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研究生: 馬莉絲
Anifah, Eka Masrifatus
論文名稱: 應用淨水汙泥產製蒸壓養護氣泡混凝土之研究
Recycling water treatment plant sludge as an alternative raw material in autoclaved aerated concrete production
指導教授: 張祖恩
Chang, Juu-En
學位類別: 碩士
Master
系所名稱: 工學院 - 環境工程學系
Department of Environmental Engineering
論文出版年: 2013
畢業學年度: 101
語文別: 英文
論文頁數: 140
外文關鍵詞: autoclaved aerated concrete, tobermorite, waste recycling, water treatment plant sludge
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    The issue on the disposal of water treatment plant (WTP) sludge has been raised in recent years. Recycling technology has been considered as an alternative method to solve the disposal problem. The purpose of this study was to investigate the feasibility of recycling WTP sludge as an alternative raw material in AAC production. Mechanical, physical and mineralogical analyses were performed to determine the influence of WTP sludge replacement on the AAC products. Different water-to-solid ratios were studied to examine the performance of WTP sludge-containing AAC. Pre-treatments of WTP sludge with the calcination processes were examined to improve the final properties of AAC product.

    The experimental results showed WTP sludge had a high moisture content of 65.7wt.% and a LOI of 16.5wt.%. The main chemical compositions of WTP sludge were SiO2, Al2O3, and Fe2O3. WTP sludge contains some phases, such as quartz, hematite and albite. It was observed that WTP sludge contained high amount of organic matters.

    The addition of WTP sludge was shown favorable to the tobermorite formation. The tobermorite formation can be enhanced if the C/S ratio was adjusted because tobermorite formation was very sensitive to the C/S ratio. The compressive strength development in AAC product was shown mainly due to the formation of tobermorite and filling of the formed tobermorite in space between raw materials. The replacement ratios of WTP sludge at 5-25% was favorable to compressive strength development. However excessive replacement ratios of WTP sludge inhibited the tobermorite formation thus having significant effects on the reduction of compressive strength.

    The experimental results showed that NaOH(aq) had significant effects to decrease the compressive strength of AAC. The addition of alkali in the form of NaOH(aq)caused significant reduction in density and compressive strengths of AAC due to the less dense microstructures. Neutralization reactions by Na ions caused higher volume expansion and swelling hydration products. In a high alkali concentration, similar minerals patterns were formed. However, less pore formed and non-uniform hydration products were found, which caused the reduction in compressive strength. Hydrogarnet was formed phase in AAC with Al/(Si+Al) ratio higher than 0.04. The amount of hydrogarnet increased with increasing of Al/(Si+Al) ratio. The hydrogarnet formation in AAC specimens leads to decreasing of the density followed by reducing the compressive strength.

    Lastly, the strength developments in AAC products depend on the density of AAC, the formation of tobermorite and filling of the formed tobermorite in space between particles of AAC specimens. The results showed that The WTP sludge can substitute primary raw materials for AAC production. It is suggested that recycling WTP sludge for production of AAC can reduce consumption of natural resources thus solve the problem of waste disposal.

    The calcination process at temperature 900°C for 30 minutes is recommended to reduce organic matters in WTP sludge and to transform silica into amorphous silica that lead to the increase silica reactivity. Activator of Na2CO3 was effective in the transformation into amorphous silica. However, the additions of Na2CO3 tend to increasing Na+ concentration in WTP sludge ashes. Using WTP sludge ash in the AAC production can obtain lighter products, which also have the higher compressive strength. The highest performance factor value was obtained due to the increase of formed tobermorite and the enhancements pore filling degree.

    Table of Contents Abstract I Acknowledgment IV Table of Contents V List of Figures VIII List of Tables XIV Notations XV Chapter 1 Introduction 1 1.1 Research Background 1 1.2 Goal and Objective 2 Chapter 2 Literature Review 5 2.1 Waste Production in Water Treatment Plant 5 2.2 Autoclaved Aerated Concrete and Properties 8 2.2.1 Autoclaved aerated concrete 8 2.2.2 Autoclaved aerated concrete chemistry 11 2.2.3 Hydrothermal treatment/autoclaving 17 2.2.4Autoclaved aerated concrete properties 24 2.2.5 Environmental challenges of AAC production 27 2.3 Reuse of Waste as Alternative Raw Materials for AAC Production 28 2.4 Reuse of WTP Sludge in AAC Production 29 2.5 Quantitative and Qualitative Analysis 30 2.5.1 Physical properties analysis density 30 2.5.2 Thermal analysis 32 2.5.3 X-ray diffraction (XRD) 33 2.4.3 Microstructure analysis 35 2.6 Summary 38 Chapter 3 Experimental Methodology 39 3.1 Research Profile 39 3.2 Material and Apparatus 41 3.2.1 Materials 41 3.2.2 Reagents 41 3.2.3 Apparatus 42 3.3 Experimental Methods 43 3.3.1 Preparation of raw materials 43 3.3.2 Preparation of AAC raw mixes 44 3.3.3 Production of AAC 47 3.4 Analysis 47 3.4.1 Solubility test of silica and aluminum 47 3.4.2 Mechanical properties 47 3.4.3 Mineralogy phase 47 3.4.4 Thermal analysis 48 3.4.5 Mercury intrusion porosimetry 48 3.4.6Particle size distribution by light scattering analysis 48 Chapter 4 Results and Discussion 51 4.1 Characterization of WTP Sludge 51 4.1.1 Approximate analysis and chemical 51 4.1.2 Thermal analysis, mineralogy, and particle size distribution 56 4.1.3 Summary 61 4.2 Production of AAC from WTP Sludge 62 4.2.1 Influence of WTP sludge replacement ratio 62 4.2.2 Influence of reaction liquids 78 4.2.3 Influence of Al2O3 (aluminum oxide) 91 4.2.3 Summary 100 4.3 Production of AAC from WTP Sludge Ashes 101 4.3.1 Characteristics of WTP sludge ashes 101 4.3.2 Influence of WTP sludge ashes replacement 114 4.3.3 Influence of W/S ratio 123 4.3.4 Summary 132 Chapter 5 Conclusions and Suggestions 133 5.1 Conclusions 133 5.2 Suggestions 134 References 135

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