TWI577642B - Method of recycling ammonia from wastewater and preparing solid calcium sulfate and calcium chloride solution - Google Patents

Method of recycling ammonia from wastewater and preparing solid calcium sulfate and calcium chloride solution Download PDF

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TWI577642B
TWI577642B TW103132688A TW103132688A TWI577642B TW I577642 B TWI577642 B TW I577642B TW 103132688 A TW103132688 A TW 103132688A TW 103132688 A TW103132688 A TW 103132688A TW I577642 B TWI577642 B TW I577642B
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ammonia
calcium
calcium chloride
chloride solution
liquid
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TW103132688A
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TW201612112A (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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由廢水中回收氨且製備硫酸鈣固體與氯化鈣溶液的方法Method for recovering ammonia from wastewater and preparing calcium sulfate solid and calcium chloride solution 【0001】【0001】

本發明係一種廢水處理方法,特別是關於一種可從廢水中回收氨,同時從回收過程中得到硫酸鈣固體與氯化鈣溶液的方法。The present invention is a wastewater treatment method, and more particularly to a method for recovering ammonia from wastewater while obtaining calcium sulfate solids and calcium chloride solution from the recovery process.

【0002】【0002】

氨氮可為水生植物的生長提供營養源,而使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。自由的氨氮分子(未離子化的部分),對水生生物則具有毒性。總體而言,使水體發生優養化及生態平衡的失調。為此,環保署已針對光電業、化工業、科學園區的氨氮排放量進行管制,而氨氮回收遂成一個重要的課題。Ammonia nitrogen can provide a nutrient source for the growth of aquatic plants, and such as seaweed and aquatic plants multiply, which will lead to the lack of oxygen in the waters, which in turn causes the aquatic organisms to die. Free ammonia nitrogen molecules (unionized fractions) are toxic to aquatic organisms. In general, the water body is dysfunctional and ecologically balanced. To this end, the Environmental Protection Agency has regulated the ammonia nitrogen emissions of the photovoltaic industry, chemical industry, and science parks, and ammonia nitrogen recovery has become an important issue.

【0003】[0003]

氨(NH3 )為廢氣污染物,一般有產生廢氨氣的工廠,都會使用濕式洗滌塔來削減廢氨氣的排放。為有效的吸附廢氨氣,通常濕式洗滌塔中的洗滌液成分為單價較低的鹽酸或硫酸,當洗滌液排放出洗滌塔時,就變成了含高氨氮廢水。Ammonia (NH 3 ) is an exhaust gas pollutant. Generally, factories that produce waste ammonia gas use a wet scrubber to reduce the emission of waste ammonia. In order to effectively adsorb waste ammonia gas, the composition of the washing liquid in the wet scrubber is usually low-priced hydrochloric acid or sulfuric acid, and when the washing liquid is discharged out of the scrubber, it becomes a wastewater containing high ammonia nitrogen.

【0004】[0004]

目前高濃度的氨氮的回收處理方法為空氣吹脫(air stripping)和蒸氣氣提(steam stripping)法,此法是在鹼性條件下用空氣吹脫(以空氣作為載氣),或用蒸氣氣提(以水蒸氣作為載氣)。利用廢水中所含氨氮的實際濃度與平衡濃度之間存在的差異,先以提供鹼性環境將氨離子轉成氨分子,再利用氨分子的揮發性,使廢水中的氨氮由液相轉移到氣相中,從而達到去除氨氮的目的。因此法須在鹼性條件下進行,通常使用氫氧化鈣(Ca(OH)2 )(俗稱石灰乳、熟石灰)、氫氧化鈉(NaOH)或氫氧化鉀(KOH)等鹼金族、鹼土族化合物來提高廢水的pH值(又稱酸鹼值)。At present, the high-concentration ammonia nitrogen recovery treatment method is air stripping and steam stripping, which is to be blown off by air under alkaline conditions (using air as a carrier gas) or by using steam. Stripping (using water vapor as a carrier gas). Using the difference between the actual concentration of ammonia nitrogen contained in the wastewater and the equilibrium concentration, firstly, the ammonia ion is converted into an ammonia molecule by providing an alkaline environment, and then the volatility of the ammonia molecule is utilized to transfer the ammonia nitrogen in the wastewater from the liquid phase to In the gas phase, the purpose of removing ammonia nitrogen is achieved. Therefore, the method must be carried out under alkaline conditions, usually using calcium hydroxide (Ca(OH) 2 ) (commonly known as lime milk, slaked lime), sodium hydroxide (NaOH) or potassium hydroxide (KOH), etc. Compounds to increase the pH of wastewater (also known as pH).

