TWI657857B - Gas treatment method and apparatus for ammonia-contained gas - Google Patents

Gas treatment method and apparatus for ammonia-contained gas Download PDF

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TWI657857B
TWI657857B TW106129058A TW106129058A TWI657857B TW I657857 B TWI657857 B TW I657857B TW 106129058 A TW106129058 A TW 106129058A TW 106129058 A TW106129058 A TW 106129058A TW I657857 B TWI657857 B TW I657857B
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ammonia
gas
solution
ammonium phosphate
aqueous solution
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TW106129058A
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TW201912235A (en
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沈瑞富
林勳佑
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中國鋼鐵股份有限公司
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Abstract

一種含氨廢氣處理方法及裝置,該方法包含:提供包含氨的一混合氣體;將該混合氣體與一水溶液接觸,以形成一預淨處理氣體及一富氨水溶液;將該預淨處理氣體與一磷酸混合液接觸,使該磷酸混合液與該預淨處理氣體反應形成一磷酸銨富液;對該富氨水溶液與磷酸銨富液則分別進行再生與回收氨處理程序;再生後之水溶液與磷酸銨貧液皆導回廢氣處理單元供循環使用。 A method and device for treating ammonia-containing waste gas, the method includes: providing a mixed gas containing ammonia; contacting the mixed gas with an aqueous solution to form a pre-cleaned processing gas and an ammonia-rich aqueous solution; A phosphoric acid mixed solution is brought into contact to make the phosphoric acid mixed solution react with the pre-cleaned treatment gas to form an ammonium phosphate rich solution; the ammonia-rich aqueous solution and the ammonium phosphate rich solution are separately subjected to regeneration and recovery ammonia treatment procedures; the regenerated aqueous solution and The ammonium phosphate lean solution is returned to the exhaust treatment unit for recycling.

Description

含氨廢氣處理方法及裝置 Method and device for treating ammonia-containing exhaust gas

本發明係關於一種含氨廢氣處理方法及裝置,特別是關於一種兩階段去除含氨廢氣之處理方法及裝置。 The invention relates to a method and a device for treating ammonia-containing exhaust gas, in particular to a two-stage method and device for removing ammonia-containing exhaust gas.

隨著溫室效應的影響,世界各國紛紛注意二氧化碳的排放量。為降低廢氣中的二氧化碳含量,以化學吸收法捕捉二氧化碳為現行最常用的碳捕捉方式,其流程中需經過化學吸收捕捉碳、經過再生後將二氧化碳以各種方式封存於特定環境中(例如廢棄油田中或地下鹽水層),使得排放的廢氣中二氧化碳的含量能減少。現行化學法捕捉二氧化碳主要有使用鹼性、氨類、醇胺類水溶液、離子溶液等吸收煙道氣體中的二氧化碳。雖使用醇胺類化學吸收液之捕碳技術,歷史悠久技術也較成熟,但卻有再生能耗高、化學品價格高、使用過程醇胺易劣化、腐蝕性高與逸散衍生環保顧慮較高等缺點,另因醇胺類化學吸收液會與氣體中硫化物發生反應,因此捕碳前必須進行深度脫硫程序,也增加捕碳的成本與限制應用性。相對而言,氨則具化學性質穩定、價格低、再生能耗較低,且無未知環保顧慮等之優點;另含SOx硫化物之氣體,也可先用氨水進行脫硫而生成硫酸銨,而硫酸銨則可回收為肥料。然技術上,需面對氨水高揮發性所衍生之問題,並需建立經濟有效之製程技術。 With the impact of the greenhouse effect, countries around the world have paid attention to carbon dioxide emissions. In order to reduce the carbon dioxide content in the exhaust gas, chemical absorption is the most commonly used carbon capture method. The process requires chemical absorption to capture carbon, and after regeneration, carbon dioxide is stored in various ways in specific environments (such as abandoned oil fields) Medium or underground brine layer), so that the content of carbon dioxide in the exhaust gas can be reduced. The current chemical methods to capture carbon dioxide mainly include the use of alkaline, ammonia, alcohol-amine aqueous solutions, ionic solutions, etc. to absorb carbon dioxide in the flue gas. Although carbon capture technology using alcohol amine chemical absorption liquid has a long history and mature technology, it has high energy consumption for regeneration, high chemical prices, easy degradation of alcohol amines during use, high corrosiveness and fugitive environmental protection concerns. Higher disadvantages, and because the alcohol-amine chemical absorption solution will react with sulfides in the gas, it must perform a deep desulfurization process before carbon capture, which also increases the cost of carbon capture and limits its applicability. In contrast, ammonia has the advantages of stable chemical properties, low price, low energy consumption for regeneration, and no unknown environmental protection concerns. In addition, the gas containing SOx sulfide can also be desulfurized with ammonia to generate ammonium sulfate. Ammonium sulfate can be recycled as fertilizer. However, technically, it is necessary to face the problems caused by the high volatility of ammonia water, and to establish a cost-effective process technology.

