217-226 Fogg, G.E., Stewart,W.G.P., Fay,P. and Walsby, A.E. 1973. The Blue green algae.pp.93-110 Academic Press, London. Ganf, G.G., 1974. Diurnal mixing and the vertical distribution of phytoplankton in a shallow equatorial lake (Lake Georg Vganda). J.Ecol. 62:611-629 Ganf, G.G., and Oliver, R.L. 1982. Vertical separation of light and available nutrients as a factor causing replacement of green algae by blue green algae in the plankton of stratified lake. J. Ecol. 70:829-844 Gerloff, G.C., Fitzgerald, G.P., and Skoog, F. 1950. 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The interaction between cell density of Microcystis batch cultures and light induced stress conditions. Z Pflanzenphysiol. 95:441-447 Kruger, G.H., Eloff, J.H. 1981. The effect of physicochemical factors on growth relevant to the mass culture of axenic Microcystis. In Carmichael, W.W. (ed.), The Water Environment Agal Toxins and Health Plenum Press, New York, pp. 193-222 Lorenzen, H. and Venkataraman, G.S. 1972. Synchrony in blue-green alga In: Prescott, D.M. (ed.) Methods in cell physiology 15:373-383 Academic Press. New York, London. Mclachlan, J. and Gorham, P.R. 1961 Growth of Microcystis aeruginosa K?tz.in a precipitate-free medium buffered with TRIS. Can. J. Microbiol. 7:869-882 Okada, M. and Aiba, S. 1986. Simulation of water-bloom in a eutrophic lake-IV. Modeling the vertical migrations in a population of Microcystis aeruginosa. Wat. Res. 20:485-490 Okino, T. 1973. Studies on the blooming of Microcystis aeruginosa. Jap. J. Bot. 20:381-402 Paerl, H.W. and Ustach,J.F. 1982. 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Elenkin in Rostherne Mere, England. Hydrobiologia 48:17-23 Rhee, G-Y. 1973. A continuous culture study of phosphate uptake growth rate and polyphosphate in Scenedesmus sp. J.Phycol. 9:495-560 Rhee, G-Y.1974. Phosphate uptake under nitrate limitation by Scenedesmus sp. and its ecological implications. J.Phycol. 10:470-5 Rhee, G-Y. 1978. Effects of N:P atomic ratios and nitrate limitation on algal growth, cell competition and nitrate uptake. Limnol. Oceanogr. 23:10-25 Rhee, G-Y. and Gotham, I.J. 1980. Optimum N:P ratio and the coexistence of planktonic algae. J.Phycol.16:486-9 Robarts, R.D. 1979. Underwater light penetraton, chlorophyll a and primary production in a tropical African lake (Lake Mollwaine, Rhodesia). Arch. Hydrobiol. 86:423-444 Scott, W.E., Barlow, W.J., and Hauman, J.H. 1981. Studies on the ecology, growth and physiology of toxic Microcystis aeruginosa in South Africa. In Carmichael, W.W. (ed.), The Water Environment Algal Toxins and Health. Plenum Press, New York pp 1-13 Takamura, N., Yasuno, M. and Sugahara, K. 1984. Overwintering of Microcystis aeruginosa K?tz. in a shallow lake. J. Plankton Res. 6:1019-1029 Terry, K.L. 1980. Nitrogen and phosphorus requirements of Pavlova lutheri in continuous culture. Bot. Mar. 13:757-64 Tilman, D. 1977. Resource competition between planktonic algae: an experimental and theoretical approach. Ecology 58:338-48 Tilman, D. 1976. Ecology competition between algae: experimental confirmation of resource-based competition theory Science 192:463-5 Ulrich, A. 1952. Physiological bases for assessing the nutritional requirements of plants. Annual Rev. Plant Phys. 3:207-228 Walsby, A.E. 1972. Structure and function of gas vacuoles. Bact.Rev. 36:1-32 Zehnder, A. and Gorham,P.R. 1960. Factors influencing the growth of Microcystis aeruginosa K?tz. Emend. Elenkin. Can. J.Microbiol. 6:645-660 | |
