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  1. NTU Theses and Dissertations Repository
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請用此 Handle URI 來引用此文件: http://tdr.lib.ntu.edu.tw/jspui/handle/123456789/48530
完整後設資料紀錄
DC 欄位值語言
dc.contributor.advisor林正芳(Cheng-Fang Lin)
dc.contributor.authorYing-Chen Yangen
dc.contributor.author楊瀅臻zh_TW
dc.date.accessioned2021-06-15T07:00:44Z-
dc.date.available2011-08-22
dc.date.copyright2011-08-22
dc.date.issued2011
dc.date.submitted2011-08-19
dc.identifier.citationAlder M.G. and Hill G.R., 1950,”The Kinetics and Mechanism of Hydroxide Ion Catalyzed Ozone Decomposition in Aqueous Solutions”, J. Am. Chem. Soc. 72, 1884-1886
Bougrier C., C. Albasi b, Delgen`e J.P., Carr`ere H., 2006,”Effect of ultrasonic, thermal and ozone pre-treatments on waste activated sludge solubilisation and anaerobic biodegradability”, Chemical Engineering and Processing 45, 711-718
Chu L.B., Yan S.T., Xing X.H., Yu A.F., Sun X.L., Jurcik B., 2008,“Enhanced sludge solubiliztion by microbubble ozonation”, Chemosphere 72, 205-212
Chu W., Chan K. H. and Graham M.J.D., 2006, “Enhancement of ozone oxidation and its associated processes in the presence of surfactant: Degradation of atrazine” , Chemosphere 64, Issue 6, 931-936
Dogruel S., Sievers M. and Germirli-Babuna F., 2007,”Effect of Ozonation on Biodegradability Characteristics of Surplus Activated Sludge“, Ozone: Science & Engineering 29, 191-199
Elliott A., Mahmood T., 2007, “Pretreatment technologies for advancing anaerobic digestion of pulp and paper biotreatment residues”, Water Research 41, 4273 – 4286
Heaven S., Milledge J., Zhang Y., 2011, “Comments on ‘Anaerobic digestion of microalgae as a necessary step to make microalgal biodiesel sustainable’”, Biotechnology advances 29, 164-167
Hong P.K. A., Cai X. and Cha Z., 2008, “Pressure-assisted chelation extraction of lead from contaminated soil“, Environmental Pollution 153, 14-21
Kleiser G., Frimmel F.H.,(2000), “Removal of precursors for disinfection by-products(DBPs)- differences between ozone – and OH-radical-induced oxidation”, The Science of The Total Environment Vol. 256, 1-9
McCarty P. L. and Smith D.P., 1986,”Anaerobic waste-water treatment 4” , Environmental Science & Technology 20, (12), 1200-1206
Mines R.O., JR, Northenor C.B. and Murchison M., 2008,“Oxidation and ozonation of waste activated sludge”, Journal of Environmental Science and Health Part A 43, 610-618
Parkin G.F. and Owen W.F., 1986,”Fundamentals of anaerobic digestion of wastewater sludges”, Journal of Environmental Engineering 112, No. 5, 867-920
Samson R., LeDuyt A., 1986, “Detailed study of anaerobic digestion of Spirulina maxima algal biomass”, Biotechnol Bioeng. 7, 1014-23.
Sanchez Hernandez E.P., Travieso Cordoba L., 1993, “Anaerobic digestion of Chlorella vulgaris for energy production”, Resources Conservation and Recycling 9 (1-2), 127-132
Sialve B., Bernet N. and Bernard O., 2009,“Anaerobic digestion of microalgae as a necessary step to make microalgal biodiesel sustainable”, Biotechnology Advances 27, 409-416
Travieso, L. et al., 2008, “Batch culture growth of Chlorella zofingiensis on effluent derived from two-stage anaerobic digestion of two-phase olive mill solid waste”, Electronic Journal of Biotechnology 11(2)
Weemaes M, Grootaerd H, Simoens F, Huysmans A and Verstraete W., 2000, “Ozonation of sewage sludge prior to anaerobic digestion”, Water Science & Technology 42 (9),175–178
Zamalloa C., Vulsteke E., Albrecht J. and Verstraete W., 2010, “The techno-economic potential of renewable energy through the anaerobic digestion of microalgae”, Bioresource Technology 102, 1149-1158
邊逢沂、謝清樹,2003,上流式厭氧污泥反應槽-UASB實場應用介紹,工業污染防治第87期
周松霖,2005,前氧化劑處理水中藻類最佳化操作之研究,碩士論文,國立成功大學環境工程學系
王智昱,2007,發光二極體(LED)於螺旋藻培養的應用,碩士論文,國立中興大學化學工程學系
蕭茂修,2007,以海洋微藻固定CO2 並作為生質能源之研究,碩士論文,國立成功大學環境工程學系
李括,2010,藻類生物質可再生能源的甲烷發酵,上海交通大學環境科學與工程學院
dc.identifier.urihttp://tdr.lib.ntu.edu.tw/jspui/handle/123456789/48530-
