TW202229172A - Method of recycling ammonia from wasting buffered oxide etchants and preparing fluoro-salt crystals and solid silicon dioxide - Google Patents

Method of recycling ammonia from wasting buffered oxide etchants and preparing fluoro-salt crystals and solid silicon dioxide Download PDF

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TW202229172A
TW202229172A TW110102204A TW110102204A TW202229172A TW 202229172 A TW202229172 A TW 202229172A TW 110102204 A TW110102204 A TW 110102204A TW 110102204 A TW110102204 A TW 110102204A TW 202229172 A TW202229172 A TW 202229172A
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ammonia
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TWI797542B (en
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顧偉民
杜建成
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雷賽克實業股份有限公司
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Abstract

The invention provides a method of recycling ammonia from wasting buffered oxide etchants and preparing fluoro-salt crystals and solid silicon dioxide, which comprises the following steps: introducing waste BOE silicon dioxide etching solution and sodium hydroxide into an ammonia generator, By heating the reaction liquid in the ammonia generator, the ammonia stripped by air is introduced into the ammonia absorption tower, and the ammonia absorption liquid is diffused and absorbed; and when the ammonia concentration of the reaction liquid in the ammonia generator is less than a certain concentration, it is transported to the pH adjustment tank uses hydrofluoric acid to adjust the PH value of the reaction solution, and introduces it into the solid-liquid separation and concentration equipment to obtain fluoride salt crystals and silicon dioxide solids. The invention can synthesize waste (water) liquid containing hydrofluoric acid in the wet silicon dioxide layer etching process of silicon wafer manufacturing. Compared with the conventional method, it focuses on calcium fluoride, sodium fluorosilicate, and sodium hexafluoroaluminate. These three categories can recover ammonia and prepare fluoride salt crystals and silicon dioxide solids.

Description

由廢BOE二氧化矽蝕刻液中回收氨且製備氟鹽晶體與二氧化矽固體的方法Method for recovering ammonia from waste BOE silicon dioxide etching solution and preparing fluorine salt crystal and silicon dioxide solid

本發明係一種廢矽晶圓蝕刻液回收再利用的方法,特別係關於一種可從廢BOE二氧化矽蝕刻液中回收氨,同時從回收過程中逐漸得到高純度的氟鹽與二氧化矽的方法。The invention relates to a method for recycling waste silicon wafer etching solution, in particular to a method for recovering ammonia from waste BOE silicon dioxide etching solution and gradually obtaining high-purity fluorine salt and silicon dioxide from the recycling process. method.

矽晶圓製程中的濕式二氧化矽層蝕刻(SiO 2Etching)製程,常使用的化學藥劑有氫氟酸(HF)溶液與緩衝氧化物蝕刻劑(Buffered Oxide Etchant,簡稱BOE)。 In the wet silicon dioxide layer etching (SiO 2 Etching) process in the silicon wafer process, the commonly used chemicals are hydrofluoric acid (HF) solution and buffered oxide etchant (Buffered Oxide Etchant, referred to as BOE).

BOE二氧化矽蝕刻液為氫氟酸(HF)與氟化氨(NH 4F)的混合液,具有緩衝的效果,其蝕刻二氧化矽層的化學反應式如下: SiO 2+ 4HF + 2NH 4F → (NH 4) 2SiF 6+ 2H 2O 傳統使用氫氟酸(HF)來蝕刻二氧化矽層的機制中,決定蝕刻速率的是HF的濃度,若要能使HF濃度於蝕刻中保持穩定,需依賴NH 4F溶液提供大量的之F -離子來達到緩衝的效果,因此蝕刻速率就可保持穩定。 BOE silicon dioxide etching solution is a mixed solution of hydrofluoric acid (HF) and ammonium fluoride (NH 4 F), which has the effect of buffering. The chemical reaction formula of etching silicon dioxide layer is as follows: SiO 2 + 4HF + 2NH 4 F → (NH 4 ) 2 SiF 6 + 2H 2 O In the traditional mechanism of using hydrofluoric acid (HF) to etch silicon dioxide layers, the etch rate is determined by the concentration of HF. Stable, need to rely on NH 4 F solution to provide a large amount of F - ions to achieve the effect of buffering, so the etching rate can be kept stable.

