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請用此 Handle URI 來引用此文件: http://tdr.lib.ntu.edu.tw/jspui/handle/123456789/86697
完整後設資料紀錄
DC 欄位值語言
dc.contributor.advisor馬鴻文(Hwong-Wen Ma)
dc.contributor.authorYung-Hui Luen
dc.contributor.author呂詠惠zh_TW
dc.date.accessioned2023-03-20T00:11:57Z-
dc.date.copyright2022-08-10
dc.date.issued2022
dc.date.submitted2022-08-01
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Prospects for the recycling of plastics in the United States. Structural Change and Economic Dynamics, 9(3), 307-331. EC. (2015). Proposal for a Directive of the European Parliament and of the Council amending Directive 94/62/EC on packaging and packaging waste. European Commission. EMF. (2020). New plastics economy global commitment (commitments, vision and definitions). Ellen MacArthur Foundation, Retrieved from: https://emf.thirdlight.com/link/pq2algvgnv1n-uitck8/@/preview/1?o Eriksen, M. K., Pivnenko, K., Faraca, G., Boldrin, A., & Astrup, T. F. (2020). Dynamic material flow analysis of PET, PE, and PP flows in Europe: evaluation of the potential for circular economy. Environmental science & technology, 54(24), 16166-16175. European Commission. (2022). Communication from the commission to the european parliament, the council, the european economic and social committee and the committee of the regions - EU strategy for sustainable and circular textiles. 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Proceedings of the National Academy of Sciences of the United States of America, 117(33), 19844-19853. doi:10.1073/pnas.2001379117 Netherlands Enterprise Agency. (2012). GD142-Duurzame-inzameling-textiel. Retrieved from: https://www.greendeals.nl/green-deals/duurzame-inzameling-textiel Netherlands Enterprise Agency. (2013). Productie Bioplastics uit Groente-, Fruit- en Tuinafval. Retrieved from: https://www.greendeals.nl/green-deals/productie-bioplastics-uit-groente-fruit-en-tuinafval Netherlands Enterprise Agency. (2020). C-232 GREEN DEAL Reliable evidence for applications of plastic recyclate. Retrieved from: https://www.greendeals.nl/green-deals/green-deal-betrouwbaar-bewijs-voor-toepassen-van-kunststof-recyclaat Netherlands Enterprise Agency. (2021a). Green Deal. Retrieved from: https://www.greendeals.nl/ Netherlands Enterprise Agency. (2021b). Green Deal Kunststof Recyclaat goed op weg. Retrieved from: https://www.greendeals.nl/nieuws/green-deal-kunststof-recyclaat-goed-op-weg Plastics Europe. (2020). Plastics - the Facts 2020. An analysis of European plastics production, demand and waste data. Retrieved from: https://plasticseurope.org/knowledge-hub/plastics-the-facts-2020/ Plastics Europe. (2022). collection & sorting. Retrieved from: https://plasticseurope.org/sustainability/circularity/waste-management-prevention/collection-sorting/ Shen, L., Worrell, E., & Patel, M. K. (2010). Open-loop recycling: A LCA case study of PET bottle-to-fibre recycling. Resources, Conservation and Recycling, 55(1), 34-52. Strassert, G. (2001). Physical input-output