§ 瀏覽學位論文書目資料
  
系統識別號 U0002-2006202014412600
DOI 10.6846/TKU.2020.00558
論文名稱(中文) 加強台灣生質能源供應管理策略之研究
論文名稱(英文) Enhancement of managerical strategy for bioenergy feedstock supply in Taiwan.
第三語言論文名稱
校院名稱 淡江大學
系所名稱(中文) 管理科學學系博士班
系所名稱(英文) Doctoral Program, Department of Management Sciences
外國學位學校名稱
外國學位學院名稱
外國學位研究所名稱
學年度 108
學期 2
出版年 109
研究生(中文) 張耿豪
研究生(英文) Keng-Hao Chang
學號 802620186
學位類別 博士
語言別 英文
第二語言別
口試日期 2020-06-12
論文頁數 119頁
口試委員 指導教授 - 婁國仁
委員 - 曹銳勤
委員 - 陳水蓮
委員 - 吳東昆
委員 - 鄭建中
關鍵字(中) 生質能
生物能源
生質酒精
林業廢棄物
稻稈
生命週期
關鍵字(英) Bioenergy
Bioethanol
Biomass
Harvest wood product
Rice Paddy
LCA
第三語言關鍵字
學科別分類
中文摘要
石化能源經過數百年的使用除了促進世界經濟的發展也導致了地球環境的污染,相對的人類對其依賴性也跟隨著使用量不斷成長不斷擴大,但其經由大自然產生要有相當的條件跟時間,所以在可預期的未來也會漸漸枯竭,綜合以上種種的狀況人類勢必積極尋找替代能源,以補足未來所產生的缺口。
台灣土地空間狹小有限,缺乏能源, 98%依賴進口,化石能源依賴度甚高,因此應充分調查台灣生產生質能源之潛力。本研究提
供了生質能源供應情境假模擬,以台灣休耕地進行稻米生產及台灣林業部門生產木材後所產生的廢棄物,進行生質能源的產出。在本研究中,計算上述兩種料源生產過程中的碳平衡情形。並估算從目前耕作地收獲後所產生的稻殼及稻稈廢棄量,及從休耕地復耕後所產生的稻殼及稻稈廢棄量。林業部門的廢棄物則包括來自木材加工廠及進口木材產品經加工後,所產生的伐後木質產品廢棄量。並從過去的消費情形推估未來50年(至2065年)內所可使用的的生質廢棄物。
生質能資源是全球最大的自然資源,可藉由直接或轉化使用生質物作為燃料產生熱、電或動力。相較於燃燒化石燃料產生之二氧化碳進入生態圈,燃燒生質燃料所產生之二氧化碳可藉由生態圈之生物固碳作用加以吸收,屬於碳中性燃料。
在本研究結果中,這些生質廢棄物製造成生質乙醇及殘餘物進行燃燒後,將可產生能源分別為222.37 PJ和206.77 PJ,相較於目前台灣2016年生質能源產量約為76.4PJ,生質能源的成長,將可大幅提高為332.56%及323.24%。從研究結果顯示台灣伐後木質產品將有相當高的生物能源利用潛力,並從綠色供應鏈及生命週期評估的角度加入循環經濟的策略,以對台灣在2025 年達到2000年排放量的水準做出貢獻。
英文摘要
Promoting biofuel to replace fossil fuels and alternative utilization schemes to replace conventional measures of biomass waste disposal have been considered a priority to mitigate CO2 emissions.  Despite fewer land resources and higher reliance on imported energy and raw material resources, the potential for bioenergy supply in a place like Taiwan should be fully investigated. This paper presents a case study regarding the utilization of waste biomass derived from an enhanced production of rice paddy and from the forest sector in Taiwan for biofuel production. In this study, the carbon balance for the two aforementioned bioenergy production scenarios was calculated. The amount of biomass waste expected to be derived from rice husk and rice straw produced from currently planted paddy and from reactivated fallow rice paddy was estimated. Forest sector wastes consist of biomass derived from processing domestically harvested and post-consumer harvested wood products. The projection was made up to 2065. The overall annual bioenergy providing potential of the biomass, estimated by this study, to replace gasoline through bioethanol production and residual combustion and to substitute coal for power generation via combustion were approximately 222.37 PJ and 206.77 PJ, respectively. These values represent 332.56 % and 323.24 % of the current level of bioenergy supplies, compared to the 76.4 PJ from biomass and waste incineration in 2016. This is the first time the bioenergy potential of post-consumer harvested wood products is being identified.