目前矽晶圓製程中所產出的BOE廢(水)液,其成分中含有氨,且氨中的氮(N)可為水生植物的生長提供營養源,而使水生植物如海藻及水草大量繁殖,此將導致該水域生物缺氧,進而讓水中生物死亡。亦即,氨氮為水環境中重要監測汙染源之一,亦是導致水體優養化之主要營養源,具有強急毒性易造成水中生物立即性危害,高濃度之氨氮廢水一但排入河川湖泊,極易導致水質迅速惡化,或微生物及藻類大量繁殖,使水體發生優養化及生態平衡的失調現象。因此,環保署已針對廢水的氨氮排放量進行管制,而氨氮回收目前已成為一個重要的課題。The BOE waste (water) liquid produced in the current silicon wafer process contains ammonia, and the nitrogen (N) in ammonia can provide a nutrient source for the growth of aquatic plants, which makes aquatic plants such as seaweed and aquatic plants abundant Reproduction, which will lead to the lack of oxygen in the waters, and then let the aquatic life die. That is, ammonia nitrogen is one of the important monitoring pollution sources in the water environment, and it is also the main nutrient source that leads to the optimization of water bodies. It has strong acute toxicity and can easily cause immediate harm to aquatic organisms. Once high-concentration ammonia nitrogen wastewater is discharged into rivers and lakes, It is easy to lead to rapid deterioration of water quality, or the proliferation of microorganisms and algae, resulting in the phenomenon of optimal nutrient and ecological balance disorders in water bodies. Therefore, the Environmental Protection Agency has regulated the discharge of ammonia nitrogen from wastewater, and the recovery of ammonia nitrogen has now become an important issue.

在矽晶圓製造的濕式二氧化矽層蝕刻(SiO 2Etching)製程中,所產出的含有氫氟酸廢(水)液,在我國已有相關的回收再利用專利被申請如下表: 專利編號 公告/公開日 申請號 專 利 名 稱 I574923 2017/03/21 105110725 一種由含氫氟酸、六氟矽酸及六氟鋁酸之廢水生產氟化鈣之方法 I529131 2016/04/11 103130633 自氫氟酸廢液回收氟矽酸鈉之方法 I518041 2016/01/21 103128491 自氫氟酸廢液回收氟鋁酸鈉之方法 I449668 2014/08/21 101112494 氟化鈣製備方法 In the wet silicon dioxide layer etching (SiO 2 Etching) process of silicon wafer manufacturing, the produced waste (water) liquid containing hydrofluoric acid has been applied for relevant recycling patents in China as follows: Patent number Announcement/Public Date Application Number patent name I574923 2017/03/21 105110725 A method for producing calcium fluoride from wastewater containing hydrofluoric acid, hexafluorosilicic acid and hexafluoroaluminate I529131 2016/04/11 103130633 Method for recovering sodium fluorosilicate from hydrofluoric acid waste liquid I518041 2016/01/21 103128491 Method for recovering sodium fluoroaluminate from hydrofluoric acid waste liquid I449668 2014/08/21 101112494 Preparation method of calcium fluoride

專利編號I574923為一種由含氫氟酸、六氟矽酸及六氟鋁酸之廢水生產氟化鈣之方法,添加氟化鉀於包含氫氟酸、六氟矽酸及六氟鋁酸之廢水,藉由氨水、氫氧化鈣及絮凝劑等藥劑輔助,經過沉澱過濾過程,生產純度良好之氟化鈣,特別可用於處理廢LCD面板玻璃蝕刻液以生產氟化鈣。Patent No. I574923 is a method for producing calcium fluoride from wastewater containing hydrofluoric acid, hexafluorosilicic acid and hexafluoroaluminate, adding potassium fluoride to the wastewater containing hydrofluoric acid, hexafluorosilicic acid and hexafluoroaluminate , With the aid of ammonia water, calcium hydroxide and flocculants, through the process of precipitation and filtration, calcium fluoride with good purity can be produced, especially for the treatment of waste LCD panel glass etching solution to produce calcium fluoride.

專利編號I529131為一種自氫氟酸廢液回收氟矽酸鈉之方法,將氫氟酸廢液與矽精礦混合,於20~50°C下反應1~4小時,生成並過濾第一混合物,獲得碳化矽及含氟矽酸之溶液,並將鈉鹽與該含氟矽酸之溶液混合,於20~50°C下反應1~4小時。可利用另一廢棄物自氫氟酸廢液中沉出氟,達到降低氫氟酸廢液之處理成本功效。Patent No. I529131 is a method for recovering sodium fluorosilicate from hydrofluoric acid waste liquid. The hydrofluoric acid waste liquid is mixed with silicon concentrate, reacted at 20 to 50 ° C for 1 to 4 hours, and the first mixture is generated and filtered. , obtain a solution of silicon carbide and fluorosilicic acid, mix sodium salt with the solution containing fluorosilicic acid, and react at 20 to 50° C. for 1 to 4 hours. Another waste can be used to precipitate fluorine from the hydrofluoric acid waste liquid, so as to achieve the effect of reducing the treatment cost of the hydrofluoric acid waste liquid.

