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研究生:馬進吉
研究生(外文):Chin-Chi Ma
論文名稱:定影廢液銀回收及COD之去除
論文名稱(外文):Recovery Silver and Removal COD of Waste Fixers
指導教授:方鴻源方鴻源引用關係
學位類別:碩士
校院名稱:國立雲林科技大學
系所名稱:環境與安全工程系碩士班
學門:工程學門
學類:環境工程學類
論文種類:學術論文
論文出版年:2006
畢業學年度:94
語文別:中文
論文頁數:108
中文關鍵詞:銀回收電解法電解氧化法蒸餾濃縮化學沈澱法COD
外文關鍵詞:Silver RecoveryCODChemical sedimentElectrolysis oxidationDistillation thickenerElectrolysis
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本研究以電解回收法瞭解廢定影液中回收金屬銀之可行性,以低電流電解在電流為0.1A、0.3A、0.5A、0.7A及0.9A下,於8小時電解後,其銀回收效率分別為10.57%、11.75%、45.5%、62.68%、83.88%,以0.9A電解8小時其銀之回收效率為83.88%較其他電流電解佳,電解0.9A且pH值控制於3、4、5、原液(pH=6.09)、7、8、9及10於8小時後其銀回收效率分別為96.04%、84.66%、81.54%、83.88%、99.09%、100%、98.63%及81.20%,由數據得知電解0.9A在pH為8時其電解銀回收率約為100%,故可知以0.9A電解其銀回收效率在pH=8時最佳。而高電流電解於3A電解6小時後得知電解3.5小時銀之回收效率已達98.64%,若電解至6小時時其銀回收效率反而下降至96.36%,因此選定最適電解時間為3.5小時;控制pH值為8且電解2.5小時則結果發現其電解時間不但減少1小時且電解銀之回收效率可由98.64%提升至99.55%。若將兩者比較之下可得知其兩者回收效率相差不大,若以時間為考量則以電解3A具有較佳之處理效能。
而銀回收後之廢定影液仍含高濃度COD,實驗取銀回收後之定影廢液1000mL加入30mL硫酸為較佳前處理,其COD去除效率為42%,再進行8A電解6小時COD濃度可降解至32,054.80mg/L,其去除效率為35%,若將前處理後之定影廢液調整不同pH值時與電解8A之處理效能差異不大,但於經濟效益的考量下則以電解氧化法較為適當。
  另未經前處理後之定影廢液直接以蒸餾濃縮的方式處理COD時,則COD去除效率為99.3%,但濃縮部分之委託代處理收費高,需更進一步瞭解較適當的處理技術;而化學沈澱方面亦取未經前處理之定影廢液取100mL直接加入含鈣物質則以添加30g氯化鈣對COD的降解有較佳的情形,COD去除效率僅達25.82%,但其去除效率不高且添加的藥量甚多較不符合經濟效益。
This study’s focus is on the recovery of silver from the spent fixer by electrolysis. Electric currents of 0.1A, 0.3A, 0.5A, 0.7A, 0.9A were applied for 8 hours. Examination showed that after electrolysis the silver recovery efficiencies are 10.57%, 11.75%, 45.5%, 62.68% and 83.88% respectively. The results show that the most efficient recovery of silver was with an electric current of 0.9A electrolysis for 8 hours, and when the spent fixer was with adjusted pH values of 3, 4, 5, 6.09, 7, 8, 9 and 10. It was found that at pH 8, with an electrolytic time of 8 hours and electric current of 0.9A the silver recovery was up to 100%. Our results also showed that with an electric current of 3A the recovery efficiency of silver was 98.64% in 3.5 hours, and if the electrolytic time was 6 hours, the efficiency of silver recovery will decrease to 96.36%. When the electrolytic time is 2.5 hours and with an electric current of 3A that was found the silver recovery increased to 99.55%, at pH8. Both comparison, under similar efficiency of silver recovery, it is considered the time the better treatment method is electrolysis with 3A.
Spent fixer still has high concentrations of COD after electrolysis, and the 1000mL waste fixer after silver recovery adds 30mL sulphuric acid, the COD removal efficiency is 42%. When 8A oxidation electrolysis is applied for 6 hours, the COD of fixer will decrease to 32,054.80mg/L, the COD removal efficiency is 35%. The adjust different pH values and the 8A electrolysis oxidation, both comparison, under similar efficiency of COD removal, the COD treatment assessment of economic benefits it shows that at 8A electrolysis oxidation will be good choice.
When the non-pretreated spent fixer is treated by distillation thickener to remove COD, the COD removal efficiency is 99.3%. But the thick parts product sludge need to contract the commission deal with high treatment cost. Thus, further study on proper treatment methods still needs to be done. hence it still need to study further proper treatment method. In chemical sediment, we were taken non-pretreated the spent fixer 100mL and add 30g calcium chloride, our results show that the best COD degrading efficiency has a removal efficiency of 25.82%. Still, it is not economical because the COD removal wastes large amounts of chemicals.