accounting. In A handbook of industrial ecology, edited by R. Ayres and L. Ayres. Cheltenham, UK: Elgar. Textile Exchange. (2021a). Preferred Fiber & Materials Market Report 2021. Retrieved from: https://textileexchange.org/wp-content/uploads/2021/08/Textile-Exchange_Preferred-Fiber-and-Materials-Market-Report_2021.pdf Textile Exchange. (2021b). Textile Exchange and Fashion Industry Charter for Climate Action launch the 2025 Recycled Polyester Challenge, a joint industry initiative. Retrieved from: https://textileexchange.org/wp-content/uploads/2021/05/News-Release-Textile-Exchange-Leads-on-rPET-Challenge-with-UNFCCC.pdf UNEP. (2019). Our planet is choking on plastic pollution. Retrieved from: https://www.unep.org/interactives/beat-plastic-pollution/ United States Environmental Protection Agency. (2016). The Social Cost of Carbon. Retrieved from: https://19january2017snapshot.epa.gov/climatechange/social-cost-carbon_.html Van Der Voet, E., Heijungs, R., Mulder, P., Huele, R., Kleijn, R., & Van Oers, L. (1995). Substance flows through the economy and environment of a region. Environmental Science and Pollution Research, 2(3), 137-144. Van Eygen, E., Laner, D., & Fellner, J. (2018). Circular economy of plastic packaging: Current practice and perspectives in Austria. Waste management, 72, 55-64. Xanthos, D., & Walker, T. R. (2017). International policies to reduce plastic marine pollution from single-use plastics (plastic bags and microbeads): A review. Marine Pollution Bulletin, 118(1-2), 17-26. doi:10.1016/j.marpolbul.2017.02.048 王塗發、楊浩彥、林幸君、賴金端(2020)。投入產出分析:理論與實務。台灣經濟研究院。 大愛感恩科技(2017),CSR企業社會責任報告書。檢自:http://www.daait.com/ebook/2017CSR/files/2017csr.pdf 行政院主計總處(2020a)。105年產業關聯表。 行政院主計總處(2020b)。產業關聯統計編製報告(民國105年)。 行政院主計總處(2021)。資源回收稽核認證量。檢自:https://data.gov.tw/dataset/9762 行政院環境保護署(2006)。免洗餐具限制使用對象及實施方式。檢自:https://oaout.epa.gov.tw/law/LawContent.aspx?id=GL006481 行政院環境保護署(2011)。一次用外帶飲料杯源頭減量及回收獎勵金實施方式。檢自:https://oaout.epa.gov.tw/law/LawContent.aspx?id=GL006479 行政院環境保護署(2012)。101年度產品碳足跡資訊揭露服務專案工作計畫。 行政院環境保護署(2014)。103年度產品碳足跡資訊揭露服務專案工作計畫。 行政院環境保護署(2015)。廢棄物及再生資源代碼表。 行政院環境保護署(2017)。限制含塑膠微粒之化粧品與個人清潔用品製造、輸入及販賣。檢自:https://oaout.epa.gov.tw/law/LawContent.aspx?id=GL006976 行政院環境保護署(2018)。紡織品回收再利用專案工作計畫。 行政院環境保護署(2019a)。推動塑膠資源循環經濟模式專案工作計畫-期末報告(正式報告)。 行政院環境保護署(2019b)。一次用塑膠吸管限制使用對象及實施方式。檢自:https://oaout.epa.gov.tw/law/LawContent.aspx?id=GL007530 行政院環境保護署(2019c)。推動紡織品資源循環再利用專案工作計畫。 行政院環境保護署(2020a)。擴大推動塑膠資源循環經濟模式專案工作計畫-期末報告(正式報告)。 行政院環境保護署(2020b)。109年度補助應回收廢棄物回收處理創新及研究發展計畫-廢塑膠容器再生類別規則與驗證制度建置研究期末報告書。 行政院環境保護署(2021a)。資源循環分析系統。檢自: https://smmdb.epa.gov.tw/SMM/WebPage/enter.aspx?v=LF 行政院環境保護署(2021b)。產品碳足跡資訊網。檢自: https://cfp-calculate.tw/cfpc/WebPage/LoginPage.aspx 行政院環境保護署廢管處(2021)。事業廢棄物管理策略。檢自:https://www.epa.gov.tw/Page/544AD7DFE4B1AECA 材料世界網(2020)。全球PET回收技術之發展趨勢。檢自:https://www.materialsnet.com.tw/DocView.aspx?id=45264 財政部南區國稅局(2005)。94年度成衣業之製造業原物料耗用通常水準調查報告。 財政部南區國稅局(2011)。100年度飲料品業之製造業原物料耗用通常水準調查報告。 財政部南區國稅局(2014)。103年度紡織業之製造業原物料耗用通常水準調查報告。 財政部南區國稅局(2016)。105年度人造纖維業之製造業原物料耗用通常水準調查報告。 