專利編號I518041為一種自氫氟酸廢液回收氟鋁酸鈉之方法,將鎳鋁精礦與含鈉鹼粉混合,於200~800°C下反應2~4小時,生成第一燒結物,將該第一燒結物浸入60~100°C的水中反應0.5~2小時,獲得鎳精礦及鋁酸鈉溶液,將鹼性物質加入該鋁酸鈉溶液中,獲得鋁酸鈉貴液與鈉鹽混合,於60~100°C下反應1~4小時。利用另一廢棄物自該氫氟酸廢液中將氟以氟鋁酸鈉的形式沉出,達到降低氫氟酸廢液之處理成本效果。Patent number I518041 is a kind of method that reclaims sodium fluoroaluminate from hydrofluoric acid waste liquid, mixes nickel-aluminum concentrate with sodium-containing alkali powder, reacts at 200~800 ℃ for 2~4 hours, generates the first sinter, This first sinter is immersed in the water of 60~100 ℃ and reacts 0.5~2 hour, obtains nickel concentrate and sodium aluminate solution, adds alkaline substance in this sodium aluminate solution, obtains sodium aluminate precious liquid and sodium The salts are mixed and reacted for 1 to 4 hours at 60 to 100°C. Using another waste to precipitate fluorine in the form of sodium fluoroaluminate from the hydrofluoric acid waste liquid, the effect of reducing the treatment cost of the hydrofluoric acid waste liquid is achieved.

專利編號I449668為一種氟化鈣製備方法,提供含有HF酸之廢液,將該廢液中之HF酸含量控制在一預定濃度範圍,添加Ca源至該廢液,同時控制Ca與HF酸之反應溫度於一預定溫度範圍,生成CaF 2。此氟化鈣製備方法之製程簡單、成本低廉,CaF 2製備速度高,且具有極高且穩定純度與品質。 Patent No. I449668 is a method for preparing calcium fluoride, which provides a waste liquid containing HF acid, controls the HF acid content in the waste liquid to a predetermined concentration range, adds a Ca source to the waste liquid, and simultaneously controls the relationship between Ca and HF acid. The reaction temperature is within a predetermined temperature range to generate CaF 2 . The preparation method of calcium fluoride has the advantages of simple process, low cost, high preparation speed of CaF 2 and extremely high and stable purity and quality.

由上,可發現目前已核准的專利其回收後的產品均著重於氟化鈣、氟矽酸鈉、氟鋁酸鈉這三大類,唯不見氨回收後的產品,可知這些專利方法並不適用於含有氟化銨(NH 4F)的氫氟酸(HF)廢液。 From the above, it can be found that the recovered products of the currently approved patents focus on the three categories of calcium fluoride, sodium fluorosilicate, and sodium fluoroaluminate, but the products after ammonia recovery are not seen. It can be seen that these patented methods are not applicable. in hydrofluoric acid (HF) waste solution containing ammonium fluoride (NH 4 F).

本發明的目的在提供一種可由含有銨的廢二氧化矽蝕刻液,從中回收氨且製備氟鹽固體與二氧化矽(SiO 2)的方法,具有先前專利所沒有可回收氨的優點,同時又保有可回收氟(F)與矽(Si)製成相關化合物的優勢。 The object of the present invention is to provide a method for recovering ammonia from waste silicon dioxide etching solution containing ammonium and preparing fluoride salt solid and silicon dioxide (SiO 2 ). Retain the advantage of recycling fluorine (F) and silicon (Si) into related compounds.

為了達成前述目的,本發明提供一種由廢BOE二氧化矽蝕刻液中回收氨且製備氟鹽晶體與二氧化矽固體的方法,包括下列步驟(A)~(D)。In order to achieve the aforementioned objects, the present invention provides a method for recovering ammonia from waste BOE silicon dioxide etching solution and preparing fluorine salt crystals and silicon dioxide solids, comprising the following steps (A) to (D).