dc.description.abstract本論文研究前處理破裂藻體結構對於微藻進行厭氧消化產甲烷之影響。前處理包含臭氧與高壓循環系統,高壓輔助系統是一種利用增壓與減壓反覆循環製造快速壓差以破裂藻類細胞結構的前處理方式。厭氧消化將微藻轉化成沼氣,其效率受藻類水解時間影響,臭氧與高壓循環系統釋放藻體內部基質,縮短厭氧消化水解時間。臭氧破裂藻類效果可藉由水中綠色素消失判定所需的臭氧曝氣時間,做為最適合的厭氧消化產氣進料,臭氧破裂淡水藻的處理效率(COD Solubilisation)可達19.63%,海水藻可達52.16%。然而,處理效率與水體中化學需氧量的分布無相對應關係,SCOD隨著曝臭氧時間上升再下降,TCOD隨著臭氧反應時間下降。
  藻類厭氧消化產氣系統不適用於高鹽度的海水藻,鹽度抑制厭氧消化菌活性,造成產氣量下降,使用海水藻作為厭氧產氣基質來源時,需選擇耐鹽度性高的厭氧污泥,或將液體中的鹽度去除。假設空白系統中的產氣量皆為污泥自行分解的產氣量時,進行厭氧消化試驗,在148.40 g厭氧污泥乾重對應1 g的藻類固體乾重的厭氧消化實驗參數下,淡水藻做微生物發酵基質,添加10.52 mg 藻類COD,將甲烷濃度由16.38%提升至22.15%,而添加9.2 mg經臭氧破裂後藻類的COD,將甲烷濃度提升至20.67%,結果顯示臭氧破裂藻類進行厭氧消化,對於最終甲烷濃度提高無明顯的效果。
  濃縮藻類可以提高厭氧消化產甲烷濃度,將藻液濃縮使COD提高為原本的2.47倍,產出的甲烷濃度為濃縮前的2.18倍,表示增加COD進料提供更多反應基質。
zh_TW
dc.description.abstractIn order to enhance the efficiency of anaerobic digestion, the effects of ozonation and high-pressure extraction were studied on microalgae. High-pressure extraction was performed with mildly elevated pressure in consecutive cycles of compression and decompression as pretreatment. Anaerobic digestion converts the organics present in microalgae into biogas, but the efficiency and the digestion rate are limited by the hydrolysis. Biodegradability of microalgae could be low depending on the nature of the cell wall, thus pretreatment was applied to rupture the cell wall in order to improve biodegradability efficiencies.
  Chemical oxygen demand (COD) and matter solubilisation caused by pretreatments was focused on organic solids. In terms of ozone pretreatment, COD solubilisation was 19.63% and 52.16% on flesh water algae and sea water algae, respectively. No significant relationship between COD solubilisation and SCOD/TCOD was observed, however, it was found that SCOD increased with ozone feeding time and then decreased, while TCOD decreased with ozone feeding time.
  In this study, anaerobic bacteria are unable to adapt the saline environment, and have low capability to deal with sea microalgae that has high saline contents. The experimental results showed that the methane production decreased when salt content is higher. However, if anaerobic digestion is used to treat the saline wastewater, the capability of anaerobic bacteria must be enhanced or remove the saline content.
  In flesh water algae system, the final methane concentrations increased from 16.38 to 22.15% when adding 10.52 mg COD of algae; the final methane concentrations increased to 20.67% when adding 9.2 mg COD of algae with ozone pretreatment. The result suggested that ozone extraction did not have significant impact on methane production.
  The final methane concentrations increased from 4.23 to 9.21% when the COD concentration of microalgae increased from 511 to 1262 mg/L. It could be concluded that inoculum/substrate ratio had a considerable effect on methane production.
en
dc.description.provenanceMade available in DSpace on 2021-06-15T07:00:44Z (GMT). No. of bitstreams: 1
ntu-100-R98541112-1.pdf: 1422995 bytes, checksum: 39960d2d392f7c8ee0099e486e330914 (MD5)
Previous issue date: 2011
en
dc.description.tableofcontents誌謝 I
摘要 II
Abstract III
目錄 V
圖目錄 VII
表目錄 VIII
第一章 前言 1
1.1 研究緣起 1
1.2 研究內容與項目 2
第二章 文獻回顧 3
2.1 藻類簡介 3
2.1.1 藻類培養 3
2.1.2藻類應用 4
2.2 破裂細胞技術 5
2.2.1 臭氧破裂機制 6
2.2.2高壓循環輔助系統 7
2.3 厭氧消化 8
第三章 實驗方法與材料 10
3.1 實驗架構與流程 10
3.2 藻類與菌種 11
3.2.1藻類來源與培養 11
3.2.2菌種來源與性質 12
3.3破裂細胞處理 13
3.3.1 臭氧高壓循環系統 13
3.3.2 實驗步驟 14
3.4厭氧消化設備與實驗參數 15
3.4.1 厭氧消化設備 15
3.4.2 厭氧消化實驗參數 18
3.5 實驗分析項目與儀器 19
3.5.1 水質分析 19
3.5.2 氣體分析 21
第四章 結果與討論 22
4.1 前處理破裂藻體 22
4.1.1 最佳前處理方式 22
4.1.2 臭氧破裂藻體效能 24
4.2 厭氧消化 27
4.2.1 海水藻與淡水藻厭氧消化 27
4.2.2 破裂藻體厭氧消化 30
4.2.3 不同有機負荷厭氧消化 31
第五章 結論與建議 34
5.1 結論 34
5.2 建議 35
參考文獻 36
附錄 39
dc.language.isozh-TW
dc.title利用臭氧與高壓循環系統破裂藻體以提高厭氧消化之甲烷產能zh_TW
dc.titleIncreased Methane Production by Microalgae Anaerobic Digestion with Ozone and High-pressure Pretreatmenten
dc.typeThesis
dc.date.schoolyear99-2
dc.description.degree碩士
dc.contributor.coadvisor張能復(Len-Fu Chang)
dc.contributor.oralexamcommittee康佩群(Andy P.K. Hong)
dc.subject.keyword厭氧消化,微藻,臭氧,高壓,臭氧與高壓循環,甲烷,zh_TW
dc.subject.keywordAnaerobic digestion,Microalgae,Ozonation,Pressure cycle,Methane,en
dc.relation.page42
dc.rights.note有償授權
dc.date.accepted2011-08-19
dc.contributor.author-college工學院zh_TW
dc.contributor.author-dept環境工程學研究所zh_TW
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