TWI396595B - A method for the recycling of tin waste - Google Patents
A method for the recycling of tin waste Download PDFInfo
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- TWI396595B TWI396595B TW99110820A TW99110820A TWI396595B TW I396595 B TWI396595 B TW I396595B TW 99110820 A TW99110820 A TW 99110820A TW 99110820 A TW99110820 A TW 99110820A TW I396595 B TWI396595 B TW I396595B
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Description
本創作屬於環境保護及廢棄物資源再生技術領域。 This creation belongs to the field of environmental protection and waste resource recycling technology.
目前國內含錫廢料資源化廠家主要係收購廢剝錫液及廢錫鉛渣,再利用液鹼調整廢剝錫液之pH值產生錫泥餅,再將錫泥餅烘乾生成乾燥氧化錫,乾燥氧化錫送入高溫熔爐於1400~1600℃進行脫氧還原反應,將其還原成錫金屬狀態。 At present, the domestic tin-containing waste resource-reducing manufacturers mainly purchase scrap tin and lead tin slag, and then use liquid alkali to adjust the pH value of the waste stripping tin to produce tin mud cake, and then dry the tin mud cake to produce dry tin oxide. The dried tin oxide is sent to a high-temperature furnace for deoxidation reduction at 1400 to 1600 ° C to reduce it to a tin metal state.
另經查國內有關廢錫資源回收之專利,發現有中華民國專利編號472030、553906、555702、I227217、I281955、I225107其名稱皆為「剝錫鉛廢液處理方法」,其主要內容係針對剝錫鉛廢液中之錫、鉛及銅進行回收,而其主要方法為先將剝錫鉛廢液氧化生成錫及鉛之氧化物或氫氧化物,將其溶解後再以電解還原之方式,生成金屬錫或金屬鉛。 In addition, the domestic patents on the recycling of waste tin resources were found. The names of the Republic of China patents 472030, 553906, 555702, I227217, I281955, and I225107 were all described as "treatment methods for stripping lead liquid waste liquid". The tin, lead and copper in the lead waste liquid are recovered, and the main method is to first oxidize the tin-lead waste liquid to form tin or lead oxide or hydroxide, dissolve it, and then generate it by electrolytic reduction. Metal tin or metal lead.
綜合上述結果得知,未發現國內外有任何相關專利與技術係針對含錫廢料予以資源化成氯化亞錫產物之技術,故本發明可提供國內相關業者作為含錫廢料中之有價錫金屬資源回收之依據。 Based on the above results, it has been found that there is no related patent and technology at home and abroad for the technology of chemically converting tin-containing scrap into stannous chloride products. Therefore, the present invention can provide domestic related industries as valuable tin-metal resources in tin-containing scraps. The basis for recycling.
IC封裝產業、印刷電路板產業、電鍍業及表面處理業等產業,於處理錫金屬過程所衍生之含錫廢料,因其含有高量之有價錫資源,如無法回收再利用,將會造成錫資源整體之浪費,甚為可惜,故有鑑於此,本發明乃針對含錫廢料中有價錫金屬進行資源化回收之工作。 The IC packaging industry, the printed circuit board industry, the electroplating industry, and the surface treatment industry, etc., are tin-based wastes derived from the tin metal process. Because they contain high amounts of valuable tin resources, if they cannot be recycled, they will cause tin. The waste of resources as a whole is a pity, so in view of this, the present invention is directed to the recycling of valuable tin metal in tin-containing scrap.