然而,上述現有之氨水吸收法在實際使用上仍具有下述問題,利用氨水吸收煙道氣體中的二氧化碳會造成尾氣中具有氨氣,人體對氨氣的嗅覺閾值(odor threshold)約為5ppm,超過5ppm人體將感覺到氨氣特殊的臭味,且當氨氣濃度高於約20ppm時且將可能導致眼睛、甚或呼吸道的刺激。因此當排放的煙道氣體中氨氣濃度過高時,將導致環保問題。現行氨水捕碳技術中,ALSTOM公司發展之冷凍氨製程(chilled-NH3 process) 為已有大規模工業實績之製程技術;其方法特點為採用低溫吸收製程(吸收塔溫約0℃至10℃)來減少氨排放量,但低溫製程之投資成本及後續操作費用皆昂貴,因而阻礙工業使用。因此,世界上已有許多機構研發常溫氨水捕碳製程技術;然由澳洲試驗工場實績,顯示氨揮發性高會造成捕碳後尾氣中氨濃度高,必須進一步淨化尾氣至符合環保,而此程序成本高,亦即氨水捕碳法需建立經濟有效之尾氣淨化技術。 However, the above-mentioned existing ammonia water absorption method still has the following problems in practical use. The absorption of carbon dioxide in the flue gas by using ammonia water will cause ammonia in the exhaust gas, and the human body's odor threshold to ammonia gas is about 5 ppm. More than 5 ppm human body will feel the special smell of ammonia, and when the ammonia concentration is higher than about 20 ppm, it may cause eye, even respiratory irritation. Therefore, when the ammonia gas concentration in the discharged flue gas is too high, environmental protection problems will be caused. Among the current carbon capture technologies for ammonia, the chilled-NH 3 process developed by ALSTOM is a process technology that has a large-scale industrial performance; its method is characterized by the use of a low-temperature absorption process (the temperature of the absorption tower is about 0 ° C to 10 ° C) ) To reduce ammonia emissions, but the investment costs and subsequent operating costs of low-temperature processes are expensive, which hinders industrial use. Therefore, many institutions in the world have developed room temperature ammonia carbon capture process technology; however, the results of Australian test plants show that high ammonia volatility will cause high ammonia concentration in the tail gas after carbon capture, and the tail gas must be further purified to meet environmental protection, and this procedure The cost is high, that is, the ammonia carbon capture method needs to establish a cost-effective exhaust gas purification technology.

故,有必要提供一種含氨廢氣處理方法及裝置,以解決習用技術所存在的問題。 Therefore, it is necessary to provide a method and a device for treating ammonia-containing exhaust gas to solve the problems existing in conventional technology.

本發明之主要目的在於提供一種淨化含氨廢氣處理方法及裝置,其係利用兩階段去除尾氣中所含之氨氣,以便降低尾氣所含之氨氣含量,進而提升空氣品質且符合環保法規。 The main purpose of the present invention is to provide a method and a device for purifying ammonia-containing exhaust gas, which use two stages to remove the ammonia gas contained in the exhaust gas in order to reduce the ammonia gas content in the exhaust gas, thereby improving the air quality and complying with environmental protection regulations.