步驟(A):將廢BOE二氧化矽蝕刻液導入氨產生器中,再投入氫氧化鈉(NaOH)提高廢BOE二氧化矽蝕刻液的pH值至11以上(以下稱反應液),將反應液增溫(採間接加熱使用蒸氣或熱煤油不要直接與反應液接觸)。採取空氣吹脫法去除氨,使用氨氣敏電極或氨氮試紙,確認反應液氨氮的殘留量<10 ppm後才可進行下一步驟(B)。此階段反應過程中,要隨時添加氫氧化鈉,確保反應液的pH>11。亦即,空氣吹脫法係在鹼性條件下用空氣吹脫(空氣作為載體)利用廢水中所含氨氮實際濃度與平衡濃度之間存在差異,經由鹼性環境將氨離子轉為氨分子,透過其揮發性氨氣成為氣體,達到收集氨的目的。 吹脫氨後,反應液剩餘的氟離子會和鈉離子結合成氟化鈉,且廢液中的矽會因氟矽酸鈉(Na 2SiF 6)在高pH環境下會分解的特性,無法形成氟矽酸鈉(Na 2SiF 6)的沉澱物,而是變成外觀為白色半透明果凍狀的無定型固體。 Step (A): Introduce the waste BOE silicon dioxide etching solution into the ammonia generator, and then add sodium hydroxide (NaOH) to increase the pH value of the waste BOE silicon dioxide etching solution to above 11 (hereinafter referred to as the reaction solution), and react Liquid warming (use steam or hot kerosene for indirect heating, do not directly contact the reaction liquid). Use the air stripping method to remove ammonia, use an ammonia gas sensing electrode or ammonia nitrogen test paper, and confirm that the residual amount of ammonia nitrogen in the reaction liquid is less than 10 ppm before proceeding to the next step (B). During the reaction at this stage, sodium hydroxide should be added at any time to ensure that the pH of the reaction solution is greater than 11. That is, the air stripping method uses air stripping (air is used as a carrier) under alkaline conditions to utilize the difference between the actual concentration and equilibrium concentration of ammonia nitrogen contained in wastewater, and convert ammonia ions into ammonia molecules through an alkaline environment. Through its volatile ammonia into gas, the purpose of collecting ammonia is achieved. After stripping off ammonia, the remaining fluoride ions in the reaction liquid will combine with sodium ions to form sodium fluoride, and the silicon in the waste liquid will be decomposed in high pH environment due to the characteristics of sodium fluorosilicate (Na 2 SiF 6 ), which cannot be used. A precipitate of sodium fluorosilicate (Na 2 SiF 6 ) was formed, instead becoming an amorphous solid with a white translucent jelly-like appearance.

收集空氣吹脫後散逸的氨,於氨吸收塔中,可利用水或鹽酸吸收吹脫出來的氨氣,分別製成氨水或氯化銨溶液。The ammonia dissipated after air stripping is collected, and in the ammonia absorption tower, water or hydrochloric acid can be used to absorb the stripped ammonia gas, respectively, to make ammonia water or ammonium chloride solution.

步驟(B):使用氫氟酸(HF)將步驟(A)的反應液之pH值下調到6~8之間。Step (B): use hydrofluoric acid (HF) to adjust the pH of the reaction solution in step (A) to between 6 and 8.

步驟(C):將步驟(B)的反應液再以固液分離設備去做分離,固體可得到矽的沉澱物,液體可得到澄清透明含有氟化鈉的液體。Step (C): The reaction solution in step (B) is separated by a solid-liquid separation device, the solid can obtain a silicon precipitate, and the liquid can obtain a clear and transparent liquid containing sodium fluoride.

步驟(D):將步驟(C)產生的矽沉澱物經過水洗程序洗淨,去除殘留的氟化鈉水溶液後,送入烘乾設備中,以100℃以上的溫度烘乾,去除所含的水分,使之成為白色的二氧化矽粉末固體。Step (D): The silicon precipitate produced in step (C) is washed with a water washing procedure, and after removing the residual sodium fluoride aqueous solution, it is sent to a drying equipment, and dried at a temperature above 100 ° C to remove the contained sodium fluoride solution. moisture, making it a white silica powder solid.

步驟(E):將步驟(C)分離出來的含有氟化鈉的液體,送入濃縮設備中,藉以去處除大量的水分,使氟化鈉液體達到過飽和狀態進而產出氟化鈉晶體。Step (E): The sodium fluoride-containing liquid separated in step (C) is sent to the concentration equipment, so as to remove a large amount of water, so that the sodium fluoride liquid reaches a supersaturated state to produce sodium fluoride crystals.

在本發明中,步驟(A)所得的氨水再提濃後可自用或販售,步驟(C)分離出來的含有氟化鈉的液體可再濃縮成氟化鈉晶體銷售,步驟(D)洗淨後之矽沉澱物經烘乾後可製成白色的二氧化矽使用。In the present invention, the ammonia water obtained in step (A) can be used or sold for personal use after being concentrated again, the liquid containing sodium fluoride separated in step (C) can be concentrated into sodium fluoride crystals for sale, and step (D) washing The cleaned silica precipitate can be made into white silica after drying.