本發明內容主要是,先將所收集之含錫廢料,以8N硝酸在固體(公克)/浸漬液(毫升)比為5/50的條件下,於室溫浸漬溶蝕4小時,可將此含錫廢料中之鉛及鋅雜質予以去除,以獲得具銷售價值之高純度氧化錫(SnO2)。而所得之氧化錫再以12 N鹽酸加還原劑在固體(公克)/浸漬液(毫升)比為1/50的條件下,於90℃下浸漬溶蝕5小時,可將氧化錫溶解於浸漬液中,以獲得含錫浸漬液。然後將其以鋅片置換,以將浸漬液中之錫置換成具銷售價值之金屬錫。然後將此置換金屬錫以12N鹽酸在固體(公克)/浸漬液(毫升)比為3/50的條件下,於70℃下加熱溶解2小時,以獲得含氯化亞錫溶液。再將此含氯化亞錫溶液在90℃下蒸發晶析,晶析完成後所得之產物,即為具銷售價值之高純度氯化亞錫產品。 The main content of the present invention is that the collected tin-containing waste material is firstly immersed and immersed for 4 hours at room temperature under the condition of a solid (g)/impregnation liquid (ml) ratio of 5N to nitric acid for 4 hours. The lead and zinc impurities in the tin scrap are removed to obtain high purity tin oxide (SnO 2 ) with a sale value. The obtained tin oxide is further immersed in a solid (g)/immersion liquid (ml) ratio at a ratio of 1/50 of 12 N hydrochloric acid plus a reducing agent at 90 ° C for 5 hours to dissolve the tin oxide in the immersion liquid. In order to obtain a tin-containing immersion liquid. It is then replaced with a zinc sheet to replace the tin in the immersion liquid with a metal tin of a sale value. Then, this replacement metal tin was dissolved by heating at 70 ° C for 2 hours under conditions of a solid (g)/impregnation liquid (ml) ratio of 3 N hydrochloric acid to obtain a stannous chloride-containing solution. Then, the stannous chloride-containing solution is evaporated and crystallized at 90 ° C, and the product obtained after the completion of the crystallization is a high-purity stannous chloride product having a sale value.
本發明之較佳方法示於第一圖,首先將收集之含錫廢料1(其外觀如附件一所示),進行硝酸浸漬溶蝕2步驟,此浸漬溶蝕之操作條件為:含錫廢料1(公克)/8N硝酸(毫升)=5/50,浸漬時間=4小時,浸漬溫度=27℃,硝酸浸漬溶蝕2步驟可將含錫廢料1中之鉛及鋅雜質予以去除,經硝酸浸漬溶蝕2步驟後,可獲得高純度氧化錫4(其外觀如附件二所示)。另此高純度氧化錫4之成份經能量分散光譜儀(Energy Dispersive Spectrometer,EDS)檢測分析結果如附件三所示,而含鉛及鋅之浸漬液21則可交予合格回收業者進行浸漬廢液回收處理3。 The preferred method of the present invention is shown in the first figure. First, the collected tin-containing scrap 1 (the appearance of which is shown in Annex 1) is subjected to a nitric acid impregnation and erosion step 2, and the impregnation and erosion operation conditions are: tin-containing scrap 1 (克)/8N nitric acid (ml)=5/50, immersion time=4 hours, immersion temperature=27°C, nitric acid immersion and erosion 2 steps can remove lead and zinc impurities in tin-containing waste 1 and impregnate by nitric acid. After the step, high-purity tin oxide 4 (the appearance of which is shown in Annex 2) can be obtained. The high-purity tin oxide 4 component is analyzed by Energy Dispersive Spectrometer (EDS) as shown in Annex III, while the lead and zinc-containing impregnating solution 21 can be submitted to qualified recyclers for impregnation waste recovery. Process 3.
另經硝酸浸漬溶蝕2所得之高純度氧化錫4,經進行鹽酸浸漬溶蝕5步驟後,可將氧化錫溶解成為含錫浸漬液52,此浸漬 溶蝕之操作條件為:高純度氧化錫4(公克)/12N鹽酸(毫升)=5/50,另加入還原劑(如草酸、酒石酸、亞硫酸鈉、次磷酸),浸漬時間=5小時,浸漬溫度=90℃,另經鹽酸浸漬溶蝕5所產生之殘渣51,則可交予合格業者進行最終處置6。 Further, the high-purity tin oxide 4 obtained by the nitric acid impregnation and etching 2 is subjected to the 5 steps of the hydrochloric acid impregnation and dissolution, and then the tin oxide is dissolved into the tin-containing impregnation liquid 52, and the impregnation is performed. The operating conditions for dissolution are: high purity tin oxide 4 (g) / 12N hydrochloric acid (ml) = 5/50, and additional reducing agent (such as oxalic acid, tartaric acid, sodium sulfite, hypophosphorous acid), immersion time = 5 hours, immersion temperature = At 90 ° C, the residue 51 produced by further impregnation of 5 by hydrochloric acid can be delivered to a qualified manufacturer for final disposal 6 .