本發明之次要目的在於提供一種含氨廢氣處理方法及裝置,其係利用一水溶液先行吸收尾氣中部分之氨氣含量,再使用磷酸銨溶液進行吸收,以便降低尾氣所含之氨氣含量,進而提高含氨廢氣處理效率。 A secondary object of the present invention is to provide a method and a device for treating ammonia-containing exhaust gas, which use an aqueous solution to first absorb a part of the ammonia content in the exhaust gas, and then use an ammonium phosphate solution for absorption in order to reduce the ammonia gas content in the exhaust gas. Further improve the efficiency of ammonia-containing waste gas treatment.

本發明之次要目的在於提供一種含氨廢氣處理方法及裝置,其係利用一水溶液先將捕碳後尾氣中之氨氣吸收去除大部分,再使用磷酸銨水溶液將尾氣中殘存之氨氣吸收去除,達成符合環保之高效率方法。 A secondary object of the present invention is to provide a method and a device for treating ammonia-containing exhaust gas, which use an aqueous solution to first absorb and remove most of the ammonia gas in the exhaust gas after carbon capture, and then use the ammonium phosphate aqueous solution to absorb the remaining ammonia gas in the exhaust gas. Removal to achieve environmentally efficient methods.

為達上述之目的,本發明之一實施例中,提供一種含氨廢氣處理方法,包含下列步驟:(a)提供一混合氣體,該混合氣體中包含氨;(b)將該混合氣體與一水溶液接觸,使該混合氣體中的氨被該水溶液吸收,以形成一含氨水溶液及一預處理氣體,另對含氨水溶液則進行回收處理程序,去除氨後之水溶液導回再吸收尾氣中氨;(c)將該預處理氣體與一磷酸混合液接觸,使該磷酸混合液與該預處理氣體反應形成一磷酸銨富液;(d)對該磷酸銨富液進行一回收處理程序,以去除該磷酸銨富液中的一部分氨,而得到一磷酸銨回收液;以及(e)將該磷酸銨回收液導回步驟(b)形成之預處理氣體中,使該磷酸銨回收液吸收該步驟(c)之預處理氣體中之氨,以形成一氨水吸收液供循環使用。 In order to achieve the above object, in one embodiment of the present invention, a method for treating ammonia-containing exhaust gas is provided, which includes the following steps: (a) providing a mixed gas containing ammonia; (b) combining the mixed gas with a The aqueous solution is contacted, so that the ammonia in the mixed gas is absorbed by the aqueous solution to form an ammonia-containing aqueous solution and a pretreatment gas, and the ammonia-containing aqueous solution is subjected to a recovery process, and the aqueous solution after ammonia removal is led back to absorb ammonia in the tail gas (C) contacting the pretreatment gas with a mixed solution of phosphoric acid, and reacting the mixed solution of phosphoric acid with the pretreatment gas to form an ammonium phosphate-rich solution; (d) performing a recovery treatment procedure on the ammonium phosphate-rich solution, Removing part of the ammonia in the ammonium phosphate rich solution to obtain an ammonium phosphate recovery solution; and (e) introducing the ammonium phosphate recovery solution back into the pretreatment gas formed in step (b), so that the ammonium phosphate recovery solution absorbs the The ammonia in the pretreatment gas of step (c) to form an ammonia water absorption liquid for recycling.

在本發明之一實施例中,該水溶液吸收該混合氣體之一操作 溫度為0℃至60℃。 In one embodiment of the present invention, the aqueous solution absorbs one of the mixed gas. The temperature is from 0 ° C to 60 ° C.

在本發明之一實施例中,該磷酸混合液吸收該混合氣體之操作溫度為10℃至100℃。 In one embodiment of the present invention, the operating temperature of the phosphoric acid mixed solution to absorb the mixed gas is 10 ° C to 100 ° C.

在本發明之一實施例中,在該磷酸銨富液包含H3PO4、(NH4)H2PO4、(NH4)2HPO4及(NH4)3PO4,且上述化合物總重量佔該磷酸銨回收液之整體重量的5%至40%。 In one embodiment of the present invention, the ammonium phosphate rich solution contains H 3 PO 4 , (NH 4 ) H 2 PO 4 , (NH 4 ) 2 HPO 4 and (NH 4 ) 3 PO 4 , and the above compounds are total The weight accounts for 5% to 40% of the entire weight of the ammonium phosphate recovery solution.