中文摘要 I
英文摘要 III
誌  謝 V
圖 目 錄 IX
表 目 錄 XI
一、緒論 1
1.1 研究背景 1
1.2 研究目的 2
二、文獻回顧 3
2.1 照相廢液之基本性質 3
2.2 銀之基本特性 11
2.3 照相沖印之流程及原理 12
2.4 含銀廢液之回收處理方法 15
2.4.1 電解回收 15
2.4.2 化學沈澱法 15
2.4.3 離子交換法 16
2.4.4 金屬置換 16
2.5 金屬電解析出原理 18
2.6 電解氧化法 20
2.6.1 電解直接氧化 20
2.6.2 電解間接氧化 20
2.6.3 電解氧化影響因子 21
2.7 照相沖印廢水處理 23
2.7.1 生物法處理 23
2.7.2 電化學法 26
2.8 FENTON 法對有機物之去除能力 27
2.9 ELECTRO-FENTON 法之原理 28
2.10 國內含銀廢液處理現況 30
2.11 國內處理廢定影液之實例簡介 31
2.11.1 案例一:廢定顯影液處理設施試運轉計畫報告 31
2.11.2 案例二:照相沖洗廢液回收處理技術 33
三、研究材料與方法 34
3.1 實驗流程 34
3.2 實驗藥品 34
3.3 實驗設備 35
3.4 實驗方法 36
3.4.1 樣品來源 36
3.4.2 電解銀回收法 37
3.4.3 COD去除效率之研究 38
3.4.4 分析方法 38
3.5 實驗步驟 42
3.5.1 電解銀回收法 42
3.5.2 COD降解 42
四、結果與討論 44
4.1 電解回收銀之研究 44
4.1.1 低電流電解 44
4.1.2 高電流電解 50
4.1.3 鍛燒實驗 53
4.1.4 銀之精煉 54
4.1.5電解回收銀之總結 57
4.2 COD降解之研究 57
4.2.1電解試驗 58
4.2.2 濃縮試驗 63
4.2.3 化學沈澱法 64
4.2.4 COD去除情形之總結 67
  4.3 廢定影液之TOC檢測數據 69
  4.4 經濟效益分析 69
五、結論與建議 73
  5.1 結論 73
  5.2 建議 74
參考文獻 75
附錄 79
[1]Al-Hayek, N. and Dore, M.(1990): “Oxidation of Phenols in Water by Hydrogen Peroxide on Alumine Supported Iron”, Wat. Res., Vol. 24, pp. 973.
[2]Brandom N. P., Kellsall G. H. (1985): “Growth Kinetics of Bubbles Electrogenerated at Microelectrodes”, Journal of Applied Electrochemistry 15, pp.475-484.
[3]Cheves, W. and Goosen, A. (1972): “Mechanism of the Ferric Ion Catalyzed Decomposition of Hydrogen Peroxide Effect of Organic Substrates”, J. Amer. Chem. Soc., Vol. 95, pp. 2987.
[4]Cheves, W., El, G. M. and Johnson, R. A. (1974): “Fenton’s Reagent IV Structure and Reactivity Relations in the Reactions of Hydroxyl Radicals and the Redox Reactions of Radicals”, J. Amer. Chem. Soc., Vol. 96, pp. 133.
[5]Chou, S., Y. H. Huang, S. N. Lee, G. H. Huang and C. Huang. (1999): “Treatment of High Strength Hexamine-Containing Wastewater by Electro-Fenton Method”Wat. Sci. Tech., Vol.33, No.3, pp. 751–759.
[6]Dagon T. J. (1973): “Biological Treatment of Photoprocessing effluents”, Journal WCPF, Vol. 45, No. 10, pp.2123-2135.
[7]Franz, Posey. (1984): “Method for the Recovery of Silver from Waste Photographic Fixer solution”, U.S. Patent 4,445,935.
[8]Girou, Valentin, Storck, Guerlet, (1987): “A New Electrochemical Reactor for Silver Recovery from Phoptgraphic Fixing Baths”, Precious Metals.
[9]Grau, J.M. and Bisang, J.M. (1992): “Silver electrodeposition from photographic process solution”,Chem. Tech. Biotechnol.
[10]Gregory J. (1984): “Solid-Liquid Separation”, Ellis Horwood Limitted, pp.29-40.
[11]Hugh, R. E.(1964) “Oxidation of Phenolic Wastes”, J. Wat. Pollution Control Fed., Vol. 36, pp. 1116.
[12]J-55. (1991): “Disposal and Treatment of Photographic Processing Solutions – In Support of Clean Water”Eastman Kodak Company.
[13]Kibbel, W. H. (1978): “Phenol Problems Solved with Hydrogen Peroxide Oxidation”, Proc. 33rd Ind. Waste. Cof., pp. 22.
