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研究生:Lamtiur Junita Bancin
研究生(外文):Lamtiur Junita Bancin
論文名稱:Beaches as Sentinels for Ocean Plastic Pollution: Microplastic and Mesoplastic Pollution on Xia-Liao Beach, New Taipei City, Taiwan
論文名稱(外文):Beaches as Sentinels for Ocean Plastic Pollution: Microplastic and Mesoplastic Pollution on Xia-Liao Beach, New Taipei City, Taiwan
指導教授:Dr. Bruno Andreas Walther
指導教授(外文):Dr. Bruno Andreas Walther
學位類別:碩士
校院名稱:臺北醫學大學
系所名稱:全球衛生暨發展碩士學位學程
學門:醫藥衛生學門
學類:公共衛生學類
論文種類:學術論文
論文出版年:2018
畢業學年度:106
語文別:英文
中文關鍵詞:MicroplasticsMesoplasticsPlastic pollutionTaiwanese beachcoastal pollutionplastic waste.
外文關鍵詞:MicroplasticsMesoplasticsPlastic pollutionTaiwanese beachcoastal pollutionplastic waste.
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Background: Microplastisc and mesoplastic particles of ocean plastic pollution are now scattered from the Arctic to the Antarctic. Each year, more than 8 million of plastic ends up in the oceans, damaging marine wildlife, fisheries, and tourism, and costing at least $8 billion in damage to marine ecosystems. The degradation of ecosystems also entails major health-related consequences. Those particles in marine ecosystems may not be biodegradable, as they can sink to the ocean floor. In 2016, Taiwan generated 7461342 tons of municipal solid waste of which some might be ending up in the ocean. Taiwanese people rely heavily on oceanic food sources as fishery production was up to 1256082 MMT in 2012. It is crucial to study microplastic pollution in Taiwan because it affects both this oceanic food source and also the coastal environments used for recreation. However, still comparatively little research has been conducted in Taiwan.
Methods: The study was conducted by sampling on the Xia Liao beach sand in New Taipei City, Taiwan with systematically sampling from dune to intertidal and doing extraction for the microplastics and mesoplastics by density separation and visual separation using Greenough Stereo microscope and polymer type analysis.
Results: 1939 microplastics and mesoplastics from the 0.25 m2 or equal with 485 particles per m2 and weight 71.44 gram recovered with fragment (59.1%), followed by Styrofoam (27.3%), pellets (11.2%), fishing lines (1.3%), plastic foils (0.9%), and fibers (0.2%) , white color (64.1%), secondary particles (88.8%), transect 1 had the most particles (51%), backshore (42.2%), there were significant differences between the number of microplastics and mesoplastics between the four transects (p=0.002) and four zones (p=0.013) which significant correlation between backshore and supralittoral (p=0.013), backshore and intertidal (p=0.015); significant differences between size categories across four transects (p=0.000) and four zones (p=0.015); significant differences between shape categories across four transects and four zones (p=0.000); significant correlation between the number of particles and transect 1 (0.012); significant correlation between the number of particles and weight (p=0.000).
Conclusions: My study found that there was huge heterogeneity among 1939 particles revered across four transects and four zones. Microplastics and mesoplastics are abundant which had large heterogeneity among the 80 samples which is an important result because my study is the first one to show such variation. Therefore, researchers should focus on (1) repeating a similarly designed study to see if this heterogeneity is a general pattern or not and (2) trying to investigate the physical factors which produce this heterogeneity.

Keywords: Microplastics, Mesoplastics, Plastic pollution, Taiwanese beach, coastal pollution, plastic waste.
Background: Microplastisc and mesoplastic particles of ocean plastic pollution are now scattered from the Arctic to the Antarctic. Each year, more than 8 million of plastic ends up in the oceans, damaging marine wildlife, fisheries, and tourism, and costing at least $8 billion in damage to marine ecosystems. The degradation of ecosystems also entails major health-related consequences. Those particles in marine ecosystems may not be biodegradable, as they can sink to the ocean floor. In 2016, Taiwan generated 7461342 tons of municipal solid waste of which some might be ending up in the ocean. Taiwanese people rely heavily on oceanic food sources as fishery production was up to 1256082 MMT in 2012. It is crucial to study microplastic pollution in Taiwan because it affects both this oceanic food source and also the coastal environments used for recreation. However, still comparatively little research has been conducted in Taiwan.
