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| DC 欄位 | 值 | 語言 |
|---|---|---|
| dc.contributor.advisor | 施信民 | |
| dc.contributor.author | Chih-Hsiang Yang | en |
| dc.contributor.author | 楊智翔 | zh_TW |
| dc.date.accessioned | 2021-06-16T17:43:43Z | - |
| dc.date.available | 2012-08-17 | |
| dc.date.copyright | 2012-08-17 | |
| dc.date.issued | 2012 | |
| dc.date.submitted | 2012-08-14 | |
| dc.identifier.citation | Bassett, H. Journal of the Chemical Society, 1270, (1934).
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Liu, C. F., Shih, S. M., and Lin, R. B. Kinetic Model for the Reaction of Ca(OH)2/Fly Ash Sorbents with SO2 at Low Temperatures. Industrial & Engineering Chemistry Research, 43, 4112-4117, (2004a). Liu, C. F., and Shih, S. M. Iron Blast Furnace Slag/Hydrated Lime Sorbents for Flue Gas Desulfurization. Environmental Science & Technology, 38, 4451-4456, (2004b). Liu, C. F., and Shih, S. M. Kinetics of the Reaction of Iron Blast Furnace Slag/Hydrated Lime Sorbents with SO2 at Low Temperatures: Effects of Sorbent Preparation Conditions. Chemical Engineering Science, 59, 1001–1008, (2004c). Liu, C. F., and Shih, S. M. Effects of Flue Gas Components on the Reaction of Ca(OH)2 with SO2. Industrial & Engineering Chemistry Research, 45, 8765-8769, (2006). Liu, C. F., and Shih, S. M. Kinetics of the Reaction of Hydrated Lime with SO2 at Low Temperatures: Effects of the Presence of CO2, O2, and NOx. Industrial & Engineering Chemistry Research, 47, 9878–9881, (2008). Liu, C. F., and Shih, S. M. Kinetics of the Reaction of Iron Blast Furnace Slag/Hydrated Lime Sorbents with SO2 at Low Temperatures: Effects of the Presence of CO2, O2, and NOx. Industrial & Engineering Chemistry Research, 48, 8335–8340, (2009). Liu, C. F., Shih, S. M., and Huang, T. B. Effect of SO2 on the Reaction of Calcium Hydroxide with CO2 at Low Temperatures. Industrial & Engineering Chemistry Research, 49, 9052–9057, (2010). Moorehead, D. R. Cementation by the Carbonation of Hydrated Lime. Cement and Concrete Research, 16, 700-708, (1986). Perry, R. H., and Chilton, C. H. Chemical engineers' handbook, 5th ed., New York: McGraw-Hill, (1973). Shih, S. M., Ho, C. S., Song, Y. S., and Lin, J. P. Kinetics of the Reaction of Ca(OH)2 with CO2 at Low Temperature. Industrial & Engineering Chemistry Research, 1999, 1316-1322, (1999). Shih, S. M., Ho, C. S., Liu, C. F., Chu, H. M., and Lee, C. D. Kinetics of the Sulfation of Ca(OH)2 at Low Temperatures. Industrial & Engineering Chemistry Research, 41, 3357-3364, (2002). Sing, K. S. W. et al. Reporting Physisortion Data for Gas/Soild System with Special Reference to the Determination of Surface Area and Porosity. International Union of Pure and Applied Chemistry.