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請用此 Handle URI 來引用此文件: http://tdr.lib.ntu.edu.tw/jspui/handle/123456789/46551
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dc.contributor.advisor於幼華
dc.contributor.authorYen-Ling Liuen
dc.contributor.author劉宴伶zh_TW
dc.date.accessioned2021-06-15T05:15:08Z-
dc.date.available2011-07-23
dc.date.copyright2010-07-23
dc.date.issued2010
dc.date.submitted2010-07-21
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dc.identifier.urihttp://tdr.lib.ntu.edu.tw/jspui/handle/123456789/46551-
dc.description.abstract本研究主要處理半導體與薄膜電晶體液晶顯示器(TFT-LCD)產業所排放之銅製程廢水,其廢水含高濃度銅離子約5000 mg/L,但於製造過程中因常使用到強螯合劑EDTA用以控制銅離子濃度,導致廢水中含大量螯合銅而難以利用傳統氫氧化法予以沉澱處理,因此,本研究欲找出有效處理效率且符合經濟效益之處理含EDTA銅製程廢水方法,目標將銅離子濃度去除至1 mg/L以下。
本研究利用單一理化方法,包括Fenton氧化法、銅-鋁置換法與硫化鈉添加法,得到最佳銅離子去除率可達99 %以上,但最低銅離子濃度僅為1.8 mg/L。考量其去除效率與經濟效益後,決定以同時添加鋁片及硫化鈉之結合性理化方法,找出最佳操作條件為控制反應pH值為13、每單位克重銅添加0.5 g 60% Na2S與1.0 g 0.4 cm* 0.4 cm鋁片,於反應60分鐘後,可將溶液中銅離子濃度降至1 mg/L以下。另外,改變此股廢水之主要成分(H2O2、NH4+、NO3-、PO43-、Al3+)其濃度介於0~2500 mg/L間,結果顯示氨氮對處理之影響性最大,鋁離子濃度則影響最小,不過,結合性理化方法皆可於60分鐘內,將其銅離子濃度去除1 mg/L以下,表示此法之操作空間頗廣大。
最後,處理後之固體物主要分為兩種含銅化合物,一係具回收價值之金屬銅沉積物,另一為硫化銅汙泥,可利用臭氧將後者氧化為工業常用之硫酸銅;此外,上澄液因含大量鋁離子與EDTA,似可供為混凝劑之用途。總而言之,由本研究所設計之處理程序未來應極具實用前景。
zh_TW
dc.description.abstractCopper processing wastewater discharged by the semiconductor and the thin transistor liquid crystal display(TFT-LCD)industries is mainly treated in this study, and the wastewater contains high concentration of copper ion which is about 5000 mg/L. In order to control the concentration of copper ion, a strong chelating agent ethylenediaminetetraacetic acid (EDTA) is usually used in the manufacturing process, and it leads to the result that the wastewater containing amounts of chelating copper is treated hardly by traditional hydroxide method. Therefore, it is necessary to find out an effective and economical method to treat the copper processing wastewater containing EDTA, and the main objective is treating the copper ion to be less than 1 mg/L.
First, this topic uses single physicochemical methods, including Fenton oxidation, copper - aluminum cementation and sodium sulfide addition method, to remove above 99% copper ion. Still, the minimum concentration of copper ion is 1.8mg/L, which does not achieve the target concentration. Considering about the copper ion removal rate and economic efficiency, the combined physicochemical method that add aluminum and sodium sulfide simultaneously is decided to use. And the best operating conditions are followings: keeping pH 13, adding 0.5 g 60% Na2S and 0.4 cm*0.4 cm 1.0 g aluminum sheets per gram of copper ion and reacting 60 minutes, and the concentration of copper ion can be removed under 1 mg/L.
In addition, the concentration of the main characteristics(H2O2、NH4+、NO3-、PO43-、Al3+) in this wastewater is changed between 0~2500 mg/L, and the results appear that the influential of ammonia nitrogen is the most and of aluminum ion is the least. Nevertheless, the concentration of copper ion can be treated below 1 mg/L after 60 min by using combined physicochemical method, so it appears that the operational flexibility of this method is quite large.