在本發明之一實施例中,在進行步驟(d)後,該磷酸銨回收液中的NH3/H3PO4莫爾比小於1.4,及在進行步驟(c)後,該磷酸銨富液中的NH3/H3PO4莫爾比小於1.8。 In one embodiment of the present invention, after performing step (d), the NH 3 / H 3 PO 4 molar ratio in the ammonium phosphate recovery solution is less than 1.4, and after performing step (c), the ammonium phosphate is rich. The molar ratio of NH 3 / H 3 PO 4 in the liquid is less than 1.8.

在本發明之一實施例中,提供一種含氨廢氣處理裝置,其包含:一第一處理單元,用以容納一水溶液以及一混合氣體,該混合氣體中至少包含氨,其中該水溶液和該混合氣體反應形成一含氨水溶液及一預處理氣體,該含氨水溶液經由一第一導出管導出;一再生單元,用以收集被導出之該含氨水溶液並處理該含氨水溶液,以產生一再生水溶液以及一氨氣,該再生水溶液經由一第一導入管導回至該第一處理單元;一第二處理單元,用以容納一磷酸混合液以及該預處理氣體,該預處理氣體中至少包含氨,其中該磷酸混合液和該預處理氣體反應形成一磷酸銨富液,該磷酸銨富液經由一第二導出管導出;以及一回收處理單元,用以收集被導出之該磷酸銨富液並處理該磷酸銨富液,以產生一磷酸銨回收液以及一氨氣,該磷酸銨回收液經由一第二導入管導回至該第二處理單元。 In one embodiment of the present invention, an ammonia-containing exhaust gas treatment device is provided, including: a first processing unit for containing an aqueous solution and a mixed gas, the mixed gas including at least ammonia, wherein the aqueous solution and the mixed gas The gas reaction forms an ammonia-containing aqueous solution and a pretreatment gas, the ammonia-containing aqueous solution is led out through a first outlet pipe; a regeneration unit for collecting the led-out ammonia-containing aqueous solution and processing the ammonia-containing aqueous solution to generate a regeneration An aqueous solution and an ammonia gas, the regenerated aqueous solution is led back to the first processing unit through a first introduction pipe; a second processing unit is configured to contain a phosphoric acid mixed solution and the pretreatment gas, and the pretreatment gas contains at least Ammonia, wherein the phosphoric acid mixed solution reacts with the pretreatment gas to form an ammonium phosphate rich solution, the ammonium phosphate rich solution is led out through a second outlet pipe; and a recovery processing unit for collecting the led out ammonium phosphate rich solution And processing the ammonium phosphate rich solution to produce an ammonium phosphate recovery liquid and an ammonia gas, the ammonium phosphate recovery liquid is led back to the Second processing unit.

在本發明之一實施例中,該再生單元及該回收處理單元分別為一蒸餾器,且該第一處理單元及該第二處理單元分別為一淋洗塔。 In one embodiment of the present invention, the regeneration unit and the recovery processing unit are each a distiller, and the first processing unit and the second processing unit are each a leaching tower.

在本發明之一實施例中,該混合氣體為經由一個二氧化碳吸收塔處理後之含氨氣體。 In one embodiment of the present invention, the mixed gas is an ammonia-containing gas processed through a carbon dioxide absorption tower.

在本發明之一實施例中,該第一處理單元之一操作溫度為0℃至60℃,該第二處理單元之一操作溫度為10℃至100℃。 In an embodiment of the present invention, an operating temperature of one of the first processing units is 0 ° C to 60 ° C, and an operating temperature of one of the second processing units is 10 ° C to 100 ° C.