【0005】[0005]

然而氫氧化鈣雖便宜但於操作過程中易產成水垢(含鈣的沉澱物),例如:硫酸鈣(CaSO4 )、碳酸鈣(CaCO3 ),造成設備效率降低甚至造成管路堵塞而使設備無法操作,因此在工業上亦經常採用氫氧化鈉調高廢水的pH值。However, although calcium hydroxide is cheap, it is easy to produce scale (calcium containing calcium) during operation, such as calcium sulfate (CaSO 4 ) or calcium carbonate (CaCO 3 ), which causes the efficiency of the equipment to decrease and even cause blockage of the pipeline. The equipment is inoperable, so it is often used in the industry to increase the pH of the wastewater.

【0006】[0006]

而若採用氫氧化鈉調高廢水的pH值,雖然不會產生沉澱物,但吹脫後殘餘的液體為氯化鈉(NaCl)或硫酸鈉(NaSO4 )溶液,這兩股溶液直接再利用性低,無法直接販售,只能當作廢水處理。However, if sodium hydroxide is used to raise the pH value of the wastewater, although no sediment will be produced, the residual liquid after stripping is sodium chloride (NaCl) or sodium sulfate (NaSO 4 ) solution, and the two solutions are directly reused. It is low in nature and cannot be sold directly. It can only be treated as wastewater.

【0007】【0007】

除此之外,空氣吹脫法或蒸氣氣提法吹脫出來的氨氣,若無收集而散逸出,易造成二次汙染。In addition, the ammonia gas blown off by the air stripping method or the steam stripping method can easily cause secondary pollution if it is not collected and escapes.

【0008】[0008]

本發明的目的在提供一種由廢水中回收氨且製備硫酸鈣固體與氯化鈣溶液的方法,有傳統空氣吹脫法之優點:氨吹出率高,而無空氣吹脫法、氫氧化鈉法、氫氧化鈣法之缺點:氨氣排放造成二次污染、副產品無法再利用、沉積物堵塞管路的問題。The object of the present invention is to provide a method for recovering ammonia from waste water and preparing calcium sulfate solid and calcium chloride solution, which has the advantages of the conventional air stripping method: high ammonia blowing rate, and no air blowing method, sodium hydroxide method The shortcomings of the calcium hydroxide method: the secondary pollution caused by ammonia emissions, the inability to reuse by-products, and the problem of sediment blocking the pipeline.

【0009】【0009】

為了達成前述目的,本發明提供一種由廢水中回收氨且製備硫酸鈣固體與氯化鈣溶液的方法,包括下列步驟(A)~(D)。In order to achieve the foregoing object, the present invention provides a method for recovering ammonia from wastewater and preparing a calcium sulfate solid and a calcium chloride solution, comprising the following steps (A) to (D).

【0010】[0010]

步驟(A):將氨氮廢水導入反應槽,加入氯化鈣,利用氯化鈣中的鈣離子(Ca2+ ),使廢水中的硫酸根離子(SO4 2- )和鈣離子結合產生硫酸鈣固體沉澱,以固液分離設備去除沉澱之後,此時的廢水為氯化銨(NH4 Cl)廢水,稱此轉化過後的廢水為反應液,將此反應液導入攪拌混合槽。Step (A): introducing ammonia nitrogen wastewater into the reaction tank, adding calcium chloride, and utilizing calcium ions (Ca 2+ ) in the calcium chloride to combine sulfate ion (SO 4 2- ) and calcium ions in the wastewater to produce sulfuric acid. After the calcium solid is precipitated and the precipitate is removed by a solid-liquid separation device, the wastewater at this time is ammonium chloride (NH 4 Cl) wastewater, and the converted wastewater is referred to as a reaction liquid, and the reaction liquid is introduced into a stirring mixing tank.