以下,將參照圖1及圖2說明由廢BOE二氧化矽蝕刻液中回收氨且製備氟鹽晶體與二氧化矽固體的方法,於其中步驟S10及S50,可配合參照圖3,其顯示不同pH值與不同溫度條件下對氨分子與銨離子相對量的影響。請參閱圖1及圖2,步驟S10中,將廢BOE二氧化矽蝕刻液與氫氧化鈉同時加入氨產生器1中,氨產生器1中的液體以下稱此為反應液。Hereinafter, a method for recovering ammonia from waste BOE silicon dioxide etching solution and preparing fluorine salt crystals and silicon dioxide solid will be described with reference to FIGS. 1 and 2 , in which steps S10 and S50 can be referred to in conjunction with FIG. 3 , which are shown differently. Effects of pH and different temperatures on the relative amounts of ammonia molecules and ammonium ions. Please refer to FIG. 1 and FIG. 2 , in step S10 , the waste BOE silicon dioxide etching solution and sodium hydroxide are simultaneously added to the ammonia generator 1 , and the liquid in the ammonia generator 1 is hereinafter referred to as the reaction solution.

步驟S20中,使用鍋爐2產生的蒸汽間接加熱反應液,在高溫與高pH的環境下,反應液中的銨離子(NH 4 +)會變成氣態氨(NH 3)散逸出來。 NH 4F + NaOH → NaF + NH 3↑ + H 2O (NH 4) 2SiF 6+ 2NaOH → Na 2SiF 6+ 2NH 3↑ + 2H 2O In step S20, the reaction liquid is indirectly heated by the steam generated by the boiler 2. Under the environment of high temperature and high pH, the ammonium ions (NH 4 + ) in the reaction liquid will become gaseous ammonia (NH 3 ) and escape. NH 4 F + NaOH → NaF + NH 3 ↑ + H 2 O (NH 4 ) 2 SiF 6 + 2NaOH → Na 2 SiF 6 + 2NH 3 ↑ + 2H 2 O

步驟S30中,使用壓送型鼓風機3將空氣由氨產生器1下方送入,利用空氣吹脫法將反應液中的氨吹出,剩下的反應液成份,主要是氟化鈉與二氧化矽。In step S30, the pressure-feeding blower 3 is used to send air from below the ammonia generator 1, and the ammonia in the reaction solution is blown out by the air stripping method, and the remaining reaction solution components are mainly sodium fluoride and silicon dioxide. .

因氟矽酸鈉無法在鹼性的環境中存在,會分解為氟化鈉和二氧化矽,且在水(H 2O)的作用下,此時的矽沉澱物為白色半透明果凍狀的無定型固體。 Na 2SiF 6+ 4NaOH → 6NaF + SiO 2‧2H 2O Because sodium fluorosilicate cannot exist in an alkaline environment, it will decompose into sodium fluoride and silicon dioxide, and under the action of water (H 2 O), the silicon precipitate at this time is white and translucent jelly-like. Amorphous solid. Na 2 SiF 6 + 4NaOH → 6NaF + SiO 2 ‧2H 2 O

步驟S40中,將吹脫出來的氨氣導入氨吸收塔4中。In step S40, the stripped ammonia gas is introduced into the ammonia absorption tower 4.

步驟S50中,將步驟S40中吹出的氨氣,以氨吸收液吸收。如氨吸收液為水,使用冷卻的方式將氨吸收液(即水)的溫度降溫以利氨氣溶於氨吸收液(即水)中,所得的成品為氨水:H 2O + NH 3→ NH 4 ++ OH -(請參考圖2)。如氨吸收液為鹽酸,則所得成品為氯化銨溶液:HCl + NH 3→ NH 4 ++ Cl -In step S50, the ammonia gas blown out in step S40 is absorbed by the ammonia absorption liquid. If the ammonia absorption liquid is water, the temperature of the ammonia absorption liquid (i.e. water) is lowered by cooling to dissolve the ammonia gas in the ammonia absorption liquid (i.e. water), and the obtained product is ammonia water: H 2 O + NH 3 → NH 4 + + OH - (please refer to Figure 2). If the ammonia absorption liquid is hydrochloric acid, the obtained product is ammonium chloride solution: HCl + NH 3 → NH 4 + + Cl - .

步驟S60,儲放氨吸收液於氨吸收液儲存槽5供氨吸收塔4循環使用,當氨吸收液達到所需濃度時更換新的氨吸收液。In step S60, the ammonia absorption liquid is stored and stored in the ammonia absorption liquid storage tank 5 for the circulating use of the ammonia absorption tower 4, and the ammonia absorption liquid is replaced with a new ammonia absorption liquid when the ammonia absorption liquid reaches the required concentration.

步驟S70,吸收液吸附氨氣後溫度會提高,因而降低吸收效率,故預先準備冷卻設備,例如冰水機6,當氨吸收液為水時,作為降低氨吸收液(即水)的溫度之用,以利氨氣溶於氨吸收液(即水)中。In step S70, the temperature of the absorption liquid will increase after absorbing ammonia gas, thus reducing the absorption efficiency. Therefore, a cooling device, such as an ice water machine 6, is prepared in advance. Used to dissolve ammonia gas in ammonia absorption liquid (ie water).