[14]Lin S. M. and Yang H. M. (1997): “Treatment of Photographic Effluents by Electrochemical Method”, Environmental Engineering Science, Vol. 14, No. 4, pp.201-206.
[15]Massimo, B., Claudio, M. and Ezio, P., “chemical Degradation of Chlorophenols with Fenton’s Reagent”, Chemosphere, Vol. 16,
[16]Minilabs Systems Managemment. (1991): Eastman Kodak Company , U.S.A.
[17]Neale E. M., Welland and Canada. (1994): “System for Treatment of Photographic wastewater effluent”, U.S. Patent 5,277,775. No. 10-12, pp. 2225, 1987.
[18]Panizza M. and Cerisola G. (2001): “Removal of Organic Pollutants from Industrial Wastewater by Electrogenerated Fenton’s Reagent”, Water Research, Vol. 35, No. 16, pp.3987-3992.
[19]Pavlostathis S. G. and Morrison D. (1994): “ Aerobic Biodegradation Potential of Photoprocessing Wastewaters” , Journal of Water Environment Research, Vol. 66, No. 3, pp.211-219.
[20]Pavlostathis S. G. and Sridhar K. (1994): “Anaerobic Biodegradation Potential of Photoprocessing Wastewaters”, Journal of Water Environment Research, Vol. 66, No. 3, pp.220-229.
[21]Pavlostathis S. G. and Morrison D. (1994): “Response of Continuous-Flow Activated Sludge Reactors to Photoprocessing Wastewaters”, Water Research, Vol. 28, No. 2, pp.269-276.
[22]Sheng H. Lin, Chi M. Cin and Horng G. Leu. (1999): “Operating Characteristics and Kinetic Studies of Surfactant Watewater Treatment by Fenton Oxidation”. Wat. Res. Vol. 33, No.7, pp. 1735-1741.
[23]Simes, A. F. E. (1983): “Industrial Effluent Treatment with Hydrogen Per-oxide”, Chemistry and Industry, pp. 5553.
[24]Spyros G. Pavlostathis and Krish Sridhar. (1994): “Treatment of Photoprocessing Effluents by the Activated Sludge Process”,J.Imaging Scienceand Technology , Vol.36.
[25]Thomas and Dagon. (1973): “Biological Treatment of Photoprocessing Effluents ”J.Water Pollution Control Federation , Vol.45,pp.2122-2135.
[26]Tseng, J. and Huang, C. P. (1991): “ Photocatalytic Oxidation Process for the Treatment of Organic Wastes”, 廢水物理化學處理程序理論講習會,交通大學, pp. 161。
[27]U.S. Environmental Protection Agency. (1991): “Guides to Pollution Prevention The Photoprocessing Industry”, EPA/625/7-91/012, Office of Research and Development, Washington, D.C. Vol. 14, No. 2, pp.35-40.
[28]台灣柯達公司物質安全資料表 (1999)。
[29]印刷會訊編輯小組 (2001),顯影液、定影液妥善處理―行政院環保署召開座談會,印刷會訊,492期,pp.10。
[30]行政院環境保護署 (1997),水污染防治法規,行政院環境保護署編印,pp.82-87。
[31]邱金同、蕭長青、詹明芳 (2002),應用電凝系統處理廚餘廢水,黎明學報 。
[32]張家倫 (1998),利用電聚浮除法處理乳化液中油脂之研究,國立台灣大學環境工程學系碩士論文,台灣台北, pp.3-13.
[33]莊亨立 (1999),以離子交換處理及回收照像廢液中之金屬銀,行政院國科會,NSC88-2214-E009-001,pp.1- 8。
[34]郭國良 (1992),Fenton法預處理照相廢液之研究,淡江大學,碩士論文。
[35]傅啟峰 (2001),電催化芬頓法處理皮革廢水,國立台灣大學環境工程學系碩士論文,台灣台北, pp.15-28。
[36]黃耀輝、周珊珊、黃國豪 (2001), Fenton 家族廢水高級技術,第二十八屆廢水處理技術研討會論文集,pp.135-146。
[37]楊婉琳 (2003),含銀廢液電解還原之研究,國立成功大學,碩士論文。
[38]經濟部工業局資源化產業資訊 (2003),“含廢定影液回收技術評析”第01期。
[39]經濟部環保署工業減廢聯合輔導小組 (1996),“工業減廢技術手冊-印刷工業”,經濟部工業局編印,pp.61-74。
[40]謝長原 (2000),電解催化氧化氯酚之研究,國立成功大學,碩士論文。
[41]林宜鋒 (2005),廢定影液之資源再利用,國立雲林科技大學,碩士論文。
[42]水質檢驗方法彙編 (1992),行政院環境保護署環境檢驗所。
[43]林世民 (1996),清潔生產雙月刊,第八期,中華民國清潔生產中心。
[44]嘉義地區醫療廢棄物共同處理委員會 (2004),廢定顯影液處理設施試運轉計畫報告。
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