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研究生: 林育樞
Yu-Shu Lin
論文名稱: 使用鐵錳載氧體於美耐皿樹脂與RDF化學迴路燃燒
Chemical Looping Combustion of Melamine-Formaldehyde Resin and RDF using Fe/Mn Oxygen Carriers
指導教授: 顧洋
Young Ku
口試委員: 曾迪華
Dyi-Hwa Tseng
蔣本基
Pen-Chi Chiang
郭俞麟
Yu-Lin Kuo
學位類別: 碩士
Master
系所名稱: 工程學院 - 化學工程系
Department of Chemical Engineering
論文出版年: 2021
畢業學年度: 109
語文別: 英文
論文頁數: 170
中文關鍵詞: 化學迴路燃燒鐵錳載氧體三聚氰胺甲醛樹脂垃圾衍生燃料
外文關鍵詞: chemical looping combustion, iron-manganese oxygen carriers, melamine-formaldehyde resin, refuse derived fuel
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化學迴路程序具有多種優勢,例如減少燃料中氮元素氧化所產生之NOx以及提高二氧化碳在廢氣中的濃度。而化學迴路釋氧程序是一種在高溫下以載氧體產生之氧氣燃燒固體廢棄物的新興技術。本研究利用熱重分析儀(TGA)分析載氧體的鐵錳重量比、粒徑大小及鍛燒溫度對反應性和循環性的影響,在Fe2O3和Mn2O3以重量比3:1混合,並篩選粒徑大小為2毫米的顆粒以900 ℃之空氣環境中鍛燒2小時之條件製備時,鐵錳載氧體具有較佳的效能,其中,摻入氧化錳是改善循環性的關鍵。以X光繞射儀(XRD)、掃描電子顯微鏡(SEM)和能量分散式光譜儀(EDS)分析反應過程中鐵錳載氧體的晶體結構與表面形態之變化。檢測結果顯示反應前之鐵錳載氧體由Fe2O3和FeMnO3組成,表面多有利於增進質傳的細小分支與不規則孔洞,而隨著還原程度增加,晶體結構逐漸轉變成Fe與MnO且表面有些微的燒結現象發生。以TGA紀錄瞬時之重量變化與氣固反應模型計算,鐵錳載氧體以氫氣還原符合一階孔擴散反應機制,經線性回歸得表觀活化能為17.06 kJ/mole。進行化學迴路燃燒程序前,探討了三聚氰胺甲醛樹脂(MF resin)為主成分之廢棄塑膠製品和以廢棄木造建材與漂流木製成之垃圾衍生燃料(RDF)在不同升溫速率之熱裂解行為並計算在各轉化率下之活化能,結果顯示提高升溫速率對熱裂解速率有顯著的正面效果,但也會使DTG之峰值延後,並以Flynn-Wall-Ozawa模型預測兩燃料之轉化率較為適合。本研究以固定床反應器進行化學迴路燃燒程序實驗,研究鐵錳載氧體與燃料之重量比和反應溫度對煙氣組成的影響。以煙氣組成分析儀紀錄瞬時的煙氣濃度變化,結果顯示提高載氧體與燃料之重量比和反應溫度都可以促進燃燒效率。本研究對鐵錳載氧體的合成比例、鐵錳載氧體的還原模型、MF resin與RDF之熱裂解行為與各轉化率下之活化能以及化學迴路燃燒MF resin與RDF之操作參數對煙氣組成的影響。


