[go: up one dir, main page]

TWI281955B - Treatment method of waste tin lead stripping solution - Google Patents

Treatment method of waste tin lead stripping solution Download PDF

Info

Publication number
TWI281955B
TWI281955B TW92104369A TW92104369A TWI281955B TW I281955 B TWI281955 B TW I281955B TW 92104369 A TW92104369 A TW 92104369A TW 92104369 A TW92104369 A TW 92104369A TW I281955 B TWI281955 B TW I281955B
Authority
TW
Taiwan
Prior art keywords
waste liquid
tin
stripping
lead
treatment
Prior art date
Application number
TW92104369A
Other languages
Chinese (zh)
Other versions
TW200417626A (en
Inventor
Guo-Jin Chen
Ching-Hua Jang
Huei-Ying Jeng
Jung-Jie Chen
Chin-Shiung Yang
Original Assignee
Amia Co Ltd
Persee Chemical Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Amia Co Ltd, Persee Chemical Co Ltd filed Critical Amia Co Ltd
Priority to TW92104369A priority Critical patent/TWI281955B/en
Publication of TW200417626A publication Critical patent/TW200417626A/en
Application granted granted Critical
Publication of TWI281955B publication Critical patent/TWI281955B/en

Links

Landscapes

  • Electrolytic Production Of Metals (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

This invention relates to a treatment method of waste tin lead stripping solution, which can be applied on recycling a waste tin stripping or tin lead stripping solution from, for example, a lead frame or a printed circuit board in the electronic industry. The method comprises an oxidation step for oxidizing stannic ions and lead ions into oxide and hydroxide precipitates of tin and lead at high temperature; a solid/liquid separation step for solid/liquid separating oxide and hydroxide precipitates of tin and lead obtained in the oxidation step; a reduction step for reducing the solid oxide and hydroxide precipitates of tin and lead obtained in the solid/liquid separation step into metal tin and tin-lead alloy; and a recycling step for neutralizing the filtrate obtained in the solid/liquid separation step with a base, which is followed by processes such as filtration, evaporation/crystallization, dissolution by adding acid, extraction, electrolysis/reduction, displacement reaction, etc. to produce valuable resources such as metal copper, copper sulfate, ferrous sulfate, ferric sulfate, ammonia, sodium nitrate or potassium nitrate so that the purpose of waste solution treatment and total resource recycling can be achieved.

Description

1281955 玖、發明說明 【發明所屬之技術領域】 ^本t明係屬於一種剝錫鉛廢液之處理方法,其應用在 電子工業lu王中,因剝離電鑛錫或電錢錫錯層所產生廢液 、 去另外,本發明亦相關於一種可自剝離電鍍錫 或電錢錫錯的廢液令,回收金屬錫、金屬銅、硫酸銅、硫 酸亞鐵或硫酸鐵的方法。 【先前技術】 在一般印刷電路板的製造過程中,常常需要在銅層上 電鍍錫層或錫鉛層,以保護在鹼性蝕刻過程中的銅層。當 蝕刻後去除非線路部份的銅層後,通常利用硝酸系的強酸 溶=將電鍍錫層或電鍍錫鉛層剝除,以便使銅層的線路部 ^ 員見利用硝酸系的強酸溶液,來剝除電鍍錫層或 電鍍錫鉛層的方法,可以參考美國專利公告號第5, 9ιι,9〇7 、5, 928, 529、5, 989, 449、6, 258, 294 B1 及 2〇〇1/_73ΠΑ號等前案,其巾強酸溶液的主要成份為硝酸 人肖&L鐵,在剝除電鍍錫層或電鍵錫錯層的過程中,當溶 液中的游離硝酸根陰離子濃度低於4Ν,或含錫量高於 l〇〇g/L時,即需重新配製更換新的硝酸系溶液,因而會產 生剝離電鍍錫層或電鍍錫鉛層的廢液。由於剝離電鍍錫層 或電鍍錫鉛層的廢液中,含有2至15g/L的銅離子、工至 4〇g/L的鐵離子或亞鐵離子、1〇至12〇g/L的錫離子或亞錫 離子(當廢液在儲存或運送的過程中,錫離子會被氧化形 成氧化錫或氫氧化錫沈澱物析出,因此有時候存在於廢液 12819551281955 玖, invention description [Technical field of invention] ^本明 is a kind of treatment method for stripping lead waste liquid, which is applied in the electronic industry Lu Wang, due to stripping of electric ore tin or electric money tin staggered layer Waste liquid, in addition, the present invention is also related to a method for recovering metallic tin, metallic copper, copper sulfate, ferrous sulfate or ferric sulfate from a waste liquid order capable of self-peeling electroplating tin or electrocalyx. [Prior Art] In the manufacturing process of a general printed circuit board, it is often necessary to plate a tin layer or a tin-lead layer on the copper layer to protect the copper layer during the alkaline etching process. After removing the copper layer of the non-line portion after etching, it is usually dissolved by a strong acid of nitric acid = stripping the electroplated tin layer or the electroplated tin-lead layer, so that the line portion of the copper layer can see a strong acid solution using a nitric acid system. For the method of stripping the tin plating layer or plating the tin-lead layer, reference can be made to U.S. Patent Publication Nos. 5, 9, 9, 7, 5, 928, 529, 5, 989, 449, 6, 258, 294 B1 and 2 In the case of 〇1/_73ΠΑ, etc., the main component of the strong acid solution of the towel is nitric acid &L iron. During the stripping of the tin plating layer or the tin-bonding layer, the concentration of free nitrate anion in the solution is low. At 4 Ν, or when the tin content is higher than l〇〇g/L, it is necessary to re-form the new nitric acid solution, thus causing the waste liquid to peel off the tin plating layer or the tin-lead layer. In the waste liquid of the electroplated tin layer or the tin-plated lead layer, it contains 2 to 15 g/L of copper ions, iron ions or ferrous ions of 4 〇g/L, and tin of 1 to 12 〇g/L. Ionic or stannous ions (since the waste liquid is stored or transported, tin ions are oxidized to form tin oxide or tin hydroxide precipitates, so sometimes they are present in the waste liquid 1281955