財政部南區國稅局(2017)。106年度塑膠及其加工業之製造業原物料耗用通常水準調查報告。 財政部關務署(2021)。統計資料庫查詢系統。檢自:https://portal.sw.nat.gov.tw/APGA/GA30 財團法人中華民國紡織業拓展會(2018)。可將聚酯廢料轉化為原生PET的新製程。檢自:http://monitor.textiles.org.tw/newsdetail.aspx?id=29391 財團法人台灣產業服務基金會(2011)。應回收容器列管範圍與課費制度規劃專案工作計畫。 許哲綾(2012)。再生紡織業供應商選擇行為之研究。國立交通大學。 經濟部統計處(2016)。經濟部工業產品分類(第16次修訂)。 經濟部統計處(2018)。工業生產量值與附加價值分配(基期:中華民國105年)。 經濟部統計處(2021)。工業產銷存動態調查產品資料庫。檢自: https://dmz26.moea.gov.tw/GMWeb/investigate/InvestigateDA.aspx 萬海航運股份有限公司(2022)。點對點查詢。檢自: https://tw.wanhai.com/views/skd/SkdByPort.xhtml?file_num=64835&parent_id=64834&top_file_num=64735
dc.identifier.urihttp://tdr.lib.ntu.edu.tw/jspui/handle/123456789/86697-
dc.description.abstract塑膠在全球的使用量與日俱增,不同國家主要生產的塑膠種類都不相同,以台灣為例,生產量最大的塑膠原料為本研究的目標對象-「聚酯粒」。為有效管理塑膠原料以減緩塑膠垃圾問題,各國訂定許多塑膠管理策略,我國亦引進荷蘭的Green Deal來推動塑膠循環經濟聯盟,目前我國已成立「塑膠容器循環經濟聯盟」與「台灣紡織資源循環聯盟」,期望整合聯盟內的合作對象,使再生料更大量使用於相關的塑膠產品。 然而這兩個聯盟當前皆處於小規模的試驗階段,為評估二者在全國規模下的實施效果,並聚焦於聚酯產品進行討論,本研究將二者改以「再生塑膠容器聯盟」及「再生聚酯纖維聯盟」來呈現,首先改良IO-MFN 模型(Input-Output Material Flow Networks Model),考量包含進口廢塑膠容器(polyethylene terephthalate,PET)及擴增國內再生料來源(廢布、廢纖維、舊衣)的五種策略,並以該模型進行聚酯粒和再生聚酯料的物質流分析。 結果顯示改良後的IO-MFN模型可以透過產業關聯表(IO表)直接連動聚酯粒及再生聚酯料的物質流桑基圖,在最節省盤查時間的情況下進行不同策略的物質流分析。在策略評估上,除了整併各個策略的策略5之外,代表廢塑膠容器(PET)進口的策略1最能有效提升我國整體的再生聚酯料總量,創造更多的產值以及碳排放減量效益。 然而若是將廢布、廢纖維產生業者以及舊衣回收業者一同納入聯盟合作對象,則塑膠容器與聚酯纖維的再生料含量將更為提升。因此雖然本研究充分展現了廢塑膠容器(PET)進口做為再生聚酯料原料的優勢,但更佳的選擇是採取策略5的方式,將有潛力的各方合作對象進行整合,以達到最佳的效果。zh_TW
dc.description.abstractThe use of plastics is expanding worldwide, and the plastics produced in different countries also vary in its substance used. This research addresses the most produced material used in plastics found in Taiwan - “polyester chip”. Upon high usage of plastics, strategies have been developed by different countries to manage and mitigate plastic waste problems effectively. Green Deal, a covenant from the Netherlands, is currently introduced to Taiwan with a goal to promote a circular economy initiative for plastics. At present, Taiwan has established the Plastic Container Circular Economy Initiative and the Taiwan Circular Textile Initiative as a team to promote the use of recycled materials in plastic products. These two initiatives, however, are still in a small-scale experimental stage. Hence, to evaluate the effect of implementing both initiatives on a national scale with a focus on polyester products, the two initiatives could then be modified as Recycled Plastic Container Initiative and Recycled Fiber Initiative. Essentially, improvements were made to the IO-MFN model. These improvements were made with imported waste of plastic containers (polyethylene terephthalate, PET) and the expansion of domestic recycled material sources (waste cloth, waste fiber, old clothes) as its main consideration. Altogether, five strategies were developed, and the model was used to analyze the material flow of polyester chips and recycled polyester materials caused by each of these strategies. The obtained results showed that the improved IO-MFN model, through the medium of Input-Output