(IUPAC), 57, 603-619, (1985). Slack, A. V., and Hollinden. G. A. Sulfur Dioxide Removal from Waste Gases. Noyes Data Corporation. (1975). Yamamoto, M. et al. Enhancement of Ca(OH)2/Fly Ash Sorbent for the Dry-Desulfurization Process. Energy & Fuels, 20, 1901-1905, (2006). Young, J. F. Humidity Control in the Laboratory Using Salt Solutions—a Review. Journal of Applied Chemistry, 17, (1967). 陳郁文、陳航,二氧化碳之捕集及再利用技術之應用介紹,工業污染防治第94期,2005年四月。 何春松,氫氧化鈣及飛灰/氫氧化鈣與二氧化硫之反應研究,碩士論文,國立台灣大學,台北,台灣(1987) 。 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, 碩士論文,國立台灣大學,台北,台灣(1999) 。 劉瓊芳,飛灰/氫氧化鈣吸收劑吸收二氧化碳之研究, 國科會/環保署研究計畫, NSC-89-EPA-Z-002-004(2000)。 郭淑德,賴正義,劉昌民,臺電火力電廠固態副產物之資源化歷程與展望,台灣電力公司,台電工程工程月刊(1996)。 年產銷概況,台灣電力公司網站(2007)。 http://www.taipower.com.tw/left_bar/jing_ying_ji_xiao/year_production.htm 全國固定汙染源排放總量,環保署(2007)。 http://stationary.estc.tw/news.asp?xItem=1888&CtNode=529 褚文欽,鍾炳利,傳統能源的綠色革新-談火力發電機組如何減少碳排放,經濟部能源局月刊, 2012年四月刊,24-30頁。 | |
| dc.identifier.uri | http://tdr.lib.ntu.edu.tw/jspui/handle/123456789/64377 | - |
| dc.description.abstract | 本研究以微分固定床反應器,於模擬噴霧乾燥和乾式廢氣除硫系統的袋式過濾器中的條件下,探討廢氣氣體成分(CO2、O2、NOx、SO2、H2O)濃度對於氫氧化鈣(HL)以及飛灰/氫氧化鈣(FA/HL)吸收劑碳酸化反應之影響。飛灰/氫氧化鈣吸收劑經由漿化、乾燥程序製備,含有矽酸鈣等水合物,具有比原料氫氧化鈣更大的比表面積和孔隙體積。
氫氧化鈣於NOx/SO2不存在下,碳酸化轉化率隨相對溼度增加而增加,CO2和O2濃度對反應無影響。在NOx/O2與CO2同時存在時,氫氧化鈣碳酸化反應受到促進,相對濕度愈高愈為顯著,CO2濃度對反應有負面影響,NOx濃度則反之,溫度則無影響。SO2與CO2/O2/NOx同時存在下,碳酸鈣分率降低,但SO2濃度愈低(<500ppm),碳酸鈣分率愈大。 飛灰/氫氧化鈣(30/70)吸收劑於NOx/SO2不存在下,碳酸化轉化率隨相對濕度增加而增加,CO2和O2濃度對反應無影響。在NOx/O2與CO2同時存在時,促進吸收劑碳酸化之作用隨相對濕度增加而減弱,而CO2與NOx濃度則無影響。當NOx和SO2都不存在時,且在相同的碳酸化條件下,飛灰/氫氧化鈣(30/70)吸收劑的碳酸鈣分率比氫氧化鈣的高,但當NOx與O2同時存在下,兩者之碳酸鈣分率於高相對濕度下十分相近。SO2與CO2/O2/NOx同時存在下,碳酸鈣分率降低,但SO2濃度愈低(<1000ppm),飛灰/氫氧化鈣吸收劑碳酸化程度愈高。 飛灰/氫氧化鈣吸收劑於O2/NOx/SO2不存在下碳酸化,1小時碳酸鈣分率和CO2捕捉率隨其重量配比改變而變化。在重量配比為30/70時,有最大CO2捕捉率(在60oC、70% RH、12.6% CO2下,為0.253g of CO2/ g of sorbent)。然而,於CO2/O2/NOx下碳酸化,氫氧化鈣反應1小時後,有最高的CO2捕捉率(在60oC、70% RH、12.6% CO2、5% O2、600ppm NOx下,為0.379 g of CO2/ g of sorbent)。在模擬一般燃煤廢氣組成的氣體下,飛灰/氫氧化鈣吸收劑1小時SO2捕捉率皆低於氫氧化鈣的(在60oC、70% RH下,為0.534 g of SO2/ g of sorbent),且SO2捕捉率隨飛灰重量配比增加而降低。 | zh_TW |
| dc.description.abstract | A differential fixed-bed reactor was employed to study the effects of the flue gas components (CO2, O2, NOx, SO2, H2O) on the carbonation reaction of Ca(OH)2 and fly ash/Ca(OH)2 (FA/HL) sorbents under the conditions similar to those in the bag filters of spray-drying flue gas desulfurization system. The FA/HL sorbents prepared by slurrying and drying processes contained foil-like calcium silicate hydrates and had a greater surface area and pore volume than Ca(OH)2.