Finally, the produced solid includes two kinds of copper compound, one is the copper deposits with recovery value, and the other is CuS sludge which could be oxidized to industrial usable CuSO4 by ozone. And the supernatant can probably be as coagulant because of its component containing amounts of aluminum ion and EDTA. According to the results discussed above, this treatment process is feasible for treating the copper processing wastewater.
en
dc.description.provenanceMade available in DSpace on 2021-06-15T05:15:08Z (GMT). No. of bitstreams: 1
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Previous issue date: 2010
en
dc.description.tableofcontents口試委員會審定書 II
誌謝 III
中文摘要 IV
英文摘要 V
目錄 VI
圖目錄 IX
表目錄 XII
第一章 緒論 1
1.1 前言 1
1.2 研究目的、範圍與內容 1
第二章 文獻回顧 3
2.1 銅製程廢水 3
2.1.1 廢水來源 3
2.1.2 廢水特性 4
2.2 Fenton法與Fenton-like反應 9
2.2.1 Fenton氧化法原理 9
2.2.2 Fenton-like反應 12
2.3 金屬置換程序 16
2.3.1金屬置換法之簡介 16
2.3.2以鋁做置換反應之機制 16
2.4 硫化物沉澱法 18
2.4.1 硫化物反應機制 18
2.4.2重金屬汙泥處理 19
第三章 實驗設備與方法 23
3.1 實驗系統簡介 23
3.2 實驗設計與操作流程 25
3.2.1 Fenton 氧化法 25
3.2.2 鋁片置換試驗 26
3.2.3 硫化鈉添加試驗 26
3.2.4 結合性理化方法試驗 26
3.2.5 廢水特性評估試驗 27
3.2.6 再回用性試驗 27
3.3 實驗設備與分析方法 29
3.3.1 實驗儀器與藥品 29
3.3.2 分析方法 30
第四章 實驗結果與討論 32
4.1 銅製程廢水特性分析 32
4.2 單階段理化處理 35
4.2.1 Fenton 氧化法 35
4.2.2 以鋁為犧牲金屬做置換 41
4.2.3 硫化鈉添加試驗 50
4.2.4 小結 57
4.3 結合性理化處理 59
4.3.1 可行性評估-同時添加硫化鈉與鋁片 60
4.3.2 廢水特性影響評估 69
4.3.3 小結 83
4.4 金屬回收與上澄液再利用 84
4.4.1 硫化銅汙泥處理試驗 84
4.4.2 上澄液再利用試驗 88
4.4.3 經濟效益分析 89
4.4.4 小結 96
第五章 結論與建議 97
5.1 結論 97
5.2 建議 99
參考文獻 100
附錄 103
dc.language.isozh-TW
dc.subject銅-鋁置換zh_TW
dc.subjectEDTAzh_TW
dc.subject銅製程廢水zh_TW
dc.subject硫化鈉zh_TW
dc.subjectCu-Al cementationen
dc.subjectNaSen
dc.subjectcopper processing wastewateren
dc.subjectEDTAen
dc.title含EDTA銅製程廢水之處理研究zh_TW
dc.titleA Study on the Treatment of the Copper Processing Wastewater Containing EDTAen
dc.typeThesis
dc.date.schoolyear98-2
dc.description.degree碩士
dc.contributor.oralexamcommittee駱尚廉,謝奇旭
dc.subject.keywordEDTA,銅製程廢水,銅-鋁置換,硫化鈉,zh_TW
dc.subject.keywordEDTA,copper processing wastewater,Cu-Al cementation,NaS,en
dc.relation.page106
dc.rights.note有償授權
dc.date.accepted2010-07-22
dc.contributor.author-college工學院zh_TW
dc.contributor.author-dept環境工程學研究所zh_TW
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