tables, could be directly linked to the polyester chip, regenerating a change in the sankey flow diagram. By the same token, it also enables the material flow analysis of different strategies to be carried out in the least amount of time. In terms of strategy evaluation, in addition to Strategy 5, Strategy 1, which is known for its representation in regard to import waste of plastic containers (PET), has the highest effectiveness in increasing the total volume of recycled polyester materials in Taiwan, creating more production value and reducing carbon emissions. The recycled content of plastic containers and polyester fibers, however, would be even higher if waste cloth, waste fiber producers, and used clothes recyclers were included in the initiatives. Although this study demonstrates the advantages of importing waste plastic containers (PET) as a raw material for recycled polyester, adopting Strategy 5 approach and integrating all potential partners could be a better option to achieve the best results.en
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dc.description.tableofcontents誌謝 i 中文摘要 ii Abstract iii 圖目錄 vii 表目錄 viii 第一章 緒論 1 1.1 研究緣起 1 1.2 研究目的與架構 2 第二章 文獻回顧 4 2.1 全球塑膠產業現況 4 2.1.1 全球塑膠流向與生產量 4 2.1.2 全球塑膠管理策略 6 2.1.3 自發性合作協議-荷蘭Green Deal 8 2.2 台灣聚酯產業現況 11 2.2.1 台灣聚酯粒流向與生產量 11 2.2.2 台灣塑膠管理策略 18 2.3 塑膠策略評估方法 22 2.4 聚酯產品的環境影響 27 第三章 材料與方法 29 3.1 方法架構 29 3.2投入產出分析 31 3.2.1投入產出分析沿革與概念 31 3.2.2投入產出分析方法 33 3.3 物質流分析 37 3.3.1 物質流分析沿革與概念 37 3.3.2 物質流分析方法 40 3.4 策略說明 45 3.5 策略評估指標說明 50 第四章 結果與討論 53 4.1 物質流分析結果 53 4.2 策略對再生料占比之影響 60 4.3 策略對經濟產生之影響 68 4.4 策略對環境產生之影響 73 第五章 結論與建議 83 5.1 結論 83 5.2 建議 85 參考文獻 87
dc.language.isozh-TW
dc.subject塑膠容器zh_TW
dc.subject聚酯纖維zh_TW
dc.subject聚酯粒zh_TW
dc.subject塑膠容器zh_TW
dc.subject物質流zh_TW
dc.subject投入產出分析zh_TW
dc.subject聚酯粒zh_TW
dc.subject循環經濟聯盟zh_TW
dc.subject循環經濟聯盟zh_TW
dc.subject聚酯纖維zh_TW
dc.subject投入產出分析zh_TW
dc.subject物質流zh_TW
dc.subjectPolyester Fiberen
dc.subjectPolyester Chipen
dc.subjectPlastic Containeren
dc.subjectMaterial Flowen
dc.subjectInput-Output Analysisen
dc.subjectCircular Economy Initiativeen
dc.subjectPolyester Chipen
dc.subjectPolyester Fiberen
dc.subjectPlastic Containeren
dc.subjectMaterial Flowen
dc.subjectInput-Output Analysisen
dc.subjectCircular Economy Initiativeen
dc.title以IO-MFN模型評估聚酯產品聯盟對經濟與環境之影響zh_TW
dc.titleMeasuring the efficacy of Polyester Product Initiatives on Economy and Environment with IO-MFN Modelen
dc.typeThesis
dc.date.schoolyear110-2
dc.description.degree碩士
dc.contributor.oralexamcommittee李公哲(Kung-Cheh Li),陳起鳳(Chi-Feng Chen)
dc.subject.keyword聚酯粒,聚酯纖維,塑膠容器,物質流,投入產出分析,循環經濟聯盟,zh_TW
dc.subject.keywordPolyester Chip,Polyester Fiber,Plastic Container,Material Flow,Input-Output Analysis,Circular Economy Initiative,en
dc.relation.page94
dc.identifier.doi10.6342/NTU202201901
dc.rights.note同意授權(全球公開)
dc.date.accepted2022-08-02
dc.contributor.author-college工學院zh_TW
dc.contributor.author-dept環境工程學研究所zh_TW
dc.date.embargo-lift2022-08-10-
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