中的錫離子及亞錫離子含量會低於1〇g/L。)、〇至Hg/L 的鉛離子及2.0至6. ON的游離硝酸溶液,因此有必要妥善 處理經剝離電鍍錫層或電鍍錫鉛層的廢液,以免嚴 、、九 環境。 ’可木 目前習用的處理方法首先利用氫氧化納中和剝錫錯層 廢液中的游離硝酸,並調整pH值在8至13 曰 〜间,使大部 伤:重金屬陽離子形成氧化物或氫氧化物之沈澱物,過遽 所得的氧化物或氫氧化物固形物,再以冶煉的方法煉製金 屬錫,或者以高濃度鹼液將固形物溶解後,再以電解的方_ 法還原以得金屬錫’而渡液則利用蒸發結晶的方式以製成 琐酸納晶體。然而f用技術之主要缺點為氧化物或氫氧化 物固形物中含有不少重金屬銅、鐵及錯,特別是銅抑塑 冶煉或電解所得金屬錫的純度。 /曰 全屬==民國專利法公告第1 7791 1號「從1㈣廢液回收 , 〜3又丨不你竿1以μ 置換還原廢液中的錫離子或亞錫離子, 屬 加以回收。然"專利内容中所闡述的處理方;金= 的遇原劑及沈殿劑,且過程繁雜,故為不經濟之處 成H 於處理過程中,錫離子或亞錫離子極易形 成虱化物或氫氧化物沈澱析出, -片置換還原得金屬錫亦為其缺點此不易找出適當時機以 n於中華民國專利公告第258758號「鑛錫 再生方法及裝置」乙案中’揭露利用離子交換樹脂以分 中了方法」乙案中,揭露利用添加還原劑、沈殺劑及 中和別的方法,使處理後的排放水達到 置換還眉麻你由ΛΛ加私7二、_ ^ + I W i呂片 1281955 離電鍍液中的鐵、鉻、錫等離子之用以回收再生鍍錫助劑 及金屬錫的方法。然而該方法亦具有處理過程相當繁雜的 缺點,因此並不適用於處理剝離電鍍錫層與電鍍錫鉛層後 的廢液。 另外,中華民國專利公告第472〇3〇號「剝錫鉛廢液之 處里方法」乙案中,揭露於廢液中加入沈殿劑與中和劑(驗 性藥剤),並進行過濾、加熱去氨、沈澱溶解等一連串分離 私序以達到廢液中的有價成份的回收與廢液處王里的環保 . 工作。該方法可由剝錫鉛廢液回收之成分製成95%純度之 錫酸納、80%之氟化鈉或硝酸鈉及93%之硫酸銅晶體。錫 酸納可經過電解精練而得到99 9%的金屬錫;^鈉或石肖酸 納及硫酸銅,則可藉由再結晶的方式提高其純度。該方法 雖然可以達到廢液中有價成份之回收與廢液處理的環保工 作,但與前述習用技術具有相同的缺點,即中和後所產之- 氧化物或氫氧化物固形物中含有不少重金屬銅、鐵及^, 特別是銅含量過高時會使得後續精製錫的程序變得過於繁 雜。 ·· 至於中華民國專利公告第期4Μ虎、美國專利公 576圖、6UG349及62_5號等專利前案,則提及„ . 鑛錫液内所沈殿的錫泥或處理剥錫錯廢液的過程中所沈! :錫泥,:強驗溶解後,再經電解還原得金屬錫的方法:、. ”可供作處理錫泥的參考。另外,與本發明 - 專利公告第4981 12號「一種去除剝 4民國_ - ^ ^ Ά …錫或剩錫鉛廢液中銅、 錫離子之方法」,其處理剥怒廢液的内容亦可併 1281955 入作為茶考。 【發明内容】 、處理方式簡單而完 子的剝錫鉛廢液處理 有鑑於此,需要一種具有經濟性 整,且可有效回收廢液中所含金屬離 方法。 、、因此’本發明之目的為提供一種處理剝錫或剝錫鉛廢 液以回收金屬㉟、金屬銅或硫酸銅與硫酸亞鐵成硫酸鐵的 方法,其包括: 氧化步驟:在高溫下將錫離子與鉛 錯之氧化物及氫氧化物沈殺物; 離子氧化成為錫 Μ 鉛之氧化物及 錫與鉛之氧化The tin ion and stannous ion content will be less than 1〇g/L. ), the lead ion of Hg/L and the free nitric acid solution of 2.0 to 6. ON, so it is necessary to properly dispose the waste liquid of the stripped tin plating or the tin-lead layer to avoid the strict environment. The current treatment method of the wood can firstly use the sodium nitrate to neutralize the free nitric acid in the stripping solution, and adjust the pH between 8 and 13 曰 to make most of the damage: heavy metal cations form oxides or hydrogen. a precipitate of oxide, which is obtained by smelting the oxide or hydroxide solid, and then refining the metal tin by a smelting method, or dissolving the solid substance in a high concentration alkali solution, and then reducing it by electrolysis The metal tin is obtained, and the liquid is evaporated to crystallize to form a sodium silicate crystal. However, the main disadvantage of the f-use technique is that the oxide or hydroxide solids contain a lot of heavy metals such as copper, iron and iron, especially the purity of the metal tin obtained by copper smelting or electrolysis. /曰All ===Republic of China Patent Law Notice No. 1 7791 No. 1 "Recovering from 1 (four) waste liquid, ~3 and not 竿1 replacing the tin ion or stannous ion in the waste liquid with μ, it is recycled. "The treatment described in the patent content; gold = the original agent and the sinking agent, and the process is complicated, so it is uneconomical to become H. During the treatment, tin or stannous ions are easily formed into telluride or Precipitation of hydroxide precipitates, and the reduction of metal tin by sheet replacement is also a disadvantage of this. It is not easy to find a suitable time to disclose the use of ion exchange resin in the case of the "mineral regeneration method and apparatus" of the Republic of China Patent No. 258758. In the case of the method, in the case of B, it is revealed that the method of adding reducing agent, killing agent and neutralization can make the discharged water after treatment reach the replacement and still add to your yin. _ ^ + IW i Lv 1281955 A method for recovering tin-plating auxiliaries and metallic tin from iron, chromium and tin in electroplating bath. However, this method also has the disadvantage of being quite complicated in the process, and therefore is not suitable for treating the waste liquid after stripping the electroplated tin layer and the tin-lead layer. In addition, in the case of the Republic of China Patent Bulletin No. 472〇3, “Methods for Stripping Lead Waste Waste Liquid”, it was revealed that the addition of a sedative agent and a neutralizing agent (inspective drug 剤) to the waste liquid was carried out, and filtration was carried out. Heating a deamination, precipitation and dissolution, etc., a series of separate private orders to achieve the recovery of valuable components in the waste liquid and the environmental protection of the waste liquid. The method can produce 95% pure sodium stannate, 80% sodium fluoride or sodium nitrate and 93% copper sulfate crystals from the components recovered by the stripping lead waste liquid. Sodium stannate can be electrolytically scoured to obtain 99 9% of metallic tin; sodium or succinic acid and copper sulphate can be recrystallized to increase their purity. Although this method can achieve the environmental protection work of the recovery of valuable components in the waste liquid and the treatment of waste liquid, it has the same disadvantages as the above-mentioned conventional technology, that is, the oxide or hydroxide solid content produced after the neutralization contains a lot of Heavy metals such as copper, iron and ^, especially when the copper content is too high, make the subsequent process of refining tin too complicated. ·· As for the pre-existing patents of the Republic of China Patent Announcement No. 4 Tiger, US Patent No. 576, 6UG349 and 62_5, mention „ . The process of tin mud in the tin bath or the process of stripping the wrong waste liquid Sinking in the middle!: Tin mud,: After the strong dissolution, the method of reducing the metal tin by electrolysis:, ” can be used as a reference for the treatment of tin mud. In addition, the present invention - Patent Publication No. 4981 12 "A method for removing copper and tin ions in the waste liquid of the tin or the residual tin-lead", the content of the treatment of the detoxification waste liquid may also be And 1281955 into the tea test. SUMMARY OF THE INVENTION In view of the above, there is a need for an economical and efficient method for recovering metal ions contained in waste liquid. Therefore, the object of the present invention is to provide a method for treating a stripping or stripping lead waste liquid to recover metal 35, metallic copper or copper sulfate and ferrous sulfate into iron sulfate, comprising: an oxidation step: at a high temperature Tin oxide and lead oxide and hydroxide sinker; ion oxidation to tin bismuth lead oxide and oxidation of tin and lead