步驟S80,使用氨氮試紙,或氨氣敏電極,監控氨產生器1內的反應液的氨氮濃度,當反應液的氨氮濃度<10 ppm時,將氨產生器1中的反應液,輸送到pH調整槽7中。Step S80, use ammonia nitrogen test paper or ammonia gas sensing electrode to monitor the ammonia nitrogen concentration of the reaction solution in the ammonia generator 1, and when the ammonia nitrogen concentration of the reaction solution is less than 10 ppm, transfer the reaction solution in the ammonia generator 1 to pH Adjust slot 7.

步驟S90,用氫氟酸(HF),調低pH調整槽7中反應液的pH值至6~8之間(最佳為7),其目的是將反應液內殘留過量的NaOH轉化成氟化鈉。 HF + NaOH → NaF + H 2O Step S90, use hydrofluoric acid (HF) to lower the pH value of the reaction solution in the pH adjustment tank 7 to between 6 and 8 (optimally 7), the purpose of which is to convert the excess NaOH remaining in the reaction solution into fluorine Sodium. HF + NaOH → NaF + H 2 O

步驟S100,將反應液導入固液分離設備,例如壓濾機8,固液分離以去除氟化鈉溶液中的矽沉澱物得到氟化鈉溶液半成品。In step S100, the reaction solution is introduced into a solid-liquid separation device, such as a filter press 8, for solid-liquid separation to remove silicon precipitates in the sodium fluoride solution to obtain a semi-finished sodium fluoride solution.

步驟S110,將氟化鈉溶液半成品輸送到濃縮設備,例如濃縮蒸發罐9,用以去除過多水份,提高氟化鈉濃度,進而達到一種氟化鈉固液相共存的過飽和溶液狀態。In step S110, the semi-finished product of the sodium fluoride solution is transported to a concentration device, such as a concentration evaporation tank 9, to remove excess water, increase the concentration of sodium fluoride, and then achieve a state of a supersaturated solution in which sodium fluoride coexists in solid and liquid phases.

步驟S120,將過飽和的氟化鈉溶液導入固液分離設備,例如離心脫水機10,經固液分離後得到的固體為氟化鈉晶體成品,分離出的液體可回收當濃縮設備的母液。In step S120, the supersaturated sodium fluoride solution is introduced into a solid-liquid separation device, such as the centrifugal dehydrator 10, the solid obtained after solid-liquid separation is a finished sodium fluoride crystal, and the separated liquid can be recovered as the mother liquor of the concentration device.

步驟S130,將步驟S100所得的矽沉澱物,加以水洗,水洗至水洗水殘留的F-離子濃度<10 ppm。前段水洗水氟離子濃度高可進濃縮設備回收,中後段水洗水則可進廢水廠。In step S130, the silicon precipitate obtained in step S100 is washed with water until the residual F-ion concentration in the washing water is less than 10 ppm. The high fluoride ion concentration in the front-end washing water can be recycled into the concentration equipment, and the middle and back-end washing water can be sent to the waste water plant.

步驟S140,將步驟S130洗淨後之矽沉澱物導入烘乾設備,例如烤箱11,用以處除去沉澱物的水份,使之成為純白色的二氧化矽粉末。In step S140 , the silicon precipitate washed in step S130 is introduced into a drying device, such as the oven 11 , to remove the water content of the precipitate and turn it into pure white silicon dioxide powder.

在另一實施例中,步驟S10中的氫氧化鈉(NaOH)可以氫氧化鉀(KOH)替代,即將廢BOE二氧化矽蝕刻液與氫氧化鉀同時加入氨產生器1中;最終,可於步驟S120得到氟化鉀(KF)的氟鹽晶體,並於步驟S140得到二氧化矽固體。In another embodiment, the sodium hydroxide (NaOH) in step S10 can be replaced by potassium hydroxide (KOH), that is, the waste BOE silicon dioxide etching solution and potassium hydroxide are added to the ammonia generator 1 at the same time; In step S120, potassium fluoride (KF) fluoride salt crystals are obtained, and silicon dioxide solid is obtained in step S140.

以上所述僅為本發明之較佳可行實施例,非因此侷限本發明的專利保護範圍。除上述實施方式外,本發明還可以有其他方式,凡採用等同替換或等效變換形成的技術方案,均落在本發明要求的保護範圍內。本發明未經描述的技術特徵可以通過或採用現有技術實現,在此不再贅述。The above descriptions are only preferred feasible embodiments of the present invention, and therefore do not limit the scope of the patent protection of the present invention. In addition to the above-mentioned embodiments, the present invention may also have other modes, and all technical solutions formed by equivalent replacement or equivalent transformation fall within the protection scope of the present invention. The undescribed technical features of the present invention can be realized by or using the prior art, and are not repeated here.