The carbonation of Ca(OH)2 was enhanced by relative humidity and was not affected by CO2 or O2 concentration when NOx and SO2 were not present. The carbonation of Ca(OH)2 was greatly enhanced with increasing relative humidity when NOx, O2, and CO2 were present simultaneously; in this case, relative humidity had a significant effect, temperature had a negligible effect, CO2 concentration had a negative effect, but NOx concentration had a positive effect. When SO2 was present with CO2, O2, and NOx, the fraction of calcium carbonate decreased, but it increased with decreasing SO2 concentration (<500ppm). The carbonation of FA/HL(30/70) sorbent was enhanced by relative humidity and was not affected by CO2 or O2 concentration when NOx and SO2 were not present. The carbonation of FA/HL sorbent were enhanced with decreasing relative humidity by the presence of NOx/O2 with CO2; in this case, the effect of relative humidity was less marked, and the effect of CO2 or NOx concentration was negligible. Under the same carbonation conditions, carbonation conversions for FA/HL(30/70) sorbent were much higher than those for Ca(OH)2 when NOx/SO2 were absent in the gas mixture, but were close to those for Ca(OH)2 at high relative humidities when NOx and O2 were also present. When SO2 was also present, the extent of carbonation of FA/HL(30/70) sorbent decreased, but it increased with decreasing SO2 concentration (<1000ppm). The reactivity of FA/HL sorbent varied with the FA/HL weight ratio. The sorbent with a ratio of 30/70 had the highest 1 h CO2 capture(0.253g of CO2/ g of sorbent at 60oC, 70% RH, and 12.6% CO2), when CO2 alone was present in humid N2. However, Ca(OH)2 had the highest 1 h CO2 capture(0.379g of CO2/ g of sorbent at 60oC, 70% RH, 12.6% CO2, 5% O2, and 600ppm NOx) when NOx and O2 were also present.Under gas the mixture with the typical flue gas composition, Ca(OH)2 had the highest 1 h SO2 capture(0.534 g of SO2/ g of sorbent at 60oC, and 70% RH), and the SO2 capture decreased with increasing FA/HL weight ratio. | en |
| dc.description.provenance | Made available in DSpace on 2021-06-16T17:43:43Z (GMT). No. of bitstreams: 1 ntu-101-R99524090-1.pdf: 6250511 bytes, checksum: 97b4eb9d8b67a62dc8403cdfe543f958 (MD5) Previous issue date: 2012 | en |
| dc.description.tableofcontents | 目錄索引