而經鹽酸浸漬溶蝕5步驟後所得含錫浸漬液52,進行鋅片置換7步驟,可將浸漬液中之錫置換成置換金屬錫9,其置換條件為:置換溫度=27℃,置換時間=10分鐘,經鋅片置換7步驟所得之置換金屬錫9,其外觀如附件四所示,另此置換金屬錫9之成份經能量分散光譜儀(Energy Dispersive Spectrometer,EDS)檢測分析結果如附件五所示,而經鋅片置換7步驟所得之置換液71,則可交予合格回收業者進行置換廢液回收處理8。 The tin-containing immersion liquid 52 obtained by the 5 steps of hydrochloric acid immersion etching is subjected to a zinc sheet replacement step of 7 to replace the tin in the immersion liquid with the replacement metal tin 9, and the replacement condition is: replacement temperature=27° C., replacement time= 10 minutes, the replacement metal tin 9 obtained by the zinc sheet replacement step 7 is as shown in Annex IV, and the composition of the replacement metal tin 9 is analyzed by Energy Dispersive Spectrometer (EDS) as shown in Annex V. It is to be noted that the replacement liquid 71 obtained by the 7-step replacement by the zinc sheet can be supplied to a qualified recycler for the replacement waste liquid recovery treatment 8.
另鋅片置換7後所得之置換金屬錫9,則予以進行鹽酸溶解10步驟,以獲得含氯化亞錫溶液101,溶解條件為:置換金屬錫9(公克)/12N鹽酸(毫升)=3/50,溶解時間=2小時,溶解溫度=70℃,在此條件下可將置換金屬錫9完全溶解成為含氯化亞錫溶液101。 Further, after replacing the metal tin 9 obtained by replacing the zinc sheet with 7, the hydrochloric acid is dissolved in 10 steps to obtain a stannous chloride-containing solution 101, and the dissolution condition is: replacement metal tin 9 (g) / 12 N hydrochloric acid (ml) = 3 /50, dissolution time = 2 hours, dissolution temperature = 70 ° C, under which conditions the replacement metal tin 9 can be completely dissolved into the stannous chloride-containing solution 101.
此含氯化亞錫溶液101經進行晶析11步驟後,可將含氯化亞錫溶液101中之錫100%晶析成高純度氯化亞錫產品12,其外觀如附件六所示,此晶析11之條件為:於90℃下加熱蒸發晶析,另此高純度氯化亞錫產品12之成份經能量分散光譜儀(Energy Dispersive Spectrometer,EDS)檢測分析結果如附件七所示。 After the stannous chloride solution 101 is subjected to the crystallization step 11, the tin in the stannous chloride solution 101 can be 100% crystallization into a high-purity stannous chloride product 12, the appearance of which is shown in Annex 6. The conditions of the crystallization 11 are: heating and crystallization at 90 ° C, and the composition of the high-purity stannous chloride product 12 is analyzed by an Energy Dispersive Spectrometer (EDS) as shown in Annex VII.
為使本發明更加顯現出其進步性與實用性,茲將本發明之優點列舉如下: In order to make the present invention more expressive and practical, the advantages of the present invention are listed as follows:
1.本發明可回收含錫廢料中之有價錫金屬,減少有價錫金屬之資源浪費。 1. The invention can recover the valuable tin metal in the tin-containing waste, and reduce the waste of valuable tin metal.
2.本發明之技術成果可獲得具市場銷售價值之「高純度氧化錫」、「置換金屬錫」及「高純度氯化亞錫」產品。 2. The technical result of the present invention can obtain "high-purity tin oxide", "replacement metal tin" and "high-purity stannous chloride" products having market value.
3.本發明可避免含錫廢料中之錫金屬污染環境及危害人體健康。 3. The invention can avoid the tin metal in the tin-containing waste polluting the environment and endangering human health.
4.本發明可提升國內含錫廢料中之錫金屬資源再生之經濟效益。 4. The invention can improve the economic benefit of the regeneration of tin metal resources in domestic tin-containing waste.
5.本發明具安全性與進步性。 5. The invention is safe and progressive.
6.本發明具工商界與產業界之利用價值。 6. The invention has the use value of the business community and the industry.
第一圖係本發明「含錫廢料資源化之方法」之實施流程圖。 The first figure is a flow chart for implementing the "method of recycling tin-containing waste" of the present invention.