【0011】[0011]

步驟(B):以氫氧化鈣(Ca(OH)2 )提高氯化銨反應液的pH值至11以上,導入氨產生器,將反應液增溫(加熱用蒸氣不會與反應液接觸)。使用空氣吹脫法去除氨後,剩餘的氯離子會和鈣離子結合成氯化鈣。Step (B): increasing the pH of the ammonium chloride reaction solution to 11 or more with calcium hydroxide (Ca(OH) 2 ), introducing the ammonia generator, and warming the reaction liquid (the heating vapor does not come into contact with the reaction liquid) . After removal of ammonia by air stripping, the remaining chloride ions combine with calcium ions to form calcium chloride.

【0012】[0012]

步驟(C):收集空氣吹脫後散逸的氨於氨吸收塔中,利用水或鹽酸吸收散逸出來的氨氣,分別製成氨水或氯化銨溶液。Step (C): collecting ammonia dissolved in the ammonia absorption tower after the air is blown off, and absorbing the dissolved ammonia gas by using water or hydrochloric acid to prepare ammonia water or ammonium chloride solution, respectively.

【0013】[0013]

步驟(D):先用鹽酸將吹脫後之反應液pH值調整到4以下,讓反應液中的碳酸鈣(由步驟B之氫氧化鈣吸收空氣中的二氧化碳(CO2 )產生)或殘餘未反應完的氫氧化鈣和鹽酸反應,待pH值穩定不再變化後緩慢逐步加入氫氧化鈣,將反應液的pH值拉高控制在6~9之間,最終再以固液分離設備過濾反應液去除矽酸鹽、硫酸鹽類等的不溶物雜質即可得氯化鈣溶液成品。Step (D): first adjust the pH of the reaction solution after stripping to below 4 with hydrochloric acid, and let the calcium carbonate in the reaction solution (the calcium hydroxide in step B absorbs carbon dioxide (CO 2 ) in the air) or residual The unreacted calcium hydroxide reacts with hydrochloric acid. After the pH value is stable, the calcium hydroxide is slowly added gradually, and the pH of the reaction solution is controlled to be between 6 and 9, and finally filtered by a solid-liquid separation device. The reaction solution removes insoluble impurities such as citrate and sulfate to obtain a finished calcium chloride solution.

【0014】[0014]

在本發明中,步驟(A)中的硫酸鈣的純度很高,有開發成硫酸鈣奈米線(棒)的潛力。步驟(B)中的氯化鈣溶液可作為廢水處理的藥劑,可用於去除廢水中的氟離子。步驟(C)中的氨水再提濃可直接販售,而氯化銨溶液可再濃縮成氯化銨粉銷售。步驟(D)中之氯化鈣溶液的濃度介於15~20%,可用來稀釋市售之氯化鈣溶液(濃度36%)。In the present invention, the calcium sulfate in the step (A) has a high purity and has the potential to be developed into a calcium sulfate nanowire (rod). The calcium chloride solution in the step (B) can be used as a medicament for wastewater treatment and can be used to remove fluoride ions in the wastewater. The ammonia water in step (C) can be directly concentrated and sold directly, while the ammonium chloride solution can be further concentrated to ammonium chloride powder for sale. The concentration of the calcium chloride solution in step (D) is between 15 and 20% and can be used to dilute a commercially available calcium chloride solution (concentration 36%).

【0015】[0015]

為讓本創作上述和其他目的、特徵和優點能更明顯易懂,下文特舉較佳實施例,並配合所附圖式,作詳細說明如下。The above and other objects, features and advantages of the present invention will become more apparent and understood.