第三語言摘要
論文目次
CHAPTER 1 INTRODUCTION	1
1.1 MOTIVATION	1
1.2 SUSTAINABLE MANAGEMENT	3
1.3 CIRCULAR ECONOMY	7
1.4 HISTORY AND CURRENT SCENARIO OF RENEWABLE ENERGY IN TAIWAN	12
1.5 OBJECTIVE	19
CHAPTER 2 RESEARCH OF BIOMASS RESOURCES FROM WASTE OF RICE PADDIES AND FOREST SECTORS.	27
2.1 BIOMASS FEEDSTOCK AND SUPPLY CHAIN	27
2.2  BIOMASS FEEDSTOCK AND LCA	30
2.3 BACKGROUND	33
2.4 AGRICULTURAL AND FORESTRY WASTE IN TAIWAN	40
2.5 THE OVERVIEW OF HWP IMPORT AND EXPORT IN TAIWAN	46
2.6 HWP CARBON ESTIMATION	53
CHAPTER 3 EVALUATION OF BIOMASS FROM RICE PADDIES AND FOREST SECTORS	61
3.1 RICE PADDY WASTE	61
3.2 RICE HUSK, RICE STRAW, AND ROUGH RICE	61
3.3 BIOMASS WASTE FROM POST-CONSUMER HWP	64
3.4 DIRECT COMBUSTION	66
3.5 BIOETHANOL WITH RESIDUE FOR COMBUSTION	67
CHAPTER 4. ESTIMATION OF BIOENERGY PRODUCTION	68
4.1 RESULTS AND DISCUSSION	68
4.1.1 Biomass accumulation from forest sector wastes	71
4.1.2 CO2 emission by unmanaged incineration	76
4.2. BIOETHANOL ACCUMULATION AND RESIDUE COMBUSTION	76
4.2.1. Bioethanol from rice paddy wastes	76
4.2.2. Bioethanol from forest sector wastes	78
4.3. DIRECT COMBUSTION	81
4.3.1 Combustion of rice paddy wastes	81
4.3.2 Combustion of biomass waste from the forest sector	83
CHAPTER 5 CONCLUSION	87
5.1 MAJOR FINDING	87
5.2 IMPLICATION	89
5.3 RECOMMENDATION	91
REFERENCES	93
APPENDIX.	104
TABLE A1 AR PROJECTION OF PADDY AREA, RICE HUSK AND RICE STRAW BIOMASS IN TAIWAN	104
TABLE A2 AR PROJECTION OF BIOMASS WASTE FROM DOMESTIC LOGGING IN TAIWAN	105
TABLE A3 EXTRAPOLATION OF HWP CARBON TONNAGE PRIOR TO 1990	108
TABLE A4 EXTRAPOLATION AND PROJECTION OF SAWN WOOD CARBON STORAGE AND BIOMASS	109
TABLE A5 EXTRAPOLATION AND PROJECTION OF WOOD PANEL CARBON STORAGE AND	112
TABLE A6 EXTRAPOLATION AND PROJECTION OF PAPER CARBON STORAGE AND BIOMASS	115
TABLE A7 PROJECTION OF DECAYED BIOMASS OF HWP FROM 2017 TO 2065    	118
List of Table
Table 2-1 Historical data of rice husk and rice straw in Taiwan  42
Table 2-2 Historical data of domestic logging volume and estimation of biomass waste from self-logging in Taiwan 45
Table 2-3 Statistics of domestic produced HWP from 1990 to 2016  48
Table 2-4 Import statistics of import HWP. Thickness of plain and fancy plywood is 3.175 mm 50
Table 2-5 Export statistics of import HWP  52
Table 2-6 Biomass tonnage of import and export HWP  55
Table 2-7 Carbon conversion from HWP statistics  57
Table 2-8 Carbon inflow statistics of HWP from 2007 to 2016  59
Table 3-1 Coefficients for forest biomass calculation and estimation  63
Table 4-1 Projected annual carbon sequestration and bioenergy capacities derived from rice straw and rice husks from active and reactivated fallow rice paddy during
2017–2065 70
Table 4-2 Projected annual biomass generated from decayed domestic HWP production wastes and domestic post-consumer HWP biomass during 2017–2065 74
Table 4-3 Projected annual bioethanol and recovered bioenergy generated from rice straw and rice husks from active and re-activated fallow rice paddy during 2017–2065 75
Table 4-4 Projected annual bioethanol and recovered bioenergy generated from biomass waste of post-consumer HWP biomass and domestic HWP production wastesduring 2017–2065 80
Table 4-5 Projected annual energy harvested and carbon sequestration from combustion of waste biomass of rice straw and rice husks from active and re-activated fallow rice paddies during 2017–2065 82
Table 4-6 Projected annual energy harvested and carbon sequestration from combustionof biomass waste from the forest sector during 2017–2065 84
List of Figures
Figure 2-1 Map of Taiwan. The rice paddy areas and forest are in light gray. Legends: rice paddy (light brown); hardwood forests (dark green); temperate hardwood/softwood mixed forests (mid green); cold temperate softwood forests (mid green); sub-alpine softwood forests (yellow)  36
Figure 2-2 Framework of this study  39
Figure 4-1 Historical and AR projection for biomass generated from rice paddy wastes. Legends:Rice husk (Blue line with hollow square); rice straw (Red line with hollow circle)  69
Figure 4-2 Waste biomass generated from domestic HWP production for exponential growthscenario. Legends: Logging slash (Blue line with hollow square); log process waste(Red line with hollow circle)  73
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