1‧‧‧含錫廢料 1‧‧‧ tin-containing scrap
2‧‧‧硝酸浸漬溶蝕 2‧‧‧Nitrate impregnation and erosion
21‧‧‧浸漬液 21‧‧‧ Impregnating solution
3‧‧‧廢液回收處理 3‧‧‧ Waste liquid recycling
4‧‧‧高純度氧化錫 4‧‧‧High purity tin oxide
5‧‧‧鹽酸浸漬溶蝕 5‧‧‧Hydraulic acid impregnation and erosion
51‧‧‧殘渣 51‧‧‧residue
52‧‧‧含錫浸漬液 52‧‧‧ tin-containing impregnating solution
6‧‧‧最終處置 6‧‧‧Final disposal
7‧‧‧鋅片置換 7‧‧‧Zinc strip replacement
71‧‧‧置換液 71‧‧‧Replacement fluid
8‧‧‧置換廢液回收處理 8‧‧‧Replacement waste liquid recycling
9‧‧‧置換金屬錫 9‧‧‧Replacement of tin
10‧‧‧鹽酸溶解 10‧‧‧ Hydrochloric acid dissolution
101‧‧‧含氯化亞錫溶液 101‧‧‧containing stannous chloride solution
11‧‧‧晶析 11‧‧ ‧ crystallization
12‧‧‧高純度氯化亞錫產品 12‧‧‧High purity stannous chloride products
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TW99110820A TWI396595B (en) | 2010-04-07 | 2010-04-07 | A method for the recycling of tin waste |
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Citations (9)
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US4600699A (en) * | 1983-02-14 | 1986-07-15 | Enthone, Incorporated | Reclamation of a palladium-tin based electroless plating catalyst from the exhausted catalyst solution and accompanying rinse waters |
JPH04304327A (en) * | 1991-03-29 | 1992-10-27 | Mitsubishi Materials Corp | Treatment of decopperized dross |
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TW312707B (en) * | 1996-02-05 | 1997-08-11 | Nat Science Council | Process for recovering solder metals from solder plating effluents and sludges |
TW403790B (en) * | 1998-12-01 | 2000-09-01 | Shiau Guo Shiung | Tin recycling method for the metal from tin plating, tin immersing and tin welding processes |
TW553906B (en) * | 2002-03-21 | 2003-09-21 | Amia Co Ltd | A method for the treatment of waste tin-lead stripping solution |
TWI250214B (en) * | 2003-06-13 | 2006-03-01 | Amia Co Ltd | Method for smelting metal tin from tin-containing compound |
CN101617067A (en) * | 2007-03-27 | 2009-12-30 | 日矿金属株式会社 | From the waste material that contains conductive oxide, reclaim the method for precious metals |
TW201012940A (en) * | 2008-09-22 | 2010-04-01 | Ching-Hwa Lee | Recycling of lead-free silver containing tin solder dross |
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2010
- 2010-04-07 TW TW99110820A patent/TWI396595B/en not_active IP Right Cessation
Patent Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
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US4600699A (en) * | 1983-02-14 | 1986-07-15 | Enthone, Incorporated | Reclamation of a palladium-tin based electroless plating catalyst from the exhausted catalyst solution and accompanying rinse waters |
JPH04304327A (en) * | 1991-03-29 | 1992-10-27 | Mitsubishi Materials Corp | Treatment of decopperized dross |
JPH0633158A (en) * | 1992-07-17 | 1994-02-08 | Techno Toriito:Kk | Treatment of zinc-and tin-containing scrap |
TW312707B (en) * | 1996-02-05 | 1997-08-11 | Nat Science Council | Process for recovering solder metals from solder plating effluents and sludges |
TW403790B (en) * | 1998-12-01 | 2000-09-01 | Shiau Guo Shiung | Tin recycling method for the metal from tin plating, tin immersing and tin welding processes |
TW553906B (en) * | 2002-03-21 | 2003-09-21 | Amia Co Ltd | A method for the treatment of waste tin-lead stripping solution |
TWI250214B (en) * | 2003-06-13 | 2006-03-01 | Amia Co Ltd | Method for smelting metal tin from tin-containing compound |
CN101617067A (en) * | 2007-03-27 | 2009-12-30 | 日矿金属株式会社 | From the waste material that contains conductive oxide, reclaim the method for precious metals |
TW201012940A (en) * | 2008-09-22 | 2010-04-01 | Ching-Hwa Lee | Recycling of lead-free silver containing tin solder dross |
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