固液分離步驟:將氧化步驟所得之錫、 氫氧化物沈殿物加以固液分離; 還原步驟:將固液分離步驟所得之固態 物及氫氧化物還原成為金屬錫或錫鉛合金; 之濾液以礙中和後 、電解還原、置換 硫酸亞鐵、硫酸鐵 回收步驟:將固液分離步驟所產生 ,經過濾、蒸發結晶、加酸溶解、萃取 反應等程序回收製得金屬銅、硫酸銅、 、氨水、硝酸鈉或確酸鉀等有價資源。 根據本發明之方法除可確實達到廢液處理的目的,並 可達到資源完全回收的效果。 【實施方式】 剝錫鉛廢液之 、中和及蒸發 、還原步驟及 請參看第一圖所示,本發明處理剝錫或 方法主要疋利用咼溫氧化、冶煉、電解還原 結晶等方法來進行氧化步驟、固液分離步驟 11 1281955 回收步驟。 -明Γ法之氧化步驟乃是在高溫下氧化生成錫與鉛 之乳*風氧化物沈殿之步驟’於45 fiJ i2〇〇c的 圍内進行,較佳是在6〇到1(^c的溫度範圍内 = =於饥進行氧化作用時,沈殿物之生成速率太慢 進行氧化作料,則會有大量錢被蒸發出來 '、、、。生鼠乳化物⑽x)等揮發物之危險。因此,在45 到、12=的溫度範圍内’較佳是在60到mt;的溫度範圍 内進仃乳化步驟將具有快速將廢液中錫離 形成錫與^氧化物及氫氧㈣驗物之功效。 ^ 在氧化步驟中,可以單獨使用通氣氧化方法、化學氧 =,或電解氧化方法,亦可合併使用以提高氧化效果。 =μ化方法是將臭氧、氧氣或空氣等有助於氧化反應 體直接通入廢液中;該化學氧化方法是對廢液進 辰細來提面廢液中硝酸濃度或是直接添加濃石肖酸到 曆液中;而該電解夤化t、、土 β & 電位差使陽極區域發生氧化作用來進行 在前述之通氣氧化方法中, L. ^ ^ T 口為虱分子在高溫下可以 快速氧化錫離子與鉛離子,使 ^ 之之形成錫與鉛之氧化物及氫 氧化物沈殿物’因此溶液中 Μ Τ錫離子與鉛離子之濃度會快速 Ρ牛低。例如在80°C的溫度下,诵人每# 入乳氣1小時,即可使廢 液中的錫離子濃度降低至5g/L以下。 在前述之化學氧化方法中, ^ _ 因為廢液中硝酸濃度會被 徒咼,而硝酸在高溫下可以快洁一 κ速乳化錫離子與鉛離子,使 *乳化方法疋在電解槽中,對加 ·< Φ 乂TV 辇 /士 17曰e .、、 一 12 1281955 之形成錫與錯之氧化物刀_ 、、田产下n 物及氧礼化物沈澱物。例如在8〇。〇的 /皿度下棱尚廢液中硝酸濃度至7Ν 錫離子濃度降低至5g/L以下 ,即可使廢液中的 、當r _ T。該化學氧化方法可以在直空 酸可以3Α 而直接添加到廢液中之濃硝 酉夂了以疋浪度介於5〇〜1〇〇%之市售硝酸。 在前述之電解氧化方法中, ^ 6V . p, # ^ θ 陰%極電位差係保持在2 之間,猎由%極區域的電解氧化作用,使得廣液中之 =錯離子w與錯之氧化物及氫氧心: "4 g C陰%極電位差4肩的條件下進行電解氧化4#| 小寺,即可使廢液中錫離子濃度降低至5g/L以下。 :其需要’在氧化步驟中’若高溫氧化廢液中之鉛離 7銘之乳化物及氫氧化物沈澱物的效率過低時,可於 高溫氧化期間或之後’於廢液中添加接近於錯離子當量的 硫酸根離子以促進形成硫酸錯晶體而錢析出。其_ 硫酸根離子的化合物包括有 ^ 或硫酸<—不限疋為·硫酸、硫酸納 本發明方法之固液分離步驟中,可利用任何習知之固魯· 液分離方法來從廢液中分離出錫與錯之氧化物及氫氧化物 、並視情況需要進而產生硫酸錯沈殿物。相較於習用技術 或中華,國專利公告號第·3Q號,以本發明方法所得錫 與錯之氧化物及氫氧化物沈殿物中僅含微量銅離子及鐵(亞 鐵)離子,故後續還原步驟較易製得高純度金屬錫或錫錯a — 金。 ° 在還原步驟中,乃是將於固液分離步驟中分離所得之 13 1281955 固態錫與錯之氧化物及氫氧化物,以及可能產生之炉較 ' 沈澱物,先以水洗淨及烘乾後,再與含碳成份為主的活^ 碳、焦碳或石墨以及碳酸納混合並研磨,於6〇〇至12〇吖 高溫下,較佳,進行冶煉,可製得金屬錫或 錫鉛合金。或者先以水洗淨後,將沈殿物溶於強驗中,可 使用的強驗包括有,但不限定於:氣氧化納、氯氧化卸或 其混合物。較佳的驗為當量濃度介於2. Q到7肩之气氧化 納、。氫氧化钾或其混合溶液,所使用的溶解溫度在室 較佳在8〇。。到16(rc之間’而溶解所需要之時㈣ 間為兩於i小時’較佳為高於5小時,如此可使溶液中的 錫含置達到3〇g/L以上,通常可達5。到15〇的之間。滤 除未溶解的固形物後,將此含錫與錯之驗性溶液,於5〇到 膽的溫度下進行電解還原步驟,可回收製得金屬錫或錫 鉛合金’而陰陽極電位差則以介於15到7.〇v之間為較佳 。以尚溫冶煉法或電解還原法所製得之金屬錫或錫錯合全 ’可於硫酸亞錫溶液中更進一步被電解精製以製得高純度 錫,而其方法與習用電解精製粗銅成為精銅者相同。a __ 經氧化步驟高溫氧化後,剝錫錯廢液中大部份錫離子 與鉛離子均已被氧化形成錫與 礼化物及虱虱化物沈澱 , ,再、、,!固液分離步驟固液分離之 ;;;::;' 離子或亞鐵離子與2.〇至6.⑽的游離硝酸。 — 將固液分離步驟所產生之據液於回收步驟中 -- 納或氯氧化卸中和並調整其pH值至8〜13,使遽液;= 14 1281955 及銅4重金屬離子形成氧化物及氫氧化物沈澱析出,再經 固液分離後,可得含硝酸鈉或硝酸鉀的濾液與含鐵及銅等 氧化物及氫氧化物沈澱物的濾餅。所得濾液經加熱除氨後 ’可使用洛發結晶方法製得硝酸鈉或硝酸鉀晶體,而濾餅 則經添加稀硫酸溶液溶解後,利用萃取法製得硫酸銅及硫 酸鐵或硫酸亞鐵,或以置換法製得金屬銅粉末與硫酸亞鐵 ’亦或以電解還原法製得金屬銅粉末與硫酸亞鐵,亦或以 電解還原法製得金屬銅與硫酸亞鐵。前述之萃取法可參考 美國專利公告號第4, 252, 621號,中國大陸專利公告號第 1 1 54723A號及第1299784A號等,利用商標名為ux_54的 曰曰 曰曰 換溶液巾之銅離子為金相粉,錢㈣溶解形成亞鐵離 2 ’經過;t、乾燥製得金屬銅粉,㈣所產生的硫酸亞鐵 f液則經蒸發結晶製得硫酸亞鐵晶體,或以氧氣、空氣等 :::成硫酸鐵溶液;前述之電解還原法為將稀硫酸溶液 置於電解槽中,於陰陽極 φ ή6 ^ ^ 1主Μ的條件下,將溶液 Τ的銅離子還原成金屬 曰 殘餘&馱亞鐵溶液則經蒸發結 曰曰I侍心酸亞鐵晶體,或氧 溶液。 礼孔工乱專虱化形成硫酸鐵 有機萃取劑萃取稀硫酸溶液中的銅離子,再以濃硫酸溶液 ,萃取溶於有機萃取劑LIX—54之迴流,再利用於萃取稀硫 酉欠溶液中的銅離子,而硫酸銅溶液則經冷卻結晶或蒸發結 、過濾及乾燥等步驟製得硫酸銅晶體,過濾所產生的結 母液亦經迴流再用於反萃取有機萃取劑lix — 54^的銅離 子,4述之置換法為利用添加鐵粉於稀硫酸溶液中,以置 Φ4 15 1281955 【實施例】 實施例1 : 取5L剝錫鉛廢液,該廢液内含約1〇g/]L Cu2+、3〇g/L Fe2VFe3+、30g/L Sn2VSn4+及 1〇 抑2+。將該廢液加熱 至8 0 C,攪拌並通入氧氣2小時後,廢液中形成大量錫之 氧化物及氫氧化物沈澱物。過濾分離錫之氧化物及氫氧化 物沈澱物。在80°C下,將所得之固態錫之氧化物及氫氧化 ‘ 物’合於2L,》辰度為3N的氫氧化鈉溶液中歷時6小時。接著 、 ,提昇此含錫鹼溶液溫度至95r,並於陰陽極電位差為 3. OV的條件下進行高溫電解還原步驟歷時丨〇小時後,溶液 中錫含量約3g/L,並回收得到約12〇§金屬錫。 實施例2 : 同實施例1的操作,於過濾分離錫之氧化物及氯氧化 物沈殿物後’將其經水洗及洪乾,取lg乾沈澱物,加 入20g活性奴及80. 〇3g碳酸鈉,經混合及研磨後,於 °C高溫下歷時4小時,冶煉製得512g純度為98 5%的金屬 錫。 實施例3 :Solid-liquid separation step: solid-liquid separation of tin and hydroxide precipitate obtained in the oxidation step; reduction step: reducing solid matter and hydroxide obtained by the solid-liquid separation step into metal tin or tin-lead alloy; After the neutralization, electrolytic reduction, replacement of ferrous sulfate, iron sulfate recovery step: the solid-liquid separation step is generated, through filtration, evaporation crystallization, acid dissolution, extraction reaction and other procedures to recover metal copper, copper sulfate, Valuable resources such as ammonia, sodium nitrate or potassium silicate. According to the method of the present invention, the purpose of the waste liquid treatment can be surely achieved, and the effect of complete recovery of resources can be achieved. [Embodiment] The process of stripping, neutralizing, evaporating and reducing the tin-lead waste liquid, and referring to the first figure, the method for treating the stripping or the method of the present invention is mainly carried out by using the method of temperature oxidation, smelting, electrolytic reduction and crystallization. Oxidation step, solid-liquid separation step 11 1281955 Recovery step. - The oxidation step of the alum method is carried out at a high temperature under the step of oxidizing tin and lead milk * wind oxide sulphide in a circle of 45 fiJ i2 〇〇 c, preferably at 6 〇 to 1 (^c Within the temperature range = = When the hunger is oxidized, the rate of formation of the stagnation is too slow to carry out the oxidation, and there will be a lot of money to be evaporated out, and the risk of volatiles such as the rat emulsion (10)x). Therefore, in the temperature range of 45 to 12 = preferably in the temperature range of 60 to mt; the emulsification step will have a rapid separation of tin from the waste liquid to form tin and oxides and hydrogen (IV) The effect. ^ In the oxidation step, aeration oxidation method, chemical oxygen =, or electrolytic oxidation method may be used alone, or may be used in combination to increase the oxidation effect. The method of μ is to facilitate the direct oxidation of the oxidation reaction body into the waste liquid by ozone, oxygen or air; the chemical oxidation method is to increase the concentration of nitric acid in the waste liquid of the waste liquid or directly add the thick stone. The acid is in the liquid state; and the electrolytic deuteration t, the soil β & potential difference causes the anode region to oxidize to perform the aeration oxidation method described above, the L. ^ ^ T port is a helium molecule which can be rapidly at a high temperature Tin oxide ions and lead ions cause the formation of tin and lead oxides and hydroxides. Therefore, the concentration of lanthanum, tin and lead ions in the solution is rapidly lower than that of yak. For example, at a temperature of 80 ° C, the concentration of tin ions in the waste liquid can be reduced to less than 5 g / L per person for 1 hour. In the aforementioned chemical oxidation method, ^ _ because the concentration of nitric acid in the waste liquid will be abrupt, and the nitric acid can quickly smelt the tin ion and the lead ion at a high temperature, so that the *emulsification method is carried in the electrolytic cell, Add·< Φ 乂TV 辇/士17曰e.,, 12 12 1955, the formation of tin and wrong oxide knives _,, the field of n material and oxygen ritual deposits. For example, at 8〇. The concentration of nitric acid in the waste liquid of the crucible is up to 7 Ν. The concentration of tin ions is reduced to less than 5 g/L, so that r _ T can be obtained in the waste liquid. The chemical oxidation method can be carried out in a concentrated nitric acid which can be directly added to the waste liquid at a concentration of 3 Torr, and commercially available nitric acid having a enthalpy of 5 〇 to 1%. In the above electrolytic oxidation method, ^ 6V . p, # ^ θ anion % potential difference is maintained between 2, hunting by the