中文摘要 I Abstract III 符號說明 V 圖表索引 VII 第一章 緒論 1 1-1 研究緣起 1 1-2 研究目標 3 第二章 文獻回顧 4 2-1 二氧化碳捕捉與儲存 4 2-1-1 二氧化碳捕捉路徑 4 2-1-2 二氧化碳的分離與存放 6 2-2 燃煤飛灰 7 2-3 Ca(OH)2在低溫濕潤條件下吸收CO2之反應 9 2-3-1 Ca(OH)2與CO2的反應 9 2-3-2 Ca(OH)2與CO2 /O2/SO2的反應 11 2-3-3 Ca(OH)2與CO2/O2/NOx/SO2的反應 12 2-4 矽/鈣吸收劑在低溫濕潤條件下吸收CO2之反應 14 2-4-1 飛灰/ Ca(OH)2吸收劑 14 2-4-2 其他鈣/矽吸收劑 18 第三章 實驗與分析方法 21 3-1 試藥來源 21 3-2 吸收劑之製備 23 3-3 吸收劑反應實驗 26 3-3-1 反應實驗設備 26 3-3-2 反應實驗步驟 34 3-4 反應後試樣成分分析 35 3-4-1 鈣含量及氫氧化鈣、亞硫酸鈣、硫酸鈣、亞硝酸鈣、硝酸鈣莫耳分率測定 35 3-4-2 碳酸鈣與矽酸鈣等水合物莫耳分率測定 39 3-4-3 總轉化率和捕捉率測定 40 3-4-4 實驗數據誤差 44 3-5 試樣分析儀器 44 3-5-1 熱重分析(TG-DTA) 44 3-5-2 X光繞射分析(XRD) 44 3-5-3 電子顯微鏡分析(SEM) 45 3-5-4 離子層析(IC) 45 3-5-5 BET比表面積以及孔隙體積測定 46 3-5-6 粒徑分析 48 第四章 結果與討論 49 4-1 Ca(OH)2之反應 49 4-1-1 XRD分析 49 4-1-2 SEM觀察 53 4-1-3 在CO2/H2O/N2中之反應 53 4-1-4 在CO2/O2/H2O/N2中之反應 56 4-1-5 在CO2/O2/NOx/H2O/N2中之反應 56 4-1-5-1 相對溼度之影響 56 4-1-5-2 CO2濃度之影響 61 4-1-5-3 NOx濃度之影響 63 4-1-5-4 O2濃度之影響 63 4-1-5-5 反應溫度之影響 66 4-1-5-6 增長反應時間之影響 66 4-1-5-7 NOx/O2促進Ca(OH)2碳酸化之機制 69 4-1-6 在CO2/O2/NOx/SO2/H2O/N2中之反應 72 4-1-6-1 SO2濃度之影響 72 4-1-6-2 CO2和NOx濃度之影響 73 4-2 飛灰/Ca(OH)2吸收劑之反應 78 4-2-1 XRD分析 78 4-2-2 SEM觀察 82 4-2-3 結構性質 82 4-2-4 吸收劑含鈣物質分率測定 87 4-2-5 在CO2 /O2/H2O/N2中之反應 90 4-2-6 在CO2/O2/NOx/H2O/N2中之反應 93 4-2-6-1 相對溼度之影響 95 4-2-6-2 CO2濃度之影響 95 4-2-6-3 NOx濃度之影響 99 4-2-7 在CO2/O2/NOx/SO2 /H2O/N2 中之反應 102 4-2-7-1 SO2濃度之影響 102 4-2-7-2 CO2和NOx濃度之影響 103 4-2-7-3 相對溼度之影響 108 4-3 FA/HL重量配比對吸收劑反應之影響 109 4-3-1 在CO2 /H2O/N2中之反應 109 4-3-2 在CO2/O2/NOx/ H2O/N2中之反應 109 4-3-3 在CO2/O2/NOx/SO2/H2O/N2中之反應 112 第五章 結論 117 參考文獻 119 | |
| dc.language.iso | zh-TW | |
| dc.subject | 二氧化碳 | zh_TW |
| dc.subject | 煙道氣 | zh_TW |
| dc.subject | 氫氧化鈣 | zh_TW |
| dc.subject | 飛灰 | zh_TW |
| dc.subject | Flue Gas | en |
| dc.subject | Carbon Dioxide | en |
| dc.subject | Calcium Hydroxide | en |
| dc.subject | Fly ash | en |
| dc.title | 飛灰/氫氧化鈣吸收劑捕捉煙道氣中二氧化碳之研究 | zh_TW |
| dc.title | Capture of CO2 from Flue Gas by Fly Ash/Ca(OH)2 Sorbents | en |
| dc.type | Thesis | |
| dc.date.schoolyear | 100-2 | |
| dc.description.degree | 碩士 | |
| dc.contributor.oralexamcommittee | 徐振哲,林仁斌,劉瓊芳 | |
| dc.subject.keyword | 氫氧化鈣,二氧化碳,飛灰,煙道氣, | zh_TW |
| dc.subject.keyword | Calcium Hydroxide,Carbon Dioxide,Fly ash,Flue Gas, | en |
| dc.relation.page | 122 | |
| dc.rights.note | 有償授權 | |
| dc.date.accepted | 2012-08-14 | |
| 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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