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dc.contributor.advisor郭修伯zh_TW
dc.contributor.advisorHsiu-Po Kuoen
dc.contributor.author任威翰zh_TW
dc.contributor.authorWei-Han Jenen
dc.date.accessioned2025-02-21T16:24:31Z-
dc.date.available2025-02-22-
dc.date.copyright2025-02-21-
dc.date.issued2024-
dc.date.submitted2025-01-06-
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dc.identifier.urihttp://tdr.lib.ntu.edu.tw/jspui/handle/123456789/96755-
dc.description.abstract本研究透過實驗及計算流體力學耦合離散元素法模擬(CFD-DEM),分析多孔板式雙向流流體化床系統內部顆粒流態,並將系統應用於連續式揮發性有機物吸附。固體顆粒和揮發性有機物(Volatile organic compounds, VOCs)分別選擇瀝青基球型活性碳及甲乙酮(Methyl ethyl ketone, MEK)作為實驗材料。
流態探討中,以實驗觀察粒子於床內的滯留情況,歸類出四種形態:不成床、稀薄床、穩定床及溢流,並建立此多孔板的操作視窗(Operating window)。以CFD-DEM 模擬分析顆粒流態及掉落機制。對於顆粒流態,粒子於多孔板中心處上升,外圍處下降,具有對稱流態。對於粒子掉落機制,主要從多孔板外圍,氣體流速較慢的孔洞掉落。穩定床階段時以團聚大量掉落的 Dumping 機制為主,當由穩定床轉變為溢流後,Dumping 掉落機制逐漸衰微,改以零星碰撞方式造成粒子掉落。
連續式 VOCs 吸附中,固定 MEK 濃度 1200±100 ppm 進行研究。MEK 移除效率(MEK removal efficiency)主要與孔板上的滯留顆粒量成正相關。當固體進料速率為 0.16±0.005 kg/m2s 時,單階流化床在氣體流速 0.84 ~ 1.08 m/s 的 MEK 移除效率為 88 ~ 97%;二階流化床氣體流速為 1.00 m/s 時,移除效率可達到 99%以上。最後,活性碳經過三小時吸附後,達到約 45%的飽和吸附量,同時 MEK 出口濃度僅為入口濃度的 10%,顯示此系統應用於連續式吸附中的長時間高穩定吸附優勢。
zh_TW
dc.description.abstractThis study employs experiments and computational fluid dynamics coupled with discrete element method (CFD-DEM) to analyze particle motion within a countercurrent fluidized bed fitted with perforated plate. Additionally, the system is applied to continuous adsorption of volatile organic compounds (VOCs). For the experimental materials, asphalt-based spherical activated carbon and methyl ethyl ketone (MEK) are selected as the representative absorbent particle and VOC, respectively.
In the investigation of particle motion, the particle residence behavior within the bed was observed experimentally and categorized into four regimes: non-growth bed, dilute bed, stable bed, and flooding bed. Moreover, an operating window for the perforated plate fluidized bed system was established. CFD-DEM simulation was used to analyze the flow patterns and particle discharge mechanisms. Regarding the flow patterns, particles rise close to the center of the perforated plate and descend around the periphery, exhibiting a spouting flow pattern. As for the particle discharge mechanism, particles mainly exit through holes with lower gas velocities around the periphery of the perforated plate. During the stable bed regime, the dumping mechanism, characterized by the falling of large particle clusters, is predominant. As the system transfering from a stable bed regime to a flooding regime, the dumping mechanism gradually diminishes, and particles discharge primarily through sporadic collisions.
In the continuous VOC adsorption study, the inlet MEK concentration was fixed at 1200±100 ppm. The MEK removal efficiency was positively correlated with the amount of particles retained on the perforated plate. With a particle feed rate of 0.16±0.005 kg/m2s, the MEK removal efficiency in a single-stage fluidized bed ranged from 88% to 97% at different gas velocities ranging from 0.84 to 1.08 m/s. In a two-stage fluidized bed with a gas velocity of 1.00 m/s, the removal efficiency could be higher than 99.0%. Finally, the activated carbon reached about 45% of its saturation adsorption capacity, while the MEK outlet concentration was only 10% of the inlet concentration after three hours of adsorption test. This demonstrates the advantage of this system for long-term, highly stable continuous adsorption applications.