electrolytic oxidation of the % pole region, causing oxidation of the wrong ions in the wide liquid w and And hydrogen-oxygen heart: "4 g C%% potential difference 4 shoulders under the conditions of electrolytic oxidation 4#| small temple, the concentration of tin ions in the waste liquid can be reduced to below 5g / L. : It needs to be 'in the oxidation step'. If the lead in the high-temperature oxidation waste liquid is too low in efficiency from the 7-Ming emulsion and hydroxide precipitate, it can be added to the waste liquid during or after high-temperature oxidation. The wrong ion equivalent sulfate ion precipitates in order to promote the formation of a sulfuric acid miscrystal. The compound of the sulfate ion includes the sulfuric acid and the sulfuric acid, and is not limited to sulfuric acid or sulfuric acid. In the solid-liquid separation step of the method of the present invention, any conventional solid solution can be used to separate from the waste liquid. The tin and the wrong oxides and hydroxides are produced, and, depending on the situation, the sulfuric acid is staggered. Compared with the conventional technology or the Chinese, the national patent publication No. 3Q, the tin and the wrong oxide and hydroxide in the method of the present invention contain only a trace amount of copper ions and iron (ferrous) ions, so follow-up The reduction step makes it easier to produce high-purity metal tin or tin-a-gold. ° In the reduction step, the 13 1281955 solid tin and the wrong oxide and hydroxide will be separated in the solid-liquid separation step, and the furnace may be produced as a 'precipitate, first washed and dried with water. After that, it is mixed with and grinded with carbon-containing carbon, coke or graphite and sodium carbonate. It is preferably smelted at a high temperature of 6 to 12 Torr to obtain metallic tin or tin-lead. alloy. Or, after washing with water, dissolve the Shen Temple in the strong test. The strong tests that can be used include, but are not limited to, gas oxidation, chlorine oxidation or a mixture thereof. Preferably, the equivalent concentration is between 2. Q and 7 shoulder gas oxides. The potassium hydroxide or a mixed solution thereof is preferably used at a temperature of 8 Torr in the chamber. . When it is between 16 (between rc and the time required for dissolution (4) is two hours, preferably more than 5 hours, so that the tin content in the solution can be set to 3 〇g/L or more, usually up to 5 Between 15 。. After filtering out the undissolved solids, the tin-and-error-containing test solution is subjected to an electrolytic reduction step at a temperature of 5 〇 to the gallbladder, and the metal tin or tin-lead can be recovered. The alloy' and the anode-anode potential difference are preferably between 15 and 7. 〇v. The metal tin or tin mismatched by the smelting method or the electrolytic reduction method can be used in the stannous sulfate solution. Further, it is electrolytically refined to obtain high-purity tin, and the method is the same as that of conventionally electrolytically refining crude copper to become refined copper. a __ After oxidation by high temperature oxidation, most of the tin ions and lead ions in the stripping waste liquid are Has been oxidized to form tin and ritual and phlegm precipitates, and then, solid solution separation step solid-liquid separation;;;::; ' ion or ferrous ion and 2. 〇 to 6. (10) free Nitric acid. - The liquid produced by the solid-liquid separation step is neutralized in the recovery step - sodium or chlorine oxidation and The pH value is adjusted to 8~13, so that the sputum; = 14 1281955 and copper 4 heavy metal ions form oxides and hydroxide precipitates, and after solid-liquid separation, the filtrate containing sodium nitrate or potassium nitrate can be obtained. A filter cake of oxides and hydroxide precipitates such as iron and copper. The obtained filtrate is heated to remove ammonia, and then sodium nitrate or potassium nitrate crystals can be obtained by using the Luofa crystallization method, and the filter cake is dissolved by adding a dilute sulfuric acid solution. Obtaining copper sulfate and iron sulfate or ferrous sulfate by extraction method, or obtaining copper metal powder and ferrous sulfate by replacement method, or preparing copper metal powder and ferrous sulfate by electrolytic reduction method, or by electrolytic reduction method Metallic copper and ferrous sulfate. For the aforementioned extraction method, reference is made to U.S. Patent No. 4,252,621, Chinese Patent Publication No. 1 1 54723A and No. 1297978A, etc., using the trade name ux_54 The copper ion of the solution towel is metallized powder, the money (4) dissolves to form ferrous iron 2' passes; t, the metal copper powder is obtained by drying, and the ferrous sulfate f liquid produced by (4) is evaporated to obtain ferrous sulfate. Crystal, or oxygen , air, etc.::: into iron sulfate solution; the above electrolytic reduction method is to place the dilute sulfuric acid solution in the electrolytic cell, and reduce the copper ions of the solution to metal after the anode and cathode of φ ή6 ^ ^ 1 main enthalpy曰Residual & ferrous solution is evaporated to form ferrous ferrous crystals, or oxygen solution. The hole is specially formed to form iron sulphate organic extractant to extract copper ions in dilute sulfuric acid solution, and then concentrated The sulfuric acid solution is extracted and dissolved in the organic extractant LIX-54, and then used to extract the copper ions in the dilute sulfur solution, and the copper sulfate solution is obtained by cooling crystallization or evaporating, filtering and drying. Crystals, the mother liquor produced by filtration is also refluxed and used to back-extract the copper extract of the organic extractant lix — 54^, and the replacement method is to use iron powder in dilute sulfuric acid solution to set Φ4 15 1281955. EXAMPLES Example 1: A 5 L stripping lead waste liquid containing about 1 〇g/] L Cu 2+ , 3 〇 g / L Fe 2 V Fe 3 + , 30 g / L Sn 2 VS n 4 + and 1 〇 2+ was taken. The waste liquid was heated to 80 C, stirred and oxygen was introduced for 2 hours, and a large amount of tin oxide and hydroxide precipitate were formed in the waste liquid. The tin oxide and hydroxide precipitate were separated by filtration. The obtained solid tin oxide and hydroxide were combined in 2 L of a 3N sodium hydroxide solution at 80 ° C for 6 hours. Then, the temperature of the tin-containing alkali solution is raised to 95r, and the high-temperature electrolytic reduction step is carried out under the condition of a cathode-anode potential difference of 3. OV, and the tin content in the solution is about 3 g/L, and about 12 is recovered. 〇§ Metal tin. Example 2: The same operation as in Example 1, after separating and separating the oxide of tin and the oxychloride from the sulphate, it was washed with water and dried, and lg dry precipitate was taken, and 20 g of active slave and 80. 〇 3 g of carbonic acid were added. Sodium, after mixing and grinding, was smelted at a high temperature of ° C for 4 hours to obtain 512 g of metallic tin having a purity of 98 5%. Example 3:

取 lm 内含約 5g/L Cu2+、30g/L Fe2 + /Fe3+、3〇g/LTake lm containing about 5g/L Cu2+, 30g/L Fe2 + /Fe3+, 3〇g/L

Sn /Sn及10 ppm Pb2+離子之剝錫鉛廢液,將該廢液加熱 至90 C㈣並通人氧氣2小時後,廢液中形成大量锡之 氧化物及氫氧化n殿物。在廢液溫度降低到5(rc以下時 過;t刀離錫之氧化物及氯氧化物沈殿物。力工⑽。C下,將 所得之固態錫之氧化物及氫氧化物溶於祖,濃度為扑的 16 1281955 f氧化鉀溶液中歷時10小時。然後,過遽去除溶液中尚去 冷解之固形物。奴後’調整此含錫鹼溶液溫度i ° 陰陽極電位差為3,的條件下進行高溫電解還原步驟= 約^、時後,此時溶液中錫含量低於5g/L,並可^ 23kg金屬錫。 了侍約 實施例4 ·· 同實施例3的操作’於過濾分離錫之氧化物及氫氧化 物沈澱物後,取254g澄沈澱物,加入63 6g活性碳及 253. 3g碳酸鈉,經混合及研磨,於95〇t高溫下歷時4小 時,冶煉製得58. 5g純度為99· 5%的金屬錫。 實施例5 : 類似於實施1〜4的操作,於過濾分離錫之氧化物及氫 · 氧化物沈澱物後,沈澱物以溼法電解還原或以火法冶煉製 得金屬錫,濾液則以濃度約3N氫氧化鈉液中和並調整pH 至約11,濾液中形成褐色的鐵、銅、錫、鉛等氧化物及氫 氧化物的褐色濾餅與含硝酸鈉的淡綠色濾液,取3 〇 〇m 1淡 綠色滤液,經蒸發結晶可製得約2Gg呈淡綠或淡黃的石肖酸_籲 納晶體’利用原子吸收光譜(A、A)分析其重金屬含量,結果^___ 編5虎 顏色 Cu(ppm) Fe(ppm) Sn(ppm) Pb(ppm)— 1 淡綠 25. 84 22. 61 ND ND 2 淡綠 ND 14. 89 ND ND 3 淡黃 ND 3. 67 ND ND__ 實施例6 ·· 17 1281955 同實施例5’於過渡分離得含鐵、銅、錫 及氫氧化物的褐色遽餅後’將此褐色據餅溶於濃度約:的 稀硫酸溶液中,形成微帶褐色的綠色溶液,於陰陽極電位 差yv及溫度15t的條件下電解2小日寺,溶液中銅離子幾 乎完全被電解還原成金屬銅,而使得溶液成為含硫酸亞鐵 為主的綠色溶液。 以上實施例僅為本發明技術的示範例子,其並非用來 , 限定本發明為特定形式,熟悉該項技術者在瞭解本發明之 後 了依此進行任何修飾或改變,而該等修飾或改變應包麵 括於本案申請專利範圍之範疇内。 【圖式簡單說明】 (一) 圖式部分 第一圖為本發明之流程示意圖。Sn/Sn and 10 ppm Pb2+ ion stripping lead waste liquid, the waste liquid is heated to 90 C (four) and passed through oxygen for 2 hours, a large amount of tin oxide and hydroxide hydroxide are formed in the waste liquid. When the temperature of the waste liquid is reduced to 5 (rc or less; t-knife is separated from the oxide of tin and the oxychloride oxide. The working solid (10). C, the obtained solid tin oxide and hydroxide are dissolved in the ancestors. The concentration was 16 hours in 16 1281955 f potassium oxide solution for 10 hours. Then, the solid solution which was still cold-decomposed in the solution was removed. After the slave, the condition of the temperature of the tin-containing alkali solution i ° and the anode-anode potential difference was 3, The high temperature electrolytic reduction step is carried out = about ^, after, at this time, the tin content in the solution is less than 5 g / L, and 23 kg of metal tin can be obtained. The service example 4 is the same as the operation of the embodiment 3 After the tin oxide and hydroxide precipitate, 254 g of precipitate was taken, 63 6 g of activated carbon and 253.3 g of sodium carbonate were added, mixed and ground, and smelted at a high temperature of 95 〇t for 4 hours to obtain 58. 5 g of metal tin having a purity of 99·5%. Example 5: Similar to the operation of Examples 1 to 4, after separation of tin oxide and hydrogen·oxide precipitate by filtration, the precipitate is reduced by wet electrolysis or by fire. The metal smelting process produces metal tin, and the filtrate is neutralized with a concentration of about 3N sodium hydroxide solution and the pH is adjusted. About 11. The brown filter cake of brown iron, copper, tin, lead and other oxides and hydroxides and the light green filtrate containing sodium nitrate are formed in the filtrate, and 3 〇〇m 1 pale green filtrate is obtained, which can be prepared by evaporation crystallization. Approximately 2Gg of light green or yellowish oleic acid was obtained. The atomic absorption spectrum (A, A) was used to analyze the heavy metal content. The result was ^___ 5 tiger color Cu (ppm) Fe (ppm) Sn (ppm) Pb(ppm) - 1 light green 25. 84 22. 61 ND ND 2 light green ND 14. 89 ND ND 3 light yellow ND 3. 67 ND ND__ Example 6 ·· 17 1281955 Same as Example 5' in transition separation After obtaining a brown cake containing iron, copper, tin and hydroxide, the brown cake is dissolved in a dilute sulfuric acid solution having a concentration of about 1: to form a micro-brown green solution, and the cathode-anode potential difference yv and temperature 15t Under the condition of electrolysis 2 Xiaori Temple, the copper ions in the solution are almost completely electrolytically reduced to metallic copper, and the solution becomes a green solution containing ferrous sulfate. The above embodiment is only an exemplary example of the present technology, and it is not used. The invention is defined in a specific form, and those skilled in the art are aware of the invention. Any modifications or changes shall be made in accordance with this, and such modifications or changes shall be included in the scope of the patent application scope of the present application. [Simplified description of the drawings] (1) The first part of the drawing is a schematic diagram of the process of the present invention. .