Chemical looping process (CLP) has exceptional performance such as reducing NOx production due to oxidation of fuel-N and increasing CO2 concentration in exhaust gases. Chemical looping with oxygen uncoupling (CLOU) is one of CLP technology that could burn the solid waste with gaseous oxygen at elevated temperature. In this study, the reactivity and recyclability of iron-manganese oxygen carriers in various compositions, particle sizes, and calcination temperatures were evaluated by thermogravimetric analyzer. Considering the reactivity and recyclability, oxygen carriers containing 75 % iron oxide in particle size 2.00 mm calcined at 900 ℃ is suitable for CLOU process. The presence of manganese oxide is the key to enhances the recyclability of oxygen carriers. The crystal structure and surface morphology of oxygen carriers before and after the reaction was analyzed by X-ray diffraction (XRD), scanning electron microscope (SEM), and energy-dispersive X-ray spectroscopy (EDS), respectively. XRD patterns showed the composition of fresh oxygen carriers was mixed by Fe2O3 and FeMnO3 then reduced to Fe and MnO gradually. The surface of fresh oxygen carriers showed small branches and irregular pores which were beneficial to the mass transfer, however, the sintering phenomenon happened was observed in SEM images after the reaction. The reduction kinetics was discussed under hydrogen atmosphere and proposed based on the gas-solid model. The regression analysis showed that reduction of oxygen carriers could be modeled by first order pore diffusion model and the apparent activation energy is 17.06 kJ/mole. This work involved two types of solid fuels used in CLOU process. One is the waste plastic made out of melamine-formaldehyde (MF) resin which is a thermosetting polymer and the other is refuse derived fuel (RDF) mainly made from agricultural and forestry residues, wood waste.
The pyrolysis behavior at various heating rate was investigated by TGA and the activation energy at each extent of conversion was estimated by iso-conversional method as well. A higher heating rate increased the maximum DTG value, but also delayed the peak. For both MF resin and RDF used in this work, the Flynn–Wall–Ozawa model was more suitable for prediction of activation energy at each extent of conversion in the pyrolysis process. The experiments for CLOU were conducted in a fixed-bed reactor. The effect of operating conditions, including oxygen carriers to fuel ratios and reaction temperatures on the composition of exhaust gas was explored. The results indicated that combustion efficiency has improved when both oxygen carriers to fuel ratio and reaction temperature increased. This work evaluated parameters for synthesis of iron-manganese oxygen carriers, the reduction model of oxygen carriers, pyrolysis behavior at various heating rate and activation energy at each extent of conversion of MF resin and RDF, and effect of operation parameters for chemical looping combustion of MF resin and RDF in a fixed-bed reactor on the exhaust gas composition.

中文摘要 I Abstract III Acknowledgements V Table of Contents VII List of Figures XI List of Tables XIX List of Symbols XXI Chapter 1 Introduction 1 1.1 Background 1 1.2 Objective and Scope 3 Chapter 2 Literature and Review 5 2.1 Introduction of Chemical Looping Process 5 2.1.1 Chemical Looping Combustion 5 2.1.2 NOx Formation in Chemical Looping Combustion 8 2.2 Application of Solid Waste in Chemical Looping Process 12 2.2.1 Pyrolysis of Melamine-Formaldehyde Resin 12 2.2.2 Melamine-Formaldehyde Resin for Chemical Looping Process 18 2.2.3 Pyrolysis of Refuse Derived Fuel 24 2.2.4 Refuse Derived Fuel for Chemical Looping Process 26 2.3 Preparation and Performance of Iron-Based Oxygen Carriers 30 2.3.1 Development of Oxygen Carriers 31 2.3.2 Calcination Temperature of Oxygen Carriers 35 2.3.3 Particle Size of Oxygen Carriers 37 2.4 Reaction Kinetic Models for Chemical Looping Process 41 2.4.1 General Gas-Solid Reaction Model 41 2.4.2 Reduction Kinetic Models of Iron-Manganese Oxygen Carriers 45 2.4.3 Activation Parameter based on Iso-Conversional Methods 46 Chapter 3 Materials and Experiments 51 3.1 Materials 51 3.2 Apparatus and Instruments 52 3.3 Experimental Procedures 52 3.3.1 Experimental Framework 52 3.3.2 Preparation and Characterization of Oxygen Carriers 55 3.3.3 Performance of Iron-Manganese Oxygen Carriers 56 3.3.4 Analysis of Fuels 58 Chapter 4 Results and Discussion 63 4.1 Performance of Iron-Manganese Oxygen Carriers 63 4.1.1 Reactivity of Iron-Manganese Oxygen Carriers 63 4.1.2 Redox Recyclability of Iron-Manganese Oxygen Carriers 83 4.1.3 Characterization of Iron-Manganese Oxygen Carriers 89 4.1.4 Reduction Mechanism of FM31 Oxygen Carriers 95 4.1.5 Kinetic Models for Reduction of FM31 Oxygen Carriers 98 4.2 Combustion of MF Resin using FM31 Oxygen Carriers 102 4.2.1 Pyrolysis Behavior of MF Resin at Various Heating Rates 102 4.2.2 Activation Energy for Thermal Pyrolysis of MF Resin 104 4.2.3 Effect of Oxygen Carriers to Fuel Ratio on Combustion of MF Resin in a Fixed-bed Reactor 109 4.2.4 Effect of Operation Temperature on Combustion of MF Resin in a Fixed-bed Reactor 114 4.3 Combustion of RDF using FM31 Oxygen Carriers 117 4.3.1 Pyrolysis Behavior of RDF at Various Heating Rates 117 4.3.2 Activation Energy for Thermal Pyrolysis of RDF 119 4.3.3 Effect of Oxygen Carriers to Fuel Ratio on Combustion of RDF in a Fixed-bed Reactor 124 4.3.4 Effect of Operation Temperature on Combustion of RDF in a Fixed-bed Reactor 126 Chapter 5 Conclusions and Recommendations 129 Reference 133

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