【0032】[0032]

1‧‧‧硫酸根去除槽1‧‧‧ sulfate removal tank

2‧‧‧壓濾機2‧‧‧ filter press

3‧‧‧攪拌混合槽3‧‧‧Stirring mixing tank

4‧‧‧鍋爐4‧‧‧Boiler

5‧‧‧鼓風機5‧‧‧Blowers

6‧‧‧氨產生器6‧‧‧Ammonia generator

7‧‧‧氨吸收塔7‧‧‧Ammonia absorption tower

8‧‧‧氨吸收液儲槽8‧‧‧Ammonia absorption tank

9‧‧‧冰水機9‧‧‧ice water machine

10‧‧‧壓濾機10‧‧‧ filter press

11‧‧‧氯化鈣儲槽11‧‧‧ calcium chloride storage tank

S10~S120‧‧‧各步驟S10~S120‧‧‧Steps

【0016】[0016]

  第1圖及第2圖為根據本發明一實施例所繪示之由廢水中回收氨且製備硫酸鈣固體與氯化鈣溶液的方法之流程圖;1 and 2 are flow charts showing a method for recovering ammonia from wastewater and preparing calcium sulfate solid and calcium chloride solution according to an embodiment of the invention;

  第3圖為不同pH值與不同溫度條件下,氨分子與銨離子之相對量示意圖。Figure 3 is a schematic diagram showing the relative amounts of ammonia molecules and ammonium ions at different pH values and different temperature conditions.

【0017】[0017]

第1圖及第2圖為根據本發明一實施例所繪示之由廢水中回收氨且製備硫酸鈣固體與氯化鈣溶液的方法之流程圖,於其中的步驟S30與步驟S70,可配合地參考第3圖,其顯示pH值與溫度對氨分子與銨離子比值的影響。1 and 2 are flow charts of a method for recovering ammonia from wastewater and preparing calcium sulfate solid and calcium chloride solution according to an embodiment of the invention, wherein step S30 and step S70 can be combined. Referring to Figure 3, it shows the effect of pH and temperature on the ratio of ammonia to ammonium.

【0018】[0018]

請先參考第1圖,步驟S10中,將硫酸銨廢水(以下稱此廢水為反應液)與氯化鈣溶液倒入硫酸根去除槽(1)中攪拌,去除反應液中的硫酸根離子。
CaCl2 + (NH4 )2 SO4 →CaSO4 (固)+ 2NH4 Cl(液)
Referring to FIG. 1 first, in step S10, ammonium sulfate wastewater (hereinafter referred to as the reaction liquid) and calcium chloride solution are poured into the sulfate removal tank (1) and stirred to remove sulfate ions in the reaction liquid.
CaCl 2 + (NH 4 ) 2 SO 4 →CaSO 4 (solid) + 2NH 4 Cl (liquid)

【0019】[0019]

步驟S20中,接著將反應液導入固液分離設備,例如壓濾機(2),使固液分離,分離出反應液中的硫酸鈣,得到硫酸鈣固體。此時反應液為氯化銨廢水。In step S20, the reaction liquid is then introduced into a solid-liquid separation device, for example, a filter press (2), and the solid-liquid separation is carried out to separate calcium sulfate in the reaction liquid to obtain a calcium sulfate solid. At this time, the reaction liquid was ammonium chloride wastewater.

【0020】[0020]

步驟S30,反應液導入攪拌混合槽(3),加入氫氧化鈣,提高反應液pH值至11以上(實務上多提高到pH=11.3~11.5),然後將反應液導入氨產生器(6)中。In step S30, the reaction liquid is introduced into the stirring mixing tank (3), calcium hydroxide is added, the pH of the reaction liquid is raised to 11 or more (in practice, the pH is increased to pH=11.3 to 11.5), and then the reaction liquid is introduced into the ammonia generator (6). in.

【0021】[0021]

由NH3 與NH4 + 之平衡反應式(請參考第3圖):
NH3 + H2 O  NH4 + + OH- 知,此時,在鹼性環境使反應液中的銨離子多轉換成氨分子存在。
The equilibrium reaction formula of NH 3 and NH 4 + (please refer to Figure 3):
NH 3 + H 2 O NH 4 + + OH - knows that at this time, the ammonium ion in the reaction liquid is converted into an ammonia molecule in an alkaline environment.