1818

Claims (1)

1281955 拾、申請專利範圍 1、一種剝錫鉛廢液之處理方法,其包括: 氧化步驟:在高溫下將錫離子與錯離子氧化成為錫、 鉛之氧化物及氫氧化物沈澱物; 固液分離步驟:將氧化舟驟^ 乳化步驟所得之錫、鉛之氧化物及 氫氧化物沈澱物加以固液分離; 還原步驟:將固液分離舟5取 從刀離步驟所得之固態錫與鉛之氣化 物及氫氧化物還原成為金屬錫或錫鉛合金; _回收步驟:將固液分離步驟所產生之濾液以驗中和後 ,經過濾、療發結晶、加酸溶解、萃取、電解還原 反應等程序时製得金屬銅、硫、 、氨水、硕酸鈉或硝酸鉀等。 亞鐵、硫酸鐵 上如申請專利範圍第1項的剝錫錯廢液之處理方法 用其中氧化步驟乃在45到1⑽的溫度範圍内進行氧;^ 3、 如申請專利範圍第1或 ^- 甘士 t 一 、的制錫斜廢液之處理 方法,”中氧化步驟乃在80到105 化作用。 匕的/皿度粑圍内進行氧 4、 如甲請專利範圍第上項的剝 ,直中ϋ仆丰挪 吻私廢液之處理方法 ,、中虱化步驟乃利用通氣氧化方法進行。 万忐 5、 如申請專利範圍第1項的剝錫:麻"♦ ,呈φ翁儿止口尾液之處理方、、表 ,、中虱化步驟乃利用化學氧化方法進行。 方法 6、 如中請專利範圍第i項的I W乾廢液之處理方法 19 1281955 ,其中氧化步驟乃利用電解氧化一 7、 如申請專利範圍第丄項:。 ’其中氧化步驟乃利用通氣氧化 ^廢液之處理方法 解氧化方法合併進行。 '化學氧化方法及電 8、 如申請專利範圍第4或7 方法,其中通氣氧化方法包括通入氧、錯廢液之處理 9、 如申請專利範圍第4或二:到廢液中。 方法’其中通氣氧化方法包括通入空氣:錫錯廢液之處理 1 〇、如申請專利範圍第5或/項I液中。 理方法,纟中化學氧化方法包括對、、二錫氣廢液之處 11、如中請專利範圍第5或:/項=了:發濃縮。 理方法…化學氧化方法包括直接二的::錯廢液之處 。 钱添加濃硝酸到廢液中 1 2、如申請專利範圍第 方法,其中可使用濃度介於5〇 液中。 1 1項的剝錫斜廢液之處理 至100%的濃硝酸來添加到廢 理方法,6. 0V之間 、如申請專利範圍第6或 其中電解氧化方法之陰陽 7項的剝錫鉛廢液之處 極電位差保持在2.0到 %哪狗曆》夜之處理; 法,在氧化步驟期間,可視需要、禾★人# △ 祝而要添加含硫酸根離子的化^ 物以促使船離子形成硫酸錯晶體。 1 5、如申請專利範圍第]4馆&立丨^ 囷乐1 4項的剝錫鉛廢液之處3 方法,其中该含硫酸根離子的化合物為硫酸。 20 1281955 16、 如申請專利範圍第14項的剝锡錯廢液之處理 方法,其中該含硫酸根離子的化合物為硫酸鈉。 17、 如申請專利範圍第14項的剝錫錯廢液之處理 方法,其中該含硫酸根離子的化合物為硫酸鉀。 、如申請專利範圍第工項的剝錫錯廢液之處理方 其中在還原步驟中,添加含碳粉末之活性碳。 19、如申請專利範圍第!項的剝锡錯廢:之處理方 其中在還原步驟中,添加含碳粉末之焦碳。 2 0、如申請專利範圍第!項的剝錫錯廢液之處理方 其中在還原步驟中,添加含碳粉末之石黑。 2 1、如申請專利範圍第丄項的剝锡錯廢液之處理方 其中在還原步驟中,添加含碳粉末之活性碳、焦碳、 石墨的混合物。 A « 2 2 :如申請專利範圍第1項的剝錫錯廢液之處理方-法,其中還原步驟中添加有碳酸鈉以進行高溫冶練。 2 3、如申請專利範圍第丄項的剝錫錯廢液之處理方 法’其中還原步驟乃是在6〇"H2G(rC的溫度範圍 _ 冶煉。 2 4、如申請專利範圍第1或2 3項的剝錫錯廢液之. 處理方法’其中還原步驟乃是在謂爿咖t的溫度範圍 内進行冶煉。 · 2 5、如申請專利範圍第丄項的剝錫鉛廢液之處理方… 法’其中還原步驟乃是以座法電解還原’先利用強鹼㈣—’ 與錯之氧化物及氫氧化物沈殿物溶解後,再進行電解還原 法 法 法 法1281955 Picking up, applying for a patent scope 1. A method for treating a tin-lead waste liquid, comprising: an oxidation step: oxidizing tin ions and a stray ion into a tin, a lead oxide, and a hydroxide precipitate at a high temperature; Separation step: solid-liquid separation of tin, lead oxide and hydroxide precipitate obtained by the oxidation step emulsification step; reduction step: taking the solid-liquid separation boat 5 from the solid-state tin and lead obtained by the knife-off step The vapor and hydroxide are reduced to metal tin or tin-lead alloy; _ recovery step: the filtrate produced by the solid-liquid separation step is neutralized, filtered, crystallized, acid-dissolved, extracted, and electrolyzed. When the program is completed, copper, sulfur, ammonia, sodium sulphate or potassium nitrate is obtained. The treatment method of the ferrous iron and the ferric sulphate in the stripping waste liquid according to the first application of the patent scope 1 wherein the oxidizing step is carried out in the temperature range of 45 to 1 (10); ^ 3, as in the patent application range 1 or ^- Gans t. The treatment method of tin-making oblique waste liquid, "the oxidation step is carried out at 80 to 105. 匕 / / 皿 进行 进行 氧 氧 氧 氧 氧 、 、 、 、 、 , , , , The method of treating the private waste liquid in the straight ϋ 丰 挪 挪 吻 , , , , , , 乃 乃 乃 乃 忐 忐 忐 忐 忐 忐 忐 忐 忐 忐 、 、 、 、 、 、 、 、 、 、 、 、 、 、 、 、 、 、 、 、 、 The process of treating the tail liquid, the table, and the middle gasification step are carried out by a chemical oxidation method. Method 6, such as the treatment method of the IW dry waste liquid of the scope of the patent item 19 1281955, wherein the oxidation step is utilized Electrolytic oxidation No. 7, as in the scope of the patent application: [The oxidation step is carried out by a combination of aeration oxidation and waste liquid treatment methods. 'Chemical oxidation method and electricity 8, as claimed in the scope of the fourth or seventh Method, its The aeration oxidation method includes the treatment of introducing oxygen and wrong waste liquid, as in the fourth or second application of the patent scope: into the waste liquid. The method of 'ventilation oxidation includes air treatment: treatment of tin wrong waste liquid 1 如Apply for the scope of patent No. 5 or /I. In the chemical method, the chemical oxidation method in the sputum includes the right point of the bismuth, and the tin sulphur waste liquid, as in the patent scope 5 or: / item =: concentrating. The chemical oxidation method includes direct two:: wrong waste liquid. Money is added with concentrated nitric acid to the waste liquid 1 2. As in the patent application method, the concentration can be used in 5 〇 liquid. The treatment of the stripping tin waste liquid to 100% concentrated nitric acid is added to the waste treatment method, between 6.0 V, as in the patent application range 6 or in the electrolytic oxidation method, the yin and yang lead stripping lead waste liquid The extreme potential difference is maintained at 2.0 to % of the dog's calendar. In the oxidation step, during the oxidation step, it is necessary to add the sulfate ion-containing chemical to the ship ion to form the sulfuric acid miscrystal. 1 5, if the scope of application for patents] &立丨^ 囷乐1 4 stripping lead waste liquid 3 method, wherein the sulfate ion-containing compound is sulfuric acid. 20 1281955 16. The stripping waste liquid of claim 14 The treatment method, wherein the sulfate ion-containing compound is sodium sulfate. 17. The method for treating a stripping waste liquid according to claim 14 wherein the sulfate ion-containing compound is potassium sulfate. The treatment of the stripping waste liquid in the range of the work item, wherein in the reduction step, the activated carbon containing the carbon powder is added. 19. As claimed in the patent scope! The stripping of the item is the treatment of the waste. In the reduction step, the coke of the carbonaceous powder is added. 2 0, such as the scope of patent application! Treatment of the stripping waste liquid in the item In the reduction step, the stone black containing the carbon powder is added. 