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| DC 欄位 | 值 | 語言 |
|---|---|---|
| dc.contributor.advisor | 施信民(Shih-Min Shih) | |
| dc.contributor.author | Chih-Wei Chang | en |
| dc.contributor.author | 張至緯 | zh_TW |
| dc.date.accessioned | 2021-06-13T02:37:21Z | - |
| dc.date.available | 2007-01-24 | |
| dc.date.copyright | 2007-01-24 | |
| dc.date.issued | 2006 | |
| dc.date.submitted | 2007-01-17 | |
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Absorption of SO2 by iron blast furance slag/hydrated lime sorbents. Proceedings Symposium on Transport Phenomena and Its Applications, Taipei, Taiwan, 2001, 703. Liu, C. F., Shih, S. M., & Lin, R. B. Kinetics of the reaction of Ca(OH)2/fly ash sorbent with SO2 at low temperature. Chemical Engineering Science, 2002, 57, 93. Liu, C. F., & Shih, S. M. Enhancement of the reactivities of iron blast furance slag/hydrated lime sorbents toward SO2 by NaOH. Journal of the Chinese Institute of Chemical Engineers, 2003, 34(5), 525. Liu, C. F., & Shih, S. M. Effect of NaOH addition on the reactivities of iron blast furance slag/hydrated lime sorbents for low-temperture flue gas desulfurization. Industrial & Engineering Chemistry Research, 2004a, 43, 184. Liu, C. F., & Shih, S. M. Kinetics of the reaction of iron blast furance slag/hydrated lime sorbents with SO2 at low temperature: Effects of sorbent preparation conditions. Chemical Engineering Science, 2004b. Liu, C. F., Shih, S. M., & Lin, R. B. Kinetic Model for the Reaction of Ca(OH)2/Fly Ash Sorbents with SO2 at Low Temperatures. Ind. Eng. Chem. Res., 2004, 43, 4112. Liu, Y., Che, D., & Xu, T. Effects of NaCl on the Capture of SO2 by CaCO3 during coal combustion. Fuel, 2006, 85, 524. Lowell, P. S., & Parson, T. B. Identification of Regenerable Metal Oxide SO2 Sorbents for Fluidized-bed Coal Combustion. Report by Radian Corporation, Austin, Texas, 1975, EPA-650/2-75-065. Mahuli, S. K., Agnihotri, R., Jadhav, R., Chauk, S., & Fan, L. S. Combined Calcination, Sintering and Sulfation Model for CaCO3-SO2 Reaction. AIChE Journal, 1999, 45, 2. Martinez, J. C., Izquierdo, J. F., Tejero, J., & Querol, J. Reaction of fly ash and Ca(OH)2 mixtures for SO2 removal of flue gas. Industrial & Engineering Chemistry Research, 1991, 30, 2143. Milne, C. R., Silcox, G. D., Pershing, D. W., & Kirchgessner, D. A. Calcination and sintering models for application to high-temperature, short-time sulfation of calcium-based sorbents. Ind. Eng. Chem. Res., 1990, 29. 139. Miller, M. J. Retrofit SO2 and NOx Control Technologies for Coal-Fired Power Plants. Environ. Prog., 1986, 5, 171. Okutani, T., Furuichi, T., & Ishii, T. Preparation of Calcium Aluminates by Solid State Reaction of CaSO4-Al2O3 System and Reactivity for SO2. J. Chem. Soc. Japan, 1975, 9, 1485. Ortiz, I., Cortabitarte, F., Garea, A., & Irabin, A. Flue gas desulfurization at low temperature characterization of the structural changes in the solid sorbents. Powder technology, 1993, 75, 167. Reed, G. D., Davis, W. T., & Pudelek, R. E. Analysis of Coal Fly Ash Properties of Importance to Sulfur Dioxide Reactivity Potential. Environmental Science & Technology, 1984, 18, 548. Renedo, M. J., Fernandez, J., Garea, A., Ayerbe, A, & Irabien, J. A. Microstructural changes in the desulfurization reaction at low temperature. Industrial Engineering and Chemical Research, 1999, 38, 1384. Ruiz-Alsop, R. N. Reaction of SO2 with Ca(OH)2. Ph. D. Dissertation Department of Chemical Engineering, The University of Texas at Austin. 