環境資源報告成果查詢系統

97年度廢棄物資源化技術暨附加價值提升研究計畫

中文摘要 依據實地訪視國內上、中、下游太陽能產業,完成調查由相關產業事業機構。本計畫運用物質流分析方法,2007年太陽能電池經由進口方式進入台灣共124,856 kg/y,而業者自行生產製造太陽能電池共782,456 kg/y,其中10%之製造量主要以內銷為主,內銷與國外進口量合計共201,146 kg/y將投入台灣太陽板組裝廠;2007年太陽能板經由進口方式進入台灣共47,868 kg/y,業者自行組裝製造太陽能板共4,779,646 kg/y,其扣除當年廢棄量與出口量,則合計約3,998,295 kg/y之太陽能板流動於國內市場中。而依據物質流佈推估結果得知2007年國內太陽能電池與太陽能板之廢棄量分別約為19,561 kg/y與191,186 kg/y。 太陽能電池經由人工拆解、鹼洗及酸溶的回收流程處理後,回收之矽晶純度可達99.7%。太陽能電池經由人工拆解後,包含有機部分(PMMA 51.56~60.18%,EVA 31.68~32.22%)與無機部分(金屬 1.6~4.39%,矽晶5.85~11.82%)。太陽能電池中矽晶上網印之金屬線比重約為6.31~10.6%。導線之成分為銅:9.75 %、銀:10.93%、鋁:79.32 %,EVA經過TGA測試後發現持溫400℃一小時後,重量損失為42.15%,之後即使持溫加熱8小時重量亦無明顯變化。使用氯仿作為溶劑處理,發現經過三小時後EVA之溶解度超過70%,PMMA之溶解度為100%。經過鹼洗得過後,矽晶片上的導線回收率達34.5%,最後利用酸溶將其餘之金屬進一步回收。針對銀進行酸溶實驗後,得到最佳之操作參數為:固液比為0.2g/100mL 、王水濃度為10% ,反應溫度為室溫。最終回收之矽晶純度為99.1~99.7%。 本計畫依顯示器產業鏈之上、中、下游供貨與加工關係,完成調查由顯示器產業相關事業機構,現行環保署事業廢棄物管制系統內並無「廢液晶顯示面板」專用之廢棄物申報代碼,目前各事業單位產出之廢棄代碼複雜,如LCD廢棄模組以E-0218申報,廢棄面板則以D-0499申報,且皆全數送往掩埋處理。2007年LCD面板具資源化潛力成分於台灣儲存於使用者端之重量為玻璃12933公噸、塑膠2130公噸、液晶19.7公噸、銦錫氧化物(ITO)共29公噸,而由面板製造廠排出之廢棄LCD面板與經回收拆解程序拆解之廢棄面板,經調查可知其全數送往掩埋場掩埋,2007年進入掩埋場之可資源化物質總量分別為玻璃6721.3公噸、塑膠1146.6公噸、液晶0.1公噸、銦錫氧化物(ITO)0.2公噸。 顯示器回收技術部分主要是針對廢液晶顯示器(Liquid crystal display, LCD)中之玻璃基板、偏光膜、彩色濾光片、銦金屬及液晶等材料進行回收分離處理,本研究係將所收集之廢LCD面板經由不同之方法包括:(1)酒精超音波震盪;(2)高溫灼燒;(3)液態氮浸泡;(4)破碎研磨;(5)單軸抗壓壓碎;(6)雙輪滾壓;(7)溶劑浸漬溶蝕等來進行再生處理。根據本研究結果顯示廢LCD面板中含有約0.03%的銦,比重為1.99 g/cm3,水份達0.39%,灰份達78.43%,另玻璃基板約佔廢LCD 面板重量之76.95%,偏光膜與保護膠片約佔廢LCD 面板重量之21.63%,而液晶則約佔面板重量達0.92%。另根據研究成果得知,將初步碎裂後之LCD面板經溶劑浸漬溶蝕後可同時將廢LCD面板中之液晶、偏光膜、彩色濾光片與玻璃基板完全分離,並可將銦金屬100%溶蝕回收。
中文關鍵字 太陽能電池, 太陽能板, 顯示器, 廢棄物資源化

