臺灣博碩士論文加值系統

Taipei Dome (TD) is under construction and located in the heart of Taipei City. It is surrounded by prominent shopping district and popular cultural centers. The capacity of TD is 40,575 seats. Songshan Cultural and Creative Park is within the same block as TD and has retained the remaining green area within the block. Once it is in operation, the impact of the subsequent vehicular and crowd noise to the nearby buildings and green area is inevitable. To understand the nearby soundscape of TD, an itinerary with 8 locations were used. In-situ visual/aural observation with video recording were performed in 4 different time periods during one weekday and one weekend. A list of taxonomy of sounds was derived. While vehicular noise is the dominant sound category, natural sound such as bird chirping and insect calling were also identified. Traffic counts were conducted. Scooters and cars were the two main vehicular types and with peak volumes during weekday evenings. Sound pressure level of each location was measured. Maximum peak sound pressure level of car noise reached as high as 109.5 dB. Mitigating expected vehicular noise and enhancing natural sound around TD should be considered by its design team.

Taipei Dome (TD) is under construction and located in the heart of Taipei City. It is surrounded by prominent shopping district and popular cultural centers. The capacity of TD is 40,575 seats. Songshan Cultural and Creative Park is within the same block as TD and has retained the remaining green area within the block. Once it is in operation, the impact of the subsequent vehicular and crowd noise to the nearby buildings and green area is inevitable. To understand the nearby soundscape of TD, an itinerary with 8 locations were used. In-situ visual/aural observation with video recording were performed in 4 different time periods during one weekday and one weekend. A list of taxonomy of sounds was derived. While vehicular noise is the dominant sound category, natural sound such as bird chirping and insect calling were also identified. Traffic counts were conducted. Scooters and cars were the two main vehicular types and with peak volumes during weekday evenings. Sound pressure level of each location was measured. Maximum peak sound pressure level of car noise reached as high as 109.5 dB. Mitigating expected vehicular noise and enhancing natural sound around TD should be considered by its design team.

TABLE OF CONTENTS
ACKNOWLEDGEMENTS 4
TABLE OF CONTENTS 5
LIST OF TABLES 7
LIST OF FIGURES 8
LIST OF EQUATIONS 13
ABSTRACT 14
INTRODUCTION 15
LITERATURE REVIEW 18
2.1 Soundscape approach and use for planning and design application 18
2.2 Simulation in city noise 20
2.3 The relationship between noise and street and building facades 23
2.4 Problem of traffic noise and risk of health 24
2.5 About Taiwan noise law standards 26
METHODS 30
3.1 Measurement Positions 30
3.2 Measurement equipment and setup 36
3.3 Cadna-A modeling and setting 41
DATA ANALYSES AND RESULTS 45
4.1 Taxonomy of sound sources 45
4.2 Vehicular volume and the corresponding LAeq 48
4.2.1 Position A 48
4.2.2 Position B 50
4.2.3 Position C 52
4.2.4 Position D 54
4.2.5 Position E 56
4.2.6 Position F 58
4.2.7 Position G 60
4.2.8 Position H 62
4.2.9 Summary of all Positions 64
4.3 Cadna-A outdoor noise predicting simulations 64
4.3.1 Existing condition of TD 65
4.3.2 Future operation condition of TD 67
CONCLUSION 72
5.1 Conclusion 72
5.2 Future study 73
APPENDIX A 74
APPENDIX B 79
APPENDIX C 80
APPENDIX D 96
REFERENCE LISTS 103
BIOGRAPHICAL SKETCH 106

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