【0022】[0022]

步驟S40,將反應液增溫,例如由鍋爐(4)提供之蒸氣加熱氨產生器(6)中的反應液(此蒸氣不會與反應液接觸)。In step S40, the reaction liquid is warmed, for example, the steam supplied from the boiler (4) heats the reaction liquid in the ammonia generator (6) (this vapor does not come into contact with the reaction liquid).

【0023】[0023]

步驟S50,由壓送型鼓風機(5)將空氣吹入氨產生器(6)中。In step S50, air is blown into the ammonia generator (6) by the pressure feed type blower (5).

【0024】[0024]

步驟S60,利用空氣吹脫法將反應液中的氨吹出。剩下的反應液,主要是氯化鈣溶液。In step S60, ammonia in the reaction liquid is blown off by air stripping. The remaining reaction solution is mainly a calcium chloride solution.

【0025】[0025]

步驟S70,將步驟S60中吹出的氨氣導入氨吸收塔(7),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:H2 O + NH3 → NH4 + + OH- (請參考第3圖)。如氨吸收液為鹽酸,則所得成品為氯化銨溶液:HCl + NH3 → NH4 + + Cl-In step S70, the ammonia gas blown in step S60 is introduced into the ammonia absorption tower (7) to be absorbed by the ammonia absorption liquid. If the ammonia absorbing liquid is water, the temperature of the ammonia absorbing liquid (ie, water) is cooled by cooling to dissolve the ammonia gas in the ammonia absorbing liquid (ie, water), and the obtained finished product is ammonia water: H 2 O + NH 3 → NH 4 + + OH - (Please refer to Figure 3). If the ammonia absorbing liquid is hydrochloric acid, the obtained product is an ammonium chloride solution: HCl + NH 3 → NH 4 + + Cl - .

【0026】[0026]

步驟S80,儲放氨吸收液於氨吸收液儲槽(8)供氨吸收塔(7)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 S80, the ammonia absorption liquid is stored in the ammonia absorption liquid storage tank (8) for recycling to the ammonia absorption tower (7), and the new ammonia absorption liquid is replaced when the ammonia absorption liquid reaches the desired concentration.

【0027】[0027]

步驟S90,預先準備冷卻設備,例如冰水機(9),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 S90, a cooling device such as an ice water machine (9) is prepared in advance, and when the ammonia absorbing liquid is water, it is used as a temperature for reducing the ammonia absorbing liquid (ie, water), so that ammonia gas is dissolved in the ammonia absorbing liquid (ie, water). )in.

【0028】[0028]

請再參考圖2,步驟S100,於氨產生器(6)中,先加鹽酸將吹脫後之反應液pH值調整到4以下,讓反應液中的碳酸鈣(由步驟S30之氫氧化鈣吸收空氣中的二氧化碳(CO2 )產生)或殘餘未反應完的氫氧化鈣和鹽酸反應,待反應液之pH值穩定之後,再以氫氧化鈣緩慢將pH值提升到6~9,得到氯化鈣半成品。Referring to FIG. 2 again, in step S100, in the ammonia generator (6), hydrochloric acid is first added to adjust the pH of the reaction solution after the stripping to below 4, and the calcium carbonate in the reaction solution (calcium hydroxide from step S30). Absorbing carbon dioxide (CO 2 ) in the air) or residual unreacted calcium hydroxide and hydrochloric acid, after the pH of the reaction liquid is stabilized, slowly raise the pH to 6-9 with calcium hydroxide to obtain chlorine. Calcium semi-finished products.

【0029】[0029]

步驟S110,將反應液導入固液分離設備,例如壓濾機(10),固液分離以去除氯化鈣半成品中矽酸鹽、硫酸鹽類等的不溶物雜質,得到氯化鈣溶液成品。In step S110, the reaction liquid is introduced into a solid-liquid separation device, for example, a filter press (10), and solid-liquid separation is performed to remove insoluble impurities such as citrate or sulfate in the calcium chloride semi-finished product to obtain a finished calcium chloride solution.