1986. Ruiz-Alsop, R. N., & Rochelle, G. T. Effect of deliquescent salt additives in the reaction of SO2 with Ca(OH)2. ACS. Symp. Ser. 1986, 88. Shi, L., & Xu, X. Partially Sulfated Lime-Fly Ash Sorbents Activated by Water or Stream for SO2 Removal at a Medium Temperature. Energy & Fuels, 2005, 19, 2335. Shih, S. M., Hung, J. T., Wang, T. Y., & Lin, R. B. Kinetics of the Reaction of Sulfur Dioxide with Calcium Oxide Powder. J. Chin. Inst. Chem. Engrs., 2004, 35, 4, 447. Shih, S. M., Ho, C. S., Song, Y. S., & Lin, J. P. Kinetics of the reaction of Ca(OH)2 with CO2 at low temperature. Industrial & Engineering Chemistry Research, 1999, 38, 1316. Skoog, D. A., Holler, F. J., & Niman, T. A. Principles of Instrumental Analysis, Fifth Edition. Snyder, R. B., Wilson, W. I., Vogel, G. J., & Jonke, A. A. Sulfation and Regeneration of Synthetic Additives. Proc. Fourth Intern. Conf. FBC, U. S. 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AIChE Journal, 2002, 16, 1585. 劉瓊芳。氫氧化鈣/燻矽與氫氧化鈣/飛灰吸收劑與二氧化硫反應之動力學研究。國立台灣大學:碩士論文,1999。 劉瓊芳。以爐石/氫氧化鈣吸收劑去除煙道氣中二氧化硫之研究。國立台灣大學:博士論文,2004。 吳奇穎。燃煤鍋爐中高反應性二氧化硫吸收劑之製備。國立台灣大學:碩士論文,2004。 宋文方。轉爐石吸收二氧化硫之研究。國立台灣大學:碩士論文,2005。 楊文德。石灰石與二氧化硫低溫反應之動力學研究。國立台灣大學:碩士論文,2000。 | |
| dc.identifier.uri | http://tdr.lib.ntu.edu.tw/jspui/handle/123456789/31232 | - |
| dc.description.abstract | 本研究以微分反應器模擬火爐乾吸收劑注入法,針對飛灰/氫氧化鈣吸收劑的飛灰/氫氧化鈣組成、不同種類之飛灰、硫酸化反應前的煅燒處理及吸收劑前處理的漿化處理等四種可能影響反應性之變因作一探討,並分別探討各情況在短時間及長時間(1小時)之結果。
吸收劑的漿化處理是將飛灰/氫氧化鈣混合物於水固比10/1、溫度65℃下漿化16小時後予以乾燥6小時;煅燒處理是將吸收劑,於950℃下煅燒20分鐘;硫酸化反應是在空氣流速4 L/min、二氧化硫濃度3000 ppm、反應溫度950℃下進行反應。 飛灰/氫氧化鈣吸收劑經漿化處理後生成箔片狀矽酸鈣水合物,其比表面積較氫氧化鈣及飛灰大,但高溫下吸收劑會因燒結而降低反應性,飛灰含量越高,燒結越嚴重。吸收劑一小時的鈣利用率在飛灰/氫氧化鈣配比小於約4/6時高於Ca(OH)2本身,但二氧化硫捕捉率則隨飛灰含量增加而下降,飛灰本身無反應性。 所用的兩種飛灰其鈣/矽比較小者所製備的吸收劑之初始反應速率較快,但長時間的結果則受飛灰影響不大。吸收劑未經煅燒時初使反應性較經煅燒者佳,但長時間下二者差異不大。漿化處理與否對於一小時鈣利用率及二氧化硫捕捉率皆有明顯的影響,在飛灰/氫氧化鈣比配比高於3/7以上時,未經漿化處理之吸收劑則以之反應性明顯高於經漿化者。 在高溫下除硫,於Ca(OH)2中添加適量的飛灰可以提升其鈣利用率,但會抑制整體吸收劑的二氧化硫捕捉率。 | zh_TW |
| dc.description.abstract | A differential fixed-bed reactor was employed to simulate the furnace dry injection process in order to study the reaction between
sorbents and SO2. The effects of fly ash/Ca(OH)2 weight ratio, the type of fly ash, the process of calcination, the process of slurrying ,and reaction time on sorbent reactivity were studied. The fly ash/Ca(OH)2 mixture was slurried at a liquid/solid ration of 10/1 and 65℃,for 16h, and then dried for 6h. The sorbent was calcined at 950℃ for 20 min. The sulfation of sorbent was carried out at an air flow rate of 4L/min, 3000 ppm SO2, and 950℃. Foil-like calcium silicate hydrates, which were formed by the reaction between Ca(OH)2 and SiO2 in the slurry, were found in the fly ash/Ca(OH)2 sorbents. The fly ash/Ca(OH)2 sorbents have greater surface areas than Ca(OH)2 or fly ash. But these sorbents tended to inter at high temperatures when the flyash content was high, and their reactivities were thus reduced. The on hour Ca utilization for a fly ash/Ca(OH)2 sorbent was higher than that of Ca(OH)2 alone when the weigh ratio was less than about 4/6; but the on hour SO2 capture decreased as the fly ash content increased. Fly ash itself was unreactive. The type of fly ash affected only the initial reaction rate of a fly ash/Ca(OH)2sorbent;the one with lower Ca/Si ratio gave a higher initial rate. The