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dc.contributor.advisor郭大孚zh_TW
dc.contributor.advisorTa Fu Dave Kuoen
dc.contributor.author陳冠佑zh_TW
dc.contributor.authorGuan You Chenen
dc.date.accessioned2026-02-26T17:03:41Z-
dc.date.available2026-02-27-
dc.date.copyright2026-02-26-
dc.date.issued2026-
dc.date.submitted2026-01-20-
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dc.identifier.urihttp://tdr.lib.ntu.edu.tw/jspui/handle/123456789/101728-
dc.description.abstract氣候變遷迫切的威脅與全球二氧化碳排放量的持續增加,促使各界積極尋求有效的碳移除策略,海洋與浸水型(waterlogged)環境因可吸收約30%的人為排放,被視為潛在的碳中和途徑;碳若能在儲存在系統中達100年,便被視為已完成碳封存,然而此一常用準則可能大幅高估浸水型環境的碳儲存量;此外,現有研究在評估不同浸水型生態系之碳穩定性時,缺乏統一的分析框架,限制了跨系統比較的可行性。
本研究透過一致的箱體框架(box framework)以及整合現有文獻中可取得的碳庫存與通量資料,對浸水型系統中的碳穩定性與儲存容量進行系統性的全球評估,浸水型生態系包含紅樹林、鹽沼、海草床、泥炭地、巨藻林及生物幫浦(BCP);同時,本研究亦建立一維擴散的海洋模型,以模擬海洋垂直碳傳輸並評估注入碳的長期洩漏行為。
模型模擬結果顯示,本研究可重現文獻所報導之全球尺度與區域尺度(大西洋、太平洋與印度洋)碳洩漏行為於±20%的範圍內重現注入碳回返大氣的比例誤差範圍內,且顯示在碳注入深度越深,碳洩漏速率越慢;進一步結果指出,注入的碳會隨時間逐漸返回大氣,顯示以100年作為碳封存指標可能高估實際有效碳儲存量約20–40%。在各類浸水型生態系中,超過90%的總碳輸入量並未滯留,而是快速通過系統;不同生態系之碳停留時間差異顯著,紅樹林、鹽沼、海草床與巨藻林的停留時間少於30年,而泥炭地與BCP則可達約200年;紅樹林、鹽沼、海草床與泥炭地雖具有可觀的碳儲存容量(20–130 kg C m-2),但是其碳累積速率相對緩慢(10–300 gC m-2 y-1);然而,過往研究指出,棲地流失可能迅速釋放60–80%的碳庫,進而使生態系轉變為碳源;過去文獻中預測亦顯示,海洋碳吸收受到碳酸鹽系統機制的限制,預期於本世紀末達到約 4–6 Pg C y⁻¹ 的上限,顯示海洋碳匯容量有限。
整體而言,浸水型生態系並非一種即時且高效的碳移除途徑。因此,在評估碳封存潛力時,納入完整的時間尺度至關重要,單純依賴100年的封存指標,可能會高估碳的穩定度。
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dc.description.abstractThe impending threats of climate change and the ever–growing global CO2 emission has prompted for major effective carbon removal strategies. Storage in oceans and other waterlogged environment have been suggested as a plausible carbon neutralization option as they can absorb ~30% of anthropogenic emissions. Although carbon is commonly considered as sequestered if it can remain stored/immobile for 100 years, such criterion may substantially overestimate total carbon storage in waterlogged environment. In addition, assessment of carbon stability across waterlogged ecosystems also suffer from the use of inconsistent frameworks. This study conducts a systematic global assessment on carbon stability and capacity in waterlogged systems by applying a consistent box framework to mangroves, saltmarshes, seagrass meadows, peatlands, macroalgal forests, and the biological carbon pump (BCP) integrating carbon stocks and fluxes availability in current literature. A one–dimensional diffusion–based ocean model is used to simulate vertical carbon transport and investigate long–term leakage of injected carbon. Model simulations reproduce global and basin–scale (Atlantic, Pacific, and Indian) estimates of the fraction of injected carbon returning to the atmosphere within ±20% and show slower leakage for deeper injections. These results further indicate that injected carbon gradually returns to the atmosphere, showing that the 100–year sequestration criterion likely overestimates effective carbon storage by 20–40%. Across waterlogged ecosystems, more than 90% of total carbon influx pass through the systems without being retained. Carbon retention times vary widely, from <30 years in mangroves, saltmarshes, seagrass meadows, and macroalgal forests to ~200 years in peatlands and the BCP. These ecosystems, referring to mangroves, saltmarshes, seagrass meadows, and peatlands, have substantial storage capacities (20–130 kg C m-2) but accumulate