1:氨產生器 2:鍋爐 3:鼓風機 4:氨吸收塔 5:氨吸收液儲存槽 6:冰水機 7:pH調整槽 8:壓濾機 9:濃縮蒸發罐 10:離心脫水機 11:烤箱 S10:將廢BOE二氧化矽蝕刻液與氫氧化鈉同時加入氨產生器 S20:使用鍋爐產生的蒸汽間接加熱反應液 S30:使用壓送型鼓風機將空氣由氨產生器下方送入 S40:將吹脫出來的氨氣導入氨吸收塔 S50:將氨氣以氨吸收液吸收 S60:氨吸收液儲槽提供氨吸收液供氨吸收塔循環使用 S70:使用冷卻設備作為降低氨吸收液溫度之用 S80:將氨產生器中的反應液輸送到pH調整槽 S90:加入氫氟酸調低反應液的pH值 S100:將反應液導入壓濾機 S110:將氟化鈉溶液半成品輸送到濃縮蒸發罐 S120:將過飽和的氟化鈉溶液導入離心脫水機 S130:將矽沉澱物加以水洗 S140:將洗淨後之矽沉澱物導入烤箱 1: Ammonia generator 2: Boiler 3: Blower 4: Ammonia absorption tower 5: Ammonia absorption liquid storage tank 6: Ice water machine 7: pH adjustment tank 8: filter press 9: Concentrated evaporation tank 10: Centrifugal dehydrator 11: Oven S10: Add waste BOE silicon dioxide etching solution and sodium hydroxide to the ammonia generator at the same time S20: Indirect heating of reaction liquid using steam generated by boiler S30: Use a pressure-feed blower to feed air from below the ammonia generator S40: introduce the stripped ammonia gas into the ammonia absorption tower S50: Absorb ammonia gas with ammonia absorption liquid S60: Ammonia absorption liquid storage tank provides ammonia absorption liquid for circulating use of ammonia absorption tower S70: Use cooling equipment to reduce the temperature of ammonia absorption liquid S80: transfer the reaction solution in the ammonia generator to the pH adjustment tank S90: adding hydrofluoric acid to lower the pH of the reaction solution S100: Introduce the reaction solution to the filter press S110: transport the semi-finished product of sodium fluoride solution to the concentrated evaporation tank S120: introduce the supersaturated sodium fluoride solution into the centrifugal dehydrator S130: Wash the silicon precipitate with water S140: Introduce the washed silicon precipitate into the oven

圖1及圖2係根據本發明一實施例所繪示之由廢BOE二氧化矽蝕刻液中回收氨且製備氟鹽晶體與二氧化矽固體的方法之流程圖; 圖3係不同pH值與不同溫度條件下,氨分子與銨離子之相對量示意圖。 1 and 2 are flowcharts of a method for recovering ammonia from waste BOE silicon dioxide etching solution and preparing fluoride salt crystals and silicon dioxide solids according to an embodiment of the present invention; Figure 3 is a schematic diagram of the relative amounts of ammonia molecules and ammonium ions under different pH values and different temperature conditions.

S10:將廢BOE二氧化矽蝕刻液與氫氧化鈉同時加入氨產生器 S10: Add waste BOE silicon dioxide etching solution and sodium hydroxide to the ammonia generator at the same time

S20:使用鍋爐產生的蒸汽間接加熱反應液 S20: Indirect heating of reaction liquid using steam generated by boiler

S30:使用壓送型鼓風機將空氣由氨產生器下方送入 S30: Use a pressure-feed blower to feed air from below the ammonia generator

S40:將吹脫出來的氨氣導入氨吸收塔 S40: introduce the stripped ammonia gas into the ammonia absorption tower

S50:將氨氣以氨吸收液吸收 S50: Absorb ammonia gas with ammonia absorption liquid

S60:氨吸收液儲槽提供氨吸收液供氨吸收塔循環使用 S60: Ammonia absorption liquid storage tank provides ammonia absorption liquid for circulating use of ammonia absorption tower

S70:使用冷卻設備作為降低氨吸收液溫度之用 S70: Use cooling equipment to reduce the temperature of ammonia absorption liquid

S80:將氨產生器中的反應液輸送到pH調整槽 S80: transfer the reaction solution in the ammonia generator to the pH adjustment tank

S90:加入氫氟酸調低反應液的pH值 S90: adding hydrofluoric acid to lower the pH of the reaction solution

S100:將反應液導入壓濾機 S100: Introduce the reaction solution to the filter press

S110:將氟化鈉溶液半成品輸送到濃縮蒸發罐 S110: transport the semi-finished product of sodium fluoride solution to the concentrated evaporation tank