基本資訊

專案計畫編號 EPA-97-U1H1-02-101 經費年度 097 計畫經費 5500 千元
專案開始日期 2008/04/02 專案結束日期 2009/04/01 專案主持人 張添晉
主辦單位 廢管處 承辦人 李長平 執行單位 國立台北科技大學

成果下載

類型 檔名 檔案大小 說明
期末報告 97期末定稿.zip 181MB [期末報告]公開完整版

A Study of Waste-to-Resource Technologies and the Enhancement of Value Addition Project

英文摘要 According to the on-site investigation to the upstream, midstream and downstream of the domestic solar power industry, this project has investigated interrelated institutions. According to material flow analysis, the import of Solar Cells was 124,856 kg/y in 2007. The Solar Cells in Taiwan were 782,456 kg/y, and 10% of which was sold domestically. Consequently, 201,146 kg/y of Solar Panels assembly plants have put to Taiwan in 2007. The imported Solar Panels were 47,868 kg/y in 2007 and the self-assembled Solar Panels were 4,779,646 kg/y. Deducting from the waste and export volume in 2007, there were totally 3,998,295 kg/y of Solar Panels circulated in domestic market. Based on material flow estimated in 2007, it shows that domestic Solar Cells and Solar Panels wastes were about 19,561 kg/y and 191,186 kg/y, respectively. Silicon solar cells can be recycled to obtain high purity silicon (99.17%) by a recycling process consisting of dissembling, caustic treatment and acid leaching. After dissembling, the silicon solar cell contains organic material (PMMA 51.56~60.18%, EVA 31.68~32.22%) and inorganic material (metal 1.6~4.39%, silicon 5.85~11.82%). For silicon wafer with connecting wire pattern, the metal content is about 6.31~10.6% with 9.75% of copper, 10.93% of silver and 79.32% of aluminum, respectively. From TGA analysis, it was found that after one hour heating at 400 ℃, the weight loss reached 42.15%, and no further weight loss was observed for further heating up to 8 hours, For solvent treatment process, the chloroform solubility experiments showed that after three hours of chloroform soaking, more than 70% of EVA, and 100% of PMMA can be dissolved. For caustic treatment, 34.5% connecting wire can be recovered. After acid pickling, the remained metal component can be further recovered. The optimum operating parameters for silver metal are: solid-liquid ratio of 0.2g/100 ml, a concentration of 10% aqua regia in the room temperature. The final purity of thus treated single crystal silicon can reach as high as 99.1~99.7% purity. Meanwhile, based on the point of material flow analysis of LCD panels in Taiwan, the LCD flow between input and output in 2007 has been inventoried. Totally 12,933 tons of glasses, 2,130 tons of plastic, 19.7 tons liquid crystal and 29 tons of ITO had been stored in Taiwan. The waste panels from the LCD manufacturer have all gone to landfill. In other words, there are 6721.3 tons of glasses, 1146.6 tons of plastic, 0.1 tons liquid crystal and 0.2 tons of ITO potentially. The main purpose of this project is to separate and recover the components of glass substrate, polarizing film, color filter, liquid crystal and indium from scrap LCD panel. Various methods of (1) supersonic washing by ethyl alcohol; (2) high temperature roasting; (3) liquid nitrogen soaking; (4) grinding; (5) pressing by normal pressure; (6) pressing by roll crusher; (7) leaching are adopted to treat the collected scrap LCD panel were carry out in this study. The result of this study reveals that the collected scrap LCD panel has a density of 1.99 g/cm3, a water content of 0.39% and an ash content of 78.43%. It also reveals that the LCD panel contains 0.03% indium, 76.95% glass substrate, 21.63% polarizing film and 0.92% liquid crystal. Among the testing methods, the leaching method was the best method which could 100% separated the liquid crystal, polarizing film, color filter and indium from glass substrate.
英文關鍵字 Liquid Crystal Display, Solar Panel, Waste-to-Resource