【0030】[0030]

步驟S120,儲放於步驟S110中得到的氯化鈣溶液於氯化鈣儲槽(11)中。In step S120, the calcium chloride solution obtained in step S110 is stored in the calcium chloride storage tank (11).

【0031】[0031]

雖然本發明已以較佳實施例揭露如上,然其並非用以限定本發明,任何本領域技術人員,在不脫離本發明的精神和範圍內,當可作些許更動與潤飾,因此本發明的保護範圍當視所附的申請專利範圍所界定者為準。Although the present invention has been disclosed in the above preferred embodiments, it is not intended to limit the present invention, and those skilled in the art can make some modifications and refinements without departing from the spirit and scope of the present invention. The scope of protection is subject to the definition of the scope of the attached patent application.

 

1‧‧‧硫酸根去除槽 1‧‧‧ sulfate removal tank

2‧‧‧壓濾機 2‧‧‧ filter press

3‧‧‧攪拌混合槽 3‧‧‧Stirring mixing tank

4‧‧‧鍋爐 4‧‧‧Boiler

5‧‧‧鼓風機 5‧‧‧Blowers

6‧‧‧氨產生器 6‧‧‧Ammonia generator

7‧‧‧氨吸收塔 7‧‧‧Ammonia absorption tower

8‧‧‧氨吸收液儲槽 8‧‧‧Ammonia absorption tank

9‧‧‧冰水機 9‧‧‧ice water machine

S10~S90‧‧‧各步驟 S10~S90‧‧‧ steps

Claims (7)

