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作者:Long Pham
作者(英文):Long Pham
論文名稱:Ecological Risk Assessment of Using Taiwan's Municipal Solid Waste Incineration Bottom Ash in Concrete Tetrapods
論文名稱(英文):Ecological Risk Assessment of Using Taiwan's Municipal Solid Waste Incineration Bottom Ash in Concrete Tetrapods
指導教授:蘇銘千
指導教授(英文):Ming-Chien Su
口試委員:施文真
高年信
江漢全
蘇銘千
口試委員(英文):Wen-Chen Shih
Nien-Hsin Kao
Hann-Chyuan Chiang
Ming-Chien Su
學位類別:碩士
校院名稱:國立東華大學
系所名稱:自然資源與環境學系
學號:610354039
出版年(民國):107
畢業學年度:106
語文別:英文
論文頁數:78
關鍵詞(英文):municipal solid waste incinerationbottom ashconcretetetrapodrisk assessmentheavy metals
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This study looks into a theoretical scenario where tetrapods were produced with various percentages of municipal solid waste incineration bottom ash used as aggregate replacement. The incineration of municipal wastes is not a permanent solution for waste management. Therefore, the use of bottom ash in tetrapod productions offers another method for disposal or recycling of bottom ash, while also adding other benefits such as the reduction of natural resource usage (gravel). Some considerations were necessary to completely run and analyze the scenarios at an overestimation or a worst case scenario for the risk assessment. There were four bottom ash replacement scenarios tested with bottom ash data from four different cities in Taiwan and a scenario where the regulated toxicity characteristic leaching procedure (TCLP) limit would be used as the bottom ash data: 30%, 50%, 60%, and 70% replacement with Yilan, Keelung, Taipei, New Taipei, and TCLP limit bottom ash data. The different cities were chosen to represent big and small cities in Taiwan while also being close to the northeast coast, which could benefit from tetrapod usage. The heavy metals of interest for this study are lead, cadmium, chromium, and copper because they were the most commonly tested metals for TCLP. The results of the scenarios were assessed with Taiwan’s sediment quality guidelines (SQGs) and Hakanson’s methods. Both methods showed chromium to be the lowest in all cities and replacement percentages while cadmium was shown to have the highest impacts of all the metals in this study. Overall, the heavy metal’s ecological impacts in the study would be in the order of cadmium > copper > lead > chromium. Based on the results, future studies could consider focusing on reducing cadmium concentrations in bottom ash by way of additional steps in the pretreatment of bottom ash.
ACKNOWLEDGEMENTS i
ABSTRACT iii
TABLE OF CONTENTS v
LIST OF FIGURES vii
LIST OF TABLES ix
1. INTRODUCTION 1
1.1. Introduction 1
1.2. Motivation 1
1.3. Assumptions in the Study 2
1.4. Research Questions and Objectives 3
2. LITERATURE REVIEW 7
2.1. Bottom Ash Regulation in Taiwan 7
2.2. Bottom Ash Composition and Comparison 7
2.3. Bottom Ash Reuse 11
2.4. Use of Bottom Ash in Concrete Production 14
2.5. Leaching of Heavy Metals from Concrete 16
2.6. Environmental Impacts in Concrete Industry 17
3. METHODOLOGY 19
3.1. Data collection 19
3.2. Statistical Analysis of Data 20
3.3. Tetrapod 20
3.4. Tetrapod Calculations 21
3.4.1. Tetrapod Volume Calculations 21
3.4.2. Tetrapod Compression Strength 22
3.4.3. TCLP Data to Bottom Ash Conversion 23
3.4.4. Tetrapod Erosion Calculations 26
3.5. Risk Assessment Calculations 27
3.5.1. Sediment Quality Guidelines 27
3.5.2. Contamination Factor Calculation 28
3.5.3. Potential Ecological Risk Factor Calculations 29
4. RESULTS AND DISCUSSION 31
4.1. TCLP Data Analysis 31
4.2. Tetrapod Calculation Results 35
4.2.1. Tetrapod Scenarios 35
4.2.2. TCLP Data to Bottom Ash Conversion Results 36
4.2.3. Tetrapod Erosion Results 37
4.3. Sediment Quality Guideline Assessment 38
4.4. Sediment Quality Guideline Scenario Summary 44
4.5. Environmental Quality Assessment 45
4.5.1. Bottom Ash Replacement Scenario Contamination Factor 46
4.5.2. Bottom Ash Replacement Scenario Contamination Factor Summary 51
4.5.3. Bottom Ash Replacement Scenario Ecological Risk Factor 51
4.5.4. Ecological Risk Factor Summary 56
4.5.5. Ecological Risk Index 57
4.6. Comparison of Assessment Methods 59
4.7. Benefits from the Application of Bottom Ash in Tetrapod Production 60
5. CONCLUSION AND SUGGESTIONS 63
5.1. Conclusion 63
5.2. Suggestions 65
REFERENCES 69
APPENDIX 75
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