2 1. The treatment of the stripping waste liquid according to the scope of the patent application. In the reduction step, a mixture of activated carbon, coke and graphite containing carbon powder is added. A « 2 2 : The method of treating the stripping waste liquid of the first application of the patent scope, wherein sodium carbonate is added in the reduction step for high temperature smelting. 2 3. The treatment method for stripping the wrong waste liquid according to the scope of the patent application s' wherein the reduction step is at 6 〇 "H2G (rC temperature range _ smelting. 2 4, as claimed in the scope of the first or second The three methods of stripping the wrong waste liquid. Treatment method 'The reduction step is to carry out the smelting within the temperature range of the temperature. · 2 5. The treatment of the stripping lead waste liquid according to the scope of the patent application The method of 'reduction step is to use the method of electrolysis to reduce the 'first use of strong alkali (four)-' and the oxides and hydroxides dissolved in the dissolved matter, then the electrolytic reduction method 21 2 1281955 處理方法 2 7 處理方法 2 8 處理方法 2 9 如申請專利範圍第U25項的刻錫錯廢液之- 其中δ亥強驗為氫氧化納。 如申請專利範圍第Η25項的剝錫錯廢液之| 其中该強驗為氫氧化鉀。 如申請專利範圍第!或25項的制錫錯廢液之 其中該強鹼為氫氧化鈉及氫氧化鉀之混合物。 ‘ 士口申請專利範圍第2 5項的剝錫錯廢液口之處理-,,其中該強鹼為鹼當量濃度介於2〇到7·⑽的溶液。 广理如申請專利範圍第1或25項的剥錫錯廢液之 處理方法,其中該溶解乃是在室溫到靴的溫度範 订0 廢、、如中請專利範圍第1或25或3 ◦項的剝錫# _ &理方法,其中該溶解乃是在8 - 範圍内進行。 』u的,皿度 3 2 、如申請專利範圊篦 處理方法,i中於,或2 5項的剝錫鉛廢液之 ”中於通原步驟乃是在50 n 内進行電解還原。 d皿度乾圍― 3 3、如申請專利範圍第 卢m t^ 乐丄次2 5項的剝錫鉛廢液 、 γέ is y- 1 ς 還原%r的陰%極電位差 係保持在1· 5到7. 〇V之間。 左 · 3 4、如申請專利範圍第1項的4 … 法,其中於逖原步驟所回收製得 乃 、隹一丰产六分 孟屬錫或錫錯合金,® 進一 y在,丨1 I亞錫溶液中電解 1月农从传鬲純度錫。 22 1281955 3 5、如申請專利範圍第1項的剝錫鉛廢液之處理方 , 法,其中於回收步驟中,該鹼中和程序為利用鹼中和固液 · 分離步驟所產生的濾液並調整pH值為8至13。 3 6、如申請專利範圍第1或3 5項的剝錫鉛廢液之 -處理方法,其中回收步驟將固液分離步驟所產生之濾液以 驗中和後,經過濾分離得含硝酸鹽的濾液及含銅及鐵等氧 化物及氫氧化物沈澱物的濾餅。 . 3 7、如申請專利範圍第1或3 6項的剝錫鉛廢液之 , 處理方法,該含硝酸鈉、硝酸鉀的濾液經蒸發結晶製得硝 酸鈉、硝酸鉀晶體。 3 8、如申請專利範圍第χ或3 6項的剝錫鉛廢液之 處理方法,該含鋼及鐵等氧化物及氫氧化物沈澱物之濾餅 — 以稀硫酸液溶解後,利用萃取法製得硫酸銅、硫酸亞鐵、 硫酸鐵。 — 3 9、如申請專利範圍第1或3 δ項的剝錫鉛廢液之 處理方法,該含銅及鐵等氧化物及氫氧化物沈澱物之濾餅 以稀硫酸液溶解後,利用置換法製得金屬銅粉末及硫酸亞·· 鐵0 •,干。间矛_L或;j b工貝的剌蜴鉛廢液之 處理方法’ 5玄含銅及鍾^装t 鐵寺虱化物及氫氧化物沈澱物之濾餅 以稀硫酸液〉谷解後’利用雷念2 ^ 〜用電解逖原法製得金屬銅及硫酸亞 鐵0 2321 2 1281955 Treatment Method 2 7 Treatment Method 2 8 Treatment Method 2 9 If you apply for the patented U25 item, you can find the sodium hydroxide solution. For example, in the case of claim 25, the stripping of the wrong waste liquid | wherein the strong test is potassium hydroxide. Such as the scope of patent application! Or 25 of the tin-making waste liquids, wherein the strong base is a mixture of sodium hydroxide and potassium hydroxide. ‘Shikou applied for the treatment of stripping the wrong waste liquid port of item 25 of the patent scope, wherein the strong base is a solution having a base equivalent concentration of 2〇 to 7·(10). For example, the processing method of the stripping waste liquid of claim 1 or 25, wherein the dissolving is the temperature at the room temperature to the temperature of the boot, and the patent range is 1 or 25 or 3剥 的 # # # # # # # # # # # # # # # # # # # # # # # # # 』u, the degree of the container 3 2, such as the application of the patent treatment method, i in, or 25 of the stripping lead waste liquid" in the original step is electrolytic reduction within 50 n. d The dryness of the dish - 3 3, such as the patent scope of the second mt ^ 丄 丄 2 2 2 2 2 、 、 、 、 、 、 、 、 、 、 、 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原 还原7. Between 〇V. Left · 3 4. For example, the 4 ... method of claim 1 of the patent scope, in which the 逖 步骤 step is recovered, and the 隹 丰 丰 产 六 六 孟 孟 或 或 或 , , , , , , y, in the 丨1 I stannous solution electrolysis in January, the agricultural purity of the tin. 22 1281955 3 5, as claimed in the scope of claim 1 of the stripping lead waste liquid treatment, the method, in the recovery step, The alkali neutralization procedure is to use a base to neutralize the filtrate produced by the solid-liquid separation step and adjust the pH to 8 to 13. 3 6. Treatment of the stripping lead waste liquid according to claim 1 or 3 a method, wherein the recovery step comprises neutralizing the filtrate produced by the solid-liquid separation step, and separating the nitrate-containing filtrate and the copper by filtration a filter cake of iron oxides and hydroxide precipitates. 3 7. For the stripping lead waste liquid of the first or third paragraph of the patent application, the treatment method, the filtrate containing sodium nitrate and potassium nitrate is evaporated Crystallization to obtain crystals of sodium nitrate and potassium nitrate. 3 8. A method for treating a stripping lead waste liquid according to the third or sixth aspect of the patent application, the filter cake containing oxides and hydroxide precipitates such as steel and iron - After dissolving in dilute sulfuric acid solution, copper sulfate, ferrous sulfate and ferric sulfate are obtained by extraction method. - 39. Treatment method for stripping lead waste liquid according to the first or third δ of the patent application scope, the copper-containing and After the filter cake of iron oxide and hydroxide precipitate is dissolved in dilute sulfuric acid solution, the metal copper powder and the sulfuric acid powder are prepared by the replacement method, and the dry spear _L or jb The treatment method of lead waste liquid ' 5 Xuan copper and bell ^ installed t iron temple sulphate and hydroxide precipitate filter cake with dilute sulfuric acid solution> trough solution 'utilizes Lei Nian 2 ^ ~ using electrolytic 逖 original method Metallic copper and ferrous sulfate 0 23
TW92104369A 2003-03-03 2003-03-03 Treatment method of waste tin lead stripping solution TWI281955B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
TW92104369A TWI281955B (en) 2003-03-03 2003-03-03 Treatment method of waste tin lead stripping solution