Methods: The study was conducted by sampling on the Xia Liao beach sand in New Taipei City, Taiwan with systematically sampling from dune to intertidal and doing extraction for the microplastics and mesoplastics by density separation and visual separation using Greenough Stereo microscope and polymer type analysis.
Results: 1939 microplastics and mesoplastics from the 0.25 m2 or equal with 485 particles per m2 and weight 71.44 gram recovered with fragment (59.1%), followed by Styrofoam (27.3%), pellets (11.2%), fishing lines (1.3%), plastic foils (0.9%), and fibers (0.2%) , white color (64.1%), secondary particles (88.8%), transect 1 had the most particles (51%), backshore (42.2%), there were significant differences between the number of microplastics and mesoplastics between the four transects (p=0.002) and four zones (p=0.013) which significant correlation between backshore and supralittoral (p=0.013), backshore and intertidal (p=0.015); significant differences between size categories across four transects (p=0.000) and four zones (p=0.015); significant differences between shape categories across four transects and four zones (p=0.000); significant correlation between the number of particles and transect 1 (0.012); significant correlation between the number of particles and weight (p=0.000).
Conclusions: My study found that there was huge heterogeneity among 1939 particles revered across four transects and four zones. Microplastics and mesoplastics are abundant which had large heterogeneity among the 80 samples which is an important result because my study is the first one to show such variation. Therefore, researchers should focus on (1) repeating a similarly designed study to see if this heterogeneity is a general pattern or not and (2) trying to investigate the physical factors which produce this heterogeneity.

Keywords: Microplastics, Mesoplastics, Plastic pollution, Taiwanese beach, coastal pollution, plastic waste.
Abstract i
Acknowledgements iii
List of tables vi
List of figures vii
CHAPTER 1 INTRODUCTION 1
1.1 Background 1
1.2 Statement of problem: Microplastic pollution in Taiwan 3
1.3 Study objectives 4
1.4 Significance of the study 4
1.5 Organization of the thesis 4
CHAPTER 2 LITERATURE REVIEW 6
2.1 Definition and the origin of microplastics and mesoplastics 6
2.2 Characteristics 6
2.3.1 Marine life impact 8
2.3.2 Potential human health impact 8
CHAPTER 3 MATERIALS AND METHODS 10
3.1 Study area 10
3.2 Data collection technique 12
3.2.1 Sampling 12
3.2.2 Extraction of microplastics and mesoplastics 16
3.2.2.1 Washing and drying 16
3.2.2.2 Density separation with NaCl solution 16
3.2.2.3 Recovery test for NaCl solution 16
3.2.2.4 Hydrogen Chloride (HCl) test 17
3.2.2.5 Visual counting 17
3.2.2.6 Fourier Transform Infrared (FTIR) spectroscopy 19
3.2.2.7 Raman spectroscopy 20
3.3 Statistical analysis 20
3.3.1 Data categories 20
3.3.2 Data analyses 22
CHAPTER 4 RESULTS 23
4.1 Characteristics and numbers of microplastics and mesoplastics 23
4.2 Spatial distribution and variation 24
4.3 Polymer type of particles 26
CHAPTER 5 DISCUSSION 37
5.1 Discussion 37
5.1.1 Microplastics and mesoplastics recovered 37
5.1.2 Polymer types of microplastics and mesoplastics 39
5.1.3 Differences of the number of microplastics and mesoplastics among the transect and zones 39
5.1.4 Correlations between the number of microplastics and mesoplastics and the distance to the dune for all the transect 40
5.1.5 The difference between shape and size among transects and zones 40
5.1.6 Regression of the number of microplastics and mesoplastics and weight 41
5.2 Study limitation 41
CHAPTER 6 CONCLUSION 43
6.1 Conclusions 43
6.2 Possible future study 43
6.3 Implications 43
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