uncalcined sorbents were more reactive than the calcined ones in the initial period of reaction, but they did not differ much at long reaction time. Whether the sorbent was slurried or not had freat effect on the sorbent reactivity. The unslurried sorbents were much more reative than the slurried ones when the fly ash/Ca(OH)2 ratio was higher than 3/7. In high-temperature desulfurization, adding proper amount of fly ash to Ca(OH)2 sorbent could raise the utilization of Ca(OH)2, but would reduce the amount of SO2 captured per unit weight of the sorbent mixture. | en |
| dc.description.provenance | Made available in DSpace on 2021-06-13T02:37:21Z (GMT). No. of bitstreams: 1 ntu-95-R93524032-1.pdf: 3121977 bytes, checksum: 7dc1753eb8e9ff0cc19b477bf9683f07 (MD5) Previous issue date: 2006 | en |
| dc.description.tableofcontents | 中文摘要……………………………………………………………. I
英文摘要……………………………………………………………. III 符號說明……………………………………………………………. IV 圖表索引……………………………………………………………. V 第一章 緒論………………………………………………………. 1 第二章 文獻回顧…………………………………………………. 4 2.1 二氧化硫污染之防治技術……………………………………. 4 2.1–1 二氧化硫…………………………………………….... 4 2.1–2 減少二氧化硫排放之技術……………………………. 5 2.2 飛灰/氫氧化鈣吸收劑與二氧化硫低溫反應…………………. 10 2.3 吸收劑與二氧化硫高溫反應………………………………….. 18 2.3–1 石灰石與熟石灰………………………………………. 18 2.3–2 其他吸收劑……………………………………………. 20 第三章 實驗與分析方法…………………………………………. 22 3.1 試料來源及吸收劑製備過程…………………………………. 22 3.1–1 試料來源……………………………………………….. 22 3.1–2 飛灰之成分分析……………………………………….. 24 3.1–3 吸收劑製備過程……………………………………….. 25 3.2 反應實驗 29 3.2–1 反應實驗裝置………………………………………… 29 3.2–2 反應實驗步驟………………………………………… 33 3.3 吸收劑物性與化性分析………….…………………………….. 36 3.3–1 BET比表面積測定…………………………………… 36 3.3–2 粒徑分析………………………………………………. 36 3.3–3 感應耦合電漿分析 (ICP)…………………………….. 36 3.3–4 掃描式電子顯微鏡觀察(SEM)...…………………….. 38 3.3–5 離子層析(IC) …………………………………………. 38 3.3–5 X射線繞射分析(XRD)…………………………….… 39 3.4 吸收劑轉化率及二氧化硫捕捉率測定……………………….. 40 第四章 結果與討論…….…………………………………………. 54 4.1 吸收劑結構性質……………………………………………….. 54 4.1–1 吸收劑粒徑………………….………………………….. 54 4.1–2 吸收劑BET比表面積………………………………….. 54 4.1–3 X–Ray繞射分析………………………………………. 57 4.1–4 SEM觀察……………………………………………… 61 4.2 吸收劑與二氧化硫之反應..…………………………………… 64 4.2–1 微分床條件之驗證………………….…………………. 64 4.2–2 吸收劑組成對吸收劑反應性之影響…………………. 66 4.2–3 飛灰種類對吸收劑反應性之影響……………..………. 73 4.2–4 煅燒與否對吸收劑反應之影響………………………... 73 4.2–5 漿化與否對吸收劑反應之影響……………………….. 79 4.2–6 與低溫反應結果之比較………………………………... 83 4.2–7 X-Ray繞射分析………………………………………. 85 4.2–8 SEM 觀察…………………………………………….. 88 第五章 結論………………………………………………………. 92 參考文獻……………………………………………………………. 94 附錄…………………………………………………………………. 101 | |
| dc.language.iso | zh-TW | |
| dc.subject | 硫酸化 | zh_TW |
| dc.subject | 二氧化硫 | zh_TW |
| dc.subject | 高溫 | zh_TW |
| dc.subject | 氫氧化鈣 | zh_TW |
| dc.subject | 飛灰 | zh_TW |
| dc.subject | high temperature | en |
| dc.subject | SO2 | en |
| dc.subject | fly ash | en |
| dc.subject | Ca(OH)2 | en |
| dc.subject | sulfation | en |
| dc.title | 飛灰/氫氧化鈣吸收劑高溫吸收二氧化硫之研究 | zh_TW |
| dc.title | Absorption of SO2 by Fly Ash/Ca(OH)2 sorbents at High Temperature | en |
| dc.type | Thesis | |
| dc.date.schoolyear | 95-1 | |
| dc.description.degree | 碩士 | |
| dc.contributor.oralexamcommittee | 林俊一,張慶源 | |
| dc.subject.keyword | 飛灰,氫氧化鈣,硫酸化,高溫,二氧化硫, | zh_TW |
| dc.subject.keyword | fly ash,Ca(OH)2,sulfation,high temperature,SO2, | en |
| dc.relation.page | 102 | |
| dc.rights.note | 有償授權 | |
| dc.date.accepted | 2007-01-17 | |
| dc.contributor.author-college | 工學院 | zh_TW |
| dc.contributor.author-dept | 化學工程學研究所 | zh_TW |
| 顯示於系所單位: | 化學工程學系 | |
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