dc.identifier.uri | http://tdr.lib.ntu.edu.tw/jspui/handle/123456789/75883 | - |
dc.description.abstract | 本論文以分離自翡翠水庫之銅綠微囊藻(Microcystis aeruginosa品系2396)為材料,探討此藻種發生藻華現象之生態生理因數。藻種經純化後培養於室內,形成單細胞,其最佳生長的溫度為34℃,光度為200μEm-2s-1,酸鹼值近於7。在生長之指數期,其細胞內之總有機氮及總磷含量下降,至靜止期,其細胞內磷含量增高,並於末期有有機碳之釋出。而細胞含磷量增加與細胞內反應磷含量之增加有關,而無聚磷酸產生。於指數期末期測得之氮、磷原子數比為22:1。此藻種對硝酸氮、銨氮、尿素之利用效率相同,在硝酸氮濃度為14μg.ml-1,磷酸濃度為2μg.ml-1時生長速率最大,當培養基中氮,磷原子數含量比範圍為11?22時生長最好。對氮及磷皆有過量消耗的情形產生,且以對磷尤甚,於湖水中作不同營養鹽之添加,則添加氮及磷之影響與添加所有重要元素相同,其中又以氮的影響最大。並對照1988年水庫之研究報告,指出於藻華發生時之水域中有大量含氮污染源流入,故對於M. aeruginosa品系2396而言水庫水域中之含氮營養鹽濃度可能是其主要之限制因數。 | zh_TW |
dc.description.abstract | A strain of Microcystis aeruginosa (No.2396) was isolated from Feitsuiku Reservoir during the bloom of thist species in it. The purpose of this study is to find out the relationship between enviromented factors and mass growth of this species. The characterization of the growth condition of this strain showed that the optimum growth condition was under 34℃, 200 μEm-2s-1 and pH at 7.0. At exponential stage of growth, the intracellular organic carbon and phosphorous content were lower than at other stage. At stationary stage, the intracellular phosphate increased with the release of total organic carbon to the medium. The increase in intracellular phosphate were found to be due to the increase of due to the increase of dissoved reactive phosphate in the cells rather than the accumulation of polyphosphate. At exponential stage, the atomic ratios of intracellular N/P was about 22. M. aeruginosa strain 2396 utilized nitrate nitrogen, ammonium nitrogen and Urea in about the same rate. The maximum growth rates were obtained when the nitrate and phosphate were 14ug.ml-1 and 2ug.ml-1, respectively under this condition, the N/P ratios was 11-22. A luxury consumption was revealed for both elements. An experment conducted with the enrichment of N and/or P in the lake water, from which this strain was isolated showed that N played more important role than P for the growth of this species of phytoplankton. This meets well with the results of the analysis of lake water during the bloom in July of 1988. | en |
dc.description.provenance | Made available in DSpace on 2021-07-01T08:16:09Z (GMT). No. of bitstreams: 0 Previous issue date: 1992 | en |
dc.description.tableofcontents | 中文摘要……………………………………………………1 英文摘要……………………………………………………2 一、前言……………………………………………………3 二、材料與方法……………………………………………………6 三、結果……………………………………………………13 3.1.藻種形態之觀察……………………………………………………13 3.2.生長時期之觀察……………………………………………………13 3.3.光照強度對生長之影響……………………………………………………14 3.4.溫度對生長之影響……………………………………………………14 3.5.酸鹼度對生長之影響……………………………………………………14 3.6.不同氮源下生長情形之比較……………………………………………………14 3.7.磷濃度對生長速率之影響……………………………………………………15 3.8.氮、磷比值對生長速率之影響……………………………………………………15 3.9.氮源濃度對細胞內氮濃度之影響……………………………………………………16 3.10.磷源濃度對細胞內磷濃度之影響……………………………………………………16 3.11.水庫水樣添加營養鹽之影響……………………………………………………16 四、討論……………………………………………………17 參考文獻……………………………………………………21 圖表……………………………………………………27 | |
dc.language.iso | zh-TW | |
dc.title | 銅綠微囊藻在水庫中大量繁殖之生態因數的研究 | zh_TW |
dc.date.schoolyear | 80-2 | |
dc.description.degree | 碩士 | |
dc.relation.page | 46 | |
dc.rights.note | 未授權 | |
dc.contributor.author-dept | 生命科學院 | zh_TW |
dc.contributor.author-dept | 植物科學研究所 | zh_TW |
顯示於系所單位: | 植物科學研究所 |
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