carbon slowly (10–300 gC m-2 y-1). However, these systems could become carbon sources as previous studies suggested habitat loss could release up to 60–80% of stored carbon therein. Similarly, literature simulations also projected that oceanic uptake carbon will peak at 4–6 Pg C y-1 by the end of the century dur to carbonate chemistry, indicating ocean as a finite carbon sink. Overall, waterlogged ecosystems do not represent an immediate or highly effective pathway for carbon removal, as reflected by their carbon retention times and capacities. Assessment of carbon sequestration with longer temporal scales is also warranted as the 100–year criterion can significantly overestimate carbon stability.en
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dc.description.tableofcontents致謝 I
摘要 II
Abstract IV
Contents VI
List of Figures XI
List of Tables XVII
Chapter 1 Introduction 1
1.1 Background 1
1.2 Research objectives 5
Chapter 2 Literature Review 6
2.1 Overview of the ocean carbon cycle 6
2.1.1 Carbon forms, stocks, and their reservoir distributions in the ocean 6
2.1.2 Major carbon fluxes in the ocean system 9
2.2 Review of modeling frameworks for ocean carbon leakage 12
2.2.1 Evolution of the carbon injection concept 12
2.2.2 Review of commonly used model parameters and configurations 15
2.3 Overview of waterlogged ecosystems and their carbon roles 17
2.3.1 Blue carbon ecosystems: mangroves, saltmarshes, and seagrass meadows 18
2.3.2 Peatlands 19
2.3.3 Macroalgal forests 20
2.3.4 Biological carbon pump (BCP) 21
2.3.5 Other waterlogged ecosystems 22
Chapter 3 Materials and Methods 23
3.1 Thematic Framework 23
3.2 Literature search 25
3.3 Topic–specific data collection strategy 26
3.3.1 Carbon flux, burial rate and carbon stock data 27
3.3.2 Waterlogged ecosystem areal extent and habitat loss data 28
3.3.3 Carbon cumulative leakage curve 29
3.3.4 Ocean diffusivity profile 30
3.3.5 Historical and projected data on ocean pH records 31
3.4 Waterlogged ecosystem classification 32
3.5 Box framework and assumptions 34
3.5.1 Basic box framework 34
3.5.2 Mangroves, saltmarshes, and seagrass meadows box framework 35
3.5.3 Peatlands box framework 37
3.5.4 Macroalgal forests box framework 38
3.5.5 Biological carbon pump (BCP) box framework 39
3.5.6 Ocean box framework 41
3.6 Carbon retention and storage metrics within the box framework 43
3.6.1 Flux (F), stock (S) and annual net deposition rate (ΔC) 43
3.6.2 Flux fraction (fF) and net deposition fraction (fΔC) 44
3.6.3 Carbon retention time (τ) 45
3.6.4 Synthesis of carbon retention and storage metrics 46
3.7 Dataset construction and categorization for OCLM 47
3.8 OCLM modeling process 49
3.8.1 Model structure and assumptions 50
3.8.2 Numerical discretization and time–stepping scheme 54
3.8.3 Optimization 58
3.8.4 Regional calibration 60
3.9 Uncertainty 61
3.10 Quantification of seawater buffering capacity under continuous CO₂ uptake 62
3.11 Other considerations 64
3.11.1 Data clean by trace the original literature 64
3.11.2 Gap filling with regional data 64
3.11.3 Standardization of units and formats 64
Chapter 4 Results and Discussion 66
4.1 Development and evaluation of the ocean carbon leakage model (OCLM) 66
4.1.1 Overview of cumulative leakage data 67
4.1.2 Optimal model selection and validation of OCLMglobal 71
4.1.3 Model calibration for regional carbon cumulative leakage assessment 75