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
TW92104369A TWI281955B (en) 2003-03-03 2003-03-03 Treatment method of waste tin lead stripping solution

Publications (2)

Publication Number Publication Date
TW200417626A TW200417626A (en) 2004-09-16
TWI281955B true TWI281955B (en) 2007-06-01

Family

ID=38777567

Family Applications (1)

Application Number Title Priority Date Filing Date
TW92104369A TWI281955B (en) 2003-03-03 2003-03-03 Treatment method of waste tin lead stripping solution

Country Status (1)

Country Link
TW (1) TWI281955B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102616971A (en) * 2011-12-14 2012-08-01 山东建筑大学 Comprehensive treatment method of laboratory acidic tin plating waste liquid

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TW201313911A (en) * 2011-09-29 2013-04-01 Hui-Ling Wang Method of recycling tin and copper metals from acidic waste liquid
CN103523947A (en) * 2013-08-26 2014-01-22 赣州聚环科技有限公司 Solder removing waste liquid regeneration treatment method
CN106495404B (en) * 2016-11-29 2019-08-20 湖南平安环保股份有限公司 A kind of processing method of the high salinity cupric organic wastewater of highly acidity
CN115449634B (en) * 2022-08-26 2024-02-09 湖北永绍科技股份有限公司 Treatment method for recycling tin stripping waste liquid

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102616971A (en) * 2011-12-14 2012-08-01 山东建筑大学 Comprehensive treatment method of laboratory acidic tin plating waste liquid

Also Published As

Publication number Publication date
TW200417626A (en) 2004-09-16

Similar Documents

Publication Publication Date Title
CN102676822B (en) A method for treating waste printed circuit boards without incineration and without cyanide
CN101575715B (en) Method for extracting valuable metals from electronic waste
US10597753B2 (en) Systems and methods of efficiently recovering precious metals using an alkaline leach, ultrasound, and electrolysis
EP3715484B1 (en) Method for treating lithium ion battery waste
JP7198081B2 (en) Valuable metal recovery method
US20180073156A1 (en) Method for producing copper and apparatus for producing copper
CN101519727A (en) A treatment method for zinc smelting by-products
US20180230571A1 (en) Systems and methods of recovering precious metals and extracting copper from diverse substances
EP2147128A1 (en) Process for producing pure metallic indium from zinc oxide and/or solution containing the metal
CN113195121A (en) Method for recovering valuable metals
Keskitalo et al. Analysis of key patents of the regeneration of acidic cupric chloride etchant waste and tin stripping waste
TWI281955B (en) Treatment method of waste tin lead stripping solution
JP7317761B2 (en) How to dispose of lithium-ion battery waste
JP7383550B2 (en) Manganese ion removal method
EP3575420A1 (en) Bismuth purification method
CN104531991A (en) Low-grade copper ore bioleaching solution treatment method
JP3113307B2 (en) Method for separating and recovering zinc and manganese from waste dry batteries
CN104152701B (en) The method that tin is reclaimed from tin refinement slag
WO2021061184A1 (en) Systems and methods of efficiently recovering precious metals using an alkaline leach, ultrasound, and electrolysis
JPH04191340A (en) Production of high purity tin
JP2002212650A (en) Method for recovering platinum group metals from metal electrodes
JPH11229056A (en) Method for producing high purity nickel aqueous solution
JP3080947B1 (en) Electric furnace dust treatment method
JP2002194581A (en) Method for recovering platinum group metals from metal electrodes
JP6750454B2 (en) Method for removing impurities from bismuth electrolyte

Legal Events

Date Code Title Description
MK4A Expiration of patent term of an invention patent