【第1項】[Item 1] 一種由廢水中回收氨且製備硫酸鈣固體與氯化鈣溶液的方法,包括:
  (A)將廢水導入硫酸根去除槽,加入氯化鈣,用氯化鈣中的鈣離子,與反應液中的硫酸根離子結合產生硫酸鈣固體沉澱,稱轉化過的廢水為反應液;
  (B)將反應液導入攪拌混合槽,以氫氧化鈣提高反應液的酸鹼值,之後導入氨產生器,將反應液增溫,以空氣吹脫法去除氨,剩餘的氯離子會和鈣離子結合成氯化鈣;
  (C) 收集空氣吹脫後散逸的氨於氨吸收塔中,利用氨吸收液吸收散逸出來的氨氣。
A method for recovering ammonia from wastewater and preparing a calcium sulfate solid and a calcium chloride solution, comprising:
(A) introducing waste water into the sulfate removal tank, adding calcium chloride, using calcium ions in the calcium chloride, and combining with the sulfate ion in the reaction liquid to produce a solid precipitate of calcium sulfate, and the converted wastewater is referred to as a reaction liquid;
(B) introducing the reaction liquid into the stirring mixing tank, increasing the pH value of the reaction liquid with calcium hydroxide, then introducing the ammonia generator, warming the reaction liquid, removing ammonia by air stripping, and remaining chlorine ions and calcium. Ion binding to calcium chloride;
(C) Collecting ammonia dissolved in the ammonia absorption tower after the air is blown off, and absorbing the dissolved ammonia gas by using the ammonia absorption liquid.
【第2項】[Item 2] 如申請專利範圍第1項所述由廢水中回收氨且製備硫酸鈣固體與氯化鈣溶液的方法,其中於步驟(A)產生硫酸鈣沉澱之後,更包括一步驟(A2),以固液分離設備去除沉澱出的硫酸鈣。A method for recovering ammonia from waste water and preparing a calcium sulfate solid and a calcium chloride solution as described in claim 1, wherein after the calcium sulfate precipitate is produced in the step (A), a step (A2) is further included to fix the liquid. The separation device removes the precipitated calcium sulfate. 【第3項】[Item 3] 如申請專利範圍第1項所述由廢水中回收氨且製備硫酸鈣固體與氯化鈣溶液的方法,其中於步驟(B)之後更包括一步驟(B2),於氨產生器中,先用鹽酸將吹脫後之反應液酸鹼值調整到4以下,讓反應液中的碳酸鈣或殘餘未反應完的氫氧化鈣和鹽酸反應,待酸鹼值穩定不再變化後緩慢逐步加入氫氧化鈣,提升酸鹼值至6~9之間,此時反應液為氯化鈣半成品。The method for recovering ammonia from wastewater and preparing calcium sulfate solid and calcium chloride solution according to claim 1, wherein step (B) further comprises a step (B2) in the ammonia generator. The pH value of the reaction liquid after the stripping of hydrochloric acid is adjusted to 4 or less, and the calcium carbonate in the reaction liquid or the residual unreacted calcium hydroxide and hydrochloric acid are reacted, and the hydroxide is slowly and gradually added after the pH value is no longer changed. Calcium, increase the pH value to 6~9, at this time the reaction liquid is a semi-finished product of calcium chloride. 【第4項】[Item 4] 如申請專利範圍第3項所述由廢水中回收氨且製備硫酸鈣固體與氯化鈣溶液的方法,其中於步驟(B2)之後更有一步驟(B3),以固液分離設備去除氯化鈣半成品中的不溶物雜質,得氯化鈣溶液。A method for recovering ammonia from waste water and preparing a calcium sulfate solid and a calcium chloride solution as described in claim 3, wherein a step (B3) is further performed after the step (B2) to remove calcium chloride by a solid-liquid separation device. Insoluble impurities in the semi-finished product give a calcium chloride solution. 【第5項】[Item 5] 如申請專利範圍第1項所述由廢水中回收氨且製備硫酸鈣固體與氯化鈣溶液的方法,其中於步驟(C),當以水作為氨吸收液時,利用氨吸收液吸收散逸出來的氨氣,所得的成品為氨水。The method for recovering ammonia from waste water and preparing calcium sulfate solid and calcium chloride solution according to claim 1, wherein in the step (C), when water is used as the ammonia absorption liquid, the ammonia absorption liquid is absorbed and dispersed. Ammonia gas, the finished product is ammonia water. 【第6項】[Item 6] 如申請專利範圍第5項所述由廢水中回收氨且製備硫酸鈣固體與氯化鈣溶液的方法,其中於步驟(C),當以水作為氨吸收液時,更包括一步驟(C2),將氨吸收液的溫度降溫以利氨氣溶於氨吸收液中。A method for recovering ammonia from waste water and preparing a calcium sulfate solid and a calcium chloride solution as described in claim 5, wherein in step (C), when water is used as the ammonia absorbent, a step (C2) is further included. The temperature of the ammonia absorbing liquid is lowered to dissolve the ammonia gas in the ammonia absorbing liquid. 【第7項】[Item 7] 如申請專利範圍第1項所述由廢水中回收氨且製備硫酸鈣固體與氯化鈣溶液的方法,其中於步驟(C),當以鹽酸作為氨吸收液時,利用氨吸收液吸收散逸出來的氨氣,所得的成品為氯化銨溶液。A method for recovering ammonia from waste water and preparing a calcium sulfate solid and a calcium chloride solution according to the first aspect of the patent application, wherein in the step (C), when hydrochloric acid is used as the ammonia absorption liquid, the ammonia absorption liquid is absorbed and dispersed. Ammonia gas, the resulting product is an ammonium chloride solution.
TW103132688A 2014-09-22 2014-09-22 Method of recycling ammonia from wastewater and preparing solid calcium sulfate and calcium chloride solution TWI577642B (en)

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TWI238148B (en) * 2002-10-25 2005-08-21 Powerchip Semiconductor Corp Method for treating fluoride containing waste water
TWM453673U (en) * 2013-01-24 2013-05-21 Zhan System Technology Co Ltd I High performance ammonia recovery system
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TWI238148B (en) * 2002-10-25 2005-08-21 Powerchip Semiconductor Corp Method for treating fluoride containing waste water
TW201420518A (en) * 2012-11-14 2014-06-01 Tsukishima Kankyo Engineering Ltd Wastewater treatment method and treatment device
TWM453673U (en) * 2013-01-24 2013-05-21 Zhan System Technology Co Ltd I High performance ammonia recovery system

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