4.1.4 Validation of OCLMregional 78
4.1.5 Interpretation of OCLM parameters (decay rate, k; diffusivity, Deff) 80
4.1.6 Insights of the OCLM simulation and the 100–year carbon sequestration issue 86
4.1.7 OCLM limitations 88
4.2 Overview of waterlogged ecosystem data 90
4.2.1 Variability in the global areal extent of waterlogged ecosystems 90
4.2.2 Fluxes, annual net deposition rates (ΔC), and treatment of missing terms 92
4.2.3 Carbon stocks and influence of sampling depth 97
4.2.4 Contribution of methane flux to ecosystem carbon output 101
4.3 Integrative box framework of waterlogged ecosystem carbon flow, capacity, and stability 103
4.3.1 Carbon flow structure and annual net deposition rates in waterlogged ecosystems 103
4.3.2 Carbon stock distribution and capacity limits across waterlogged ecosystems 107
4.3.3 Carbon retention time and its controlling factors across waterlogged ecosystems 111
4.3.4 Global perspective of carbon storage and loss in waterlogged ecosystems 115
4.4 Global ocean carbon balance and future constraints 119
4.4.1 Global patterns and variability of ocean carbon sedimentation fluxes (Fsed) 120
4.4.2 Variability and anthropogenic influence on global land–sea carbon fluxes (Fland–sea) 122
4.4.3 Global air–sea carbon flux (Fair–sea) and its natural and anthropogenic components 124
4.4.4 Estimation and validation of the ocean annual net carbon deposition (ΔCocean) 127
4.4.5 Feedback mechanisms limiting the future ocean carbon sink 129
Chapter 5 Suggestions and Implications 134
5.1 Limitations of carbon exported to the deep ocean as sequestration 134
5.2 Implications of ocean uptake as a form of carbon injection 134
5.3 Assessing carbon storage in waterlogged ecosystems beyond NPP 135
5.4 Strategic considerations for waterlogged ecosystems as carbon reservoirs 136
Chapter 6 Conclusions and Future works 137
6.1 Conclusions 137
6.2 Future works 139
Chapter 7 References 140
Chapter 8 Appendix 171
8.1 Guide to appendix data presentation 171
8.2 Ocean model configurations reported in the literature 172
8.3 Global ocean carbon balance 174
8.4 Ocean carbon leakage model (OCLM) 181
8.5 Waterlogged ecosystem 197
-
dc.language.isoen-
dc.subject碳封存-
dc.subject碳停留時間-
dc.subject浸水型生態系-
dc.subject薈萃分析-
dc.subject海洋碳擴散模型-
dc.subject箱型框架-
dc.subjectCarbon sequestration-
dc.subjectCarbon retention time-
dc.subjectWaterlogged ecosystem-
dc.subjectMeta–analysis-
dc.subjectOcean carbon diffusion model-
dc.subjectBox–framework-
dc.title全球生態系碳停留時間與容量之評估於 紅樹林、鹽沼、海草床、泥炭地、巨藻林與生物幫浦zh_TW
dc.titleGlobal Assessment of Carbon Retention Time and Capacity in Mangroves, Saltmarshes, Seagrass Meadows, Peatlands, Macroalgal Forests, and the Biological Carbon Pumpen
dc.typeThesis-
dc.date.schoolyear114-1-
dc.description.degree碩士-
dc.contributor.oralexamcommittee于昌平;曾鈞懋zh_TW
dc.contributor.oralexamcommitteeChang-Ping Yu;Chun-Mao Tsengen
dc.subject.keyword碳封存,碳停留時間浸水型生態系薈萃分析海洋碳擴散模型箱型框架zh_TW
dc.subject.keywordCarbon sequestration,Carbon retention timeWaterlogged ecosystemMeta–analysisOcean carbon diffusion modelBox–frameworken
dc.relation.page214-
dc.identifier.doi10.6342/NTU202600161-
dc.rights.note同意授權(全球公開)-
dc.date.accepted2026-01-21-
dc.contributor.author-college工學院-
dc.contributor.author-dept環境工程學研究所-
dc.date.embargo-lift2028-01-19-
顯示於系所單位:環境工程學研究所

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