S120:將過飽和的氟化鈉溶液導入離心脫水機 S120: introduce the supersaturated sodium fluoride solution into the centrifugal dehydrator

S130:將矽沉澱物加以水洗 S130: Wash the silicon precipitate with water

S140:將洗淨後之矽沉澱物導入烤箱 S140: Introduce the washed silicon precipitate into the oven

Claims (10)

一種由廢BOE二氧化矽蝕刻液中回收氨且製備氟鹽晶體與二氧化矽固體的方法,其特徵在於包含以下步驟: (A)將廢BOE二氧化矽蝕刻液與氫氧化鈉導入氨產生方法,透過加熱氨產生方法中之反應液將經空氣吹脫後的氨導入氨吸收方法,以氨吸收液加以吸收; (B)當氨產生方法中反應液之氨濃度小於一定濃度以下時,將其輸送至pH調整方法,用氫氟酸調整反應液之pH值,並導入到固液分離與濃縮方法得到氟化鈉的氟鹽晶體與二氧化矽固體。 A method for recovering ammonia from waste BOE silicon dioxide etching solution and preparing fluorine salt crystal and silicon dioxide solid, which is characterized by comprising the following steps: (A) introduce waste BOE silicon dioxide etching solution and sodium hydroxide into the ammonia production method, and introduce the ammonia after air stripping into the ammonia absorption method by heating the reaction liquid in the ammonia production method, and absorb it with the ammonia absorption liquid; (B) When the ammonia concentration of the reaction liquid in the ammonia production method is less than a certain concentration, it is sent to the pH adjustment method, the pH value of the reaction liquid is adjusted with hydrofluoric acid, and introduced into the solid-liquid separation and concentration method to obtain fluorination. Sodium fluoride salt crystals and silica solid. 如請求項1所述之方法,其中步驟(A)中的氫氧化鈉以氫氧化鉀替代,而於步驟(B)中的固液分離與濃縮方法得到氟化鉀的氟鹽晶體。The method according to claim 1, wherein the sodium hydroxide in step (A) is replaced by potassium hydroxide, and the fluoride salt crystal of potassium fluoride is obtained by the solid-liquid separation and concentration method in step (B). 如請求項1所述之方法,其中步驟(A)係透過鍋爐產生的蒸汽加熱反應液,並使用鼓風機送入空氣,將反應液的氨吹出。The method as claimed in claim 1, wherein step (A) is to heat the reaction liquid through steam generated by a boiler, and use a blower to send in air to blow out ammonia in the reaction liquid. 如請求項1所述之方法,其中步驟(A)之氨吸收方法係循環使用氨吸收液儲存槽之氨吸收液。The method according to claim 1, wherein the ammonia absorption method of step (A) is to recycle the ammonia absorption liquid of the ammonia absorption liquid storage tank. 如請求項1所述之方法,其中更進一步設置冷卻方法,冷卻氨吸收液。The method of claim 1, wherein a cooling method is further provided to cool the ammonia absorption liquid. 如請求項1所述之方法,其中步驟(B)監控氨產生方法中反應液之氨濃度小於10 ppm時,輸送至pH調整槽。The method according to claim 1, wherein in the step (B), when the ammonia concentration of the reaction solution in the monitoring ammonia production method is less than 10 ppm, it is sent to a pH adjustment tank. 如請求項1所述之方法,其中步驟(B)係用氫氟酸調整反應液之pH值至6~8之間。The method according to claim 1, wherein step (B) is to adjust the pH value of the reaction solution to between 6 and 8 with hydrofluoric acid. 如請求項1所述之方法,其中步驟(B)之後更有一步驟(B2),經固液分離得到氟鹽晶體溶液輸送到濃縮方法,再經過固液分離方法得到氟鹽晶體。The method according to claim 1, wherein step (B) is followed by a step (B2), the fluorine salt crystal solution obtained by solid-liquid separation is sent to the concentration method, and then the fluorine salt crystal is obtained by the solid-liquid separation method. 如請求項1或8所述之方法,其中步驟(B)之後更有一步驟(B3),經固液分離的矽沉澱物水洗至水洗水殘留氟離子濃度小於一定值,導入烘乾方法,除去水份得到二氧化矽固體。The method according to claim 1 or 8, wherein step (B) is followed by a step (B3), wherein the silicon precipitate after solid-liquid separation is washed with water until the residual fluoride ion concentration in the washing water is less than a certain value, and a drying method is introduced to remove Moisture yields silica solids. 如請求項9所述之方法,其中該定值為10 ppm。The method of claim 9, wherein the fixed value is 10 ppm.
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