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dc.description.tableofcontents致謝 i
摘要 ii
Abstract iii
目次 v
圖次 ix
表次 xv
符號說明 xvi
第一章 緒論 1
第二章 文獻回顧 3
2.1 吸附總述 3
2.1.1 吸附類別 3
2.1.2 多孔材料之物理吸附 4
2.1.3 活性碳製備及種類 5
2.1.4 等溫吸附型態 7
2.1.5 等溫吸附模型 9
2.1.6 吸附動力模型 12
2.2 流體化床 15
2.2.1 Geldart 粒子分類 15
2.2.2 連續式雙向流流體化床 18
2.2.3 多孔板式雙向流流體化床操作 19
2.2.4 多孔板設計及操作視窗 24
2.2.5 流體化床應用於吸附 27
2.3 CFD-DEM 耦合 30
2.3.1 CFD-DEM 介紹及架構 30
2.3.2 CFD-DEM 耦合種類 31
2.3.3 CFD-DEM 優勢與劣勢 32
2.3.4 CFD-DEM 網格大小與固體顆粒關係 33
第三章 研究方法 36
3.1 實驗材料與裝置 36
3.1.1 吸附物 36
3.1.2 吸附材 37
3.1.3 實驗裝置 38
3.2 分析儀器 40
3.2.1 靜態雷射光繞射粒徑分析儀(Laser Diffraction Particle Size Analyzer) 40
3.2.2 比 表 面 積 與 孔 隙 分 佈 分 析 儀 (Specific Surface Area & Pore Size Distribution Analyzer by Gas Adsorption Method) 41
3.2.3 氣相層析儀(Gas Chromatography, GC) 41
3.2.4 熱重分析儀(Thermogravimetric Analysis, TGA) 43
3.2.5 掃描式電子顯微鏡(Scanning Electron Microscope, SEM) 44
3.3 流態分析實驗 45
3.3.1 最小流體化速度測量 45
3.3.2 粒子於多孔板雙向流流體化床內的滯留情形 46
3.4 VOC 吸附實驗 48
3.4.1 等溫吸附實驗 48
3.4.2 吸附動力實驗 49
3.4.3 連續式 VOC 吸附實驗 50
3.4.4 吸附量循環實驗 51
3.5 VOC 吸附實驗參數介紹 53
3.5.1 VOC 移除效率(Removal efficiency, RE) 53
3.5.2 吸附量(Adsorption capacity) 53
3.5.3 脫附活化能 53
3.7 計算流體力學與離散元素法耦合模擬 55
3.7.1 耦合計算方法 55
3.7.2 流體統御方程式 56
3.7.3 固體顆粒運動計算 58
3.7.4 流體-固體交互作用計算 60
3.7.5 幾何建構. 62
3.7.6 網格生成 65
3.7.7 參數設定 67
第四章 結果與討論 70
4.1 市售與國產活性碳之物理性質分析 70
4.1.1 粒徑分佈 70
4.1.2 孔洞結構 71
4.1.3 表面形貌 73
4.1.4 最小流體化速度 77
4.2 活性碳吸脫附結果 79
4.2.1 等溫吸附探討 79
4.2.2 吸附動力學探討 80
4.2.3 活性碳脫附再生探討 83
4.2.4 脫附速率對脫附的影響 85
4.3 雙向流式流體化床流態探討 87
4.3.1 多階雙向流式流體化床實驗流化分析 87
4.3.2 CFD-DEM 模擬流態分析 91
4.3.3 CFD-DEM 模擬與實驗及理論整合 99
4.4 連續式 VOC 吸附探討 105
4.4.1 壓降對於 VOC 吸附影響探討 105
4.4.2 階數對於連續式 VOC 吸附影響探討 108
4.4.3 不同活性碳對於 VOC 吸附影響探討 110
4.4.4 不同多孔板對於 VOC 吸附影響探討 111
4.4.5 活性碳循環次數對於 VOC 吸附影響探討 115
4.5 MEK 質量平衡探討 118
第五章 結論 120
參考文獻 122
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dc.language.isozh_TW-
dc.subject計算流體力學耦合離散元素法zh_TW
dc.subject連續式吸附zh_TW
dc.subject流體化床zh_TW
dc.subject雙向流zh_TW
dc.subject活性碳zh_TW
dc.subjectContinuous adsorptionen
dc.subjectActivated carbonen
dc.subjectCountercurrenten
dc.subjectFluidized beden
dc.subjectCFD-DEMen
dc.title多階雙向流式流體化床之CFD-DEM模擬研究及應用於連續式揮發性有機物吸附zh_TW
dc.titleA CFD-DEM Study of Continuous VOC Adsorption in a Multi-stage Countercurrent Fluidized Beden
dc.typeThesis-
dc.date.schoolyear113-1-
dc.description.degree碩士-
dc.contributor.oralexamcommittee李豪業;黃安婗zh_TW
dc.contributor.oralexamcommitteeHao-Yeh Lee;An-Ni Huangen
dc.subject.keyword活性碳,雙向流,流體化床,計算流體力學耦合離散元素法,連續式吸附,zh_TW
dc.subject.keywordActivated carbon,Countercurrent,Fluidized bed,CFD-DEM,Continuous adsorption,en
dc.relation.page127-
dc.identifier.doi10.6342/NTU202500015-
dc.rights.note未授權-
dc.date.accepted2025-01-07-
dc.contributor.author-college工學院-
dc.contributor.author-dept化學工程學系-
dc.date.embargo-liftN/A-
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