1‧‧‧混合氣體 1‧‧‧ mixed gas

2‧‧‧預處理氣體 2‧‧‧ pretreatment gas

3‧‧‧尾氣 3‧‧‧ exhaust

11‧‧‧第一階段淨化處理程序 11‧‧‧The first stage purification process

111‧‧‧水溶液 111‧‧‧ water solution

112‧‧‧含氨水溶液 112‧‧‧Ammonia solution

12‧‧‧第二階段淨化處理程序 12‧‧‧Second stage purification process

121‧‧‧磷酸混合液 121‧‧‧ phosphoric acid mixed solution

122‧‧‧磷酸銨富液 122‧‧‧ ammonium phosphate rich solution

13‧‧‧再生處理程序 13‧‧‧ regeneration process

131‧‧‧再生水溶液 131‧‧‧ regeneration aqueous solution

14‧‧‧回收處理程序 14‧‧‧Recycling process

141‧‧‧磷酸銨回收液 141‧‧‧Ammonium phosphate recovery liquid

41‧‧‧第一處理單元 41‧‧‧first processing unit

411‧‧‧水溶液 411‧‧‧water solution

412‧‧‧含氨水溶液 412‧‧‧aqueous ammonia solution

413‧‧‧第一導出管 413‧‧‧first outlet tube

414‧‧‧第一輸送管 414‧‧‧The first delivery pipe

415‧‧‧第一泵 415‧‧‧The first pump

42‧‧‧第二處理單元 42‧‧‧Second Processing Unit

421‧‧‧磷酸混合液 421‧‧‧ phosphoric acid mixed solution

422‧‧‧磷酸銨富液 422‧‧‧ammonium phosphate rich solution

423‧‧‧第二導出管 423‧‧‧Second outlet tube

43‧‧‧再生單元 43‧‧‧Regeneration unit

431‧‧‧再生水溶液 431‧‧‧Regenerated aqueous solution

432‧‧‧第一導入管 432‧‧‧The first introduction tube

44‧‧‧回收處理單元 44‧‧‧Recycling unit

441‧‧‧磷酸銨回收液 441‧‧‧Ammonium Phosphate Recovery Solution

442‧‧‧第二導入管 442‧‧‧Second introduction pipe

45‧‧‧二氧化碳吸收塔 45‧‧‧CO2 absorption tower

451‧‧‧第二輸送管 451‧‧‧second duct

452‧‧‧第二泵 452‧‧‧Second Pump

46‧‧‧純水儲存槽 46‧‧‧Pure water storage tank

461‧‧‧純水輸送管 461‧‧‧Pure water delivery pipe

47‧‧‧磷酸儲存槽 47‧‧‧Phosphoric acid storage tank

471‧‧‧磷酸輸送管 471‧‧‧ phosphoric acid delivery tube

第1圖:本發明一實施例之含氨廢氣處理方法之流程方塊圖。 FIG. 1 is a flow block diagram of an ammonia-containing exhaust gas treatment method according to an embodiment of the present invention.

第2圖:本發明一實施例之不同溫度下氨氣的熱力學平衡特性圖。 FIG. 2 is a thermodynamic equilibrium characteristic diagram of ammonia gas at different temperatures according to an embodiment of the present invention.

第3圖:本發明一實施例之NH3-H3PO4-H2O系統之氣液相熱力平衡圖。 FIG. 3 is a gas-liquid phase thermodynamic equilibrium diagram of an NH 3 -H 3 PO 4 -H 2 O system according to an embodiment of the present invention.

第4圖:本發明一實施例之含氨廢氣處理裝置之示意圖。 FIG. 4 is a schematic diagram of an ammonia-containing exhaust gas treatment device according to an embodiment of the present invention.

為了讓本發明之上述及其他目的、特徵、優點能更明顯易懂,下文將特舉本發明較佳實施例,並配合所附圖式,作詳細說明如下。再者,本發明所提到的方向用語,例如上、下、頂、底、前、後、左、右、內、外、側面、周圍、中央、水平、橫向、垂直、縱向、軸向、徑向、最上層或最下層等,僅是參考附加圖式的方向。因此,使用的方向用語是用以說明及理解本發明,而非用以限制本發明。 In order to make the above and other objects, features, and advantages of the present invention more comprehensible, the following describes the preferred embodiments of the present invention and the accompanying drawings in detail, as follows. Furthermore, the directional terms mentioned in the present invention include, for example, top, bottom, top, bottom, front, back, left, right, inside, outside, side, periphery, center, horizontal, horizontal, vertical, vertical, axial, The radial direction, the uppermost layer, or the lowermost layer, etc., are only directions referring to the attached drawings. Therefore, the directional terms used are for explaining and understanding the present invention, but not for limiting the present invention.

請參照第1圖所示,本發明一實施例之含氨廢氣處理方法主要包含下列步驟:提供一混合氣體1,該混合氣體1中包含氨;將該混合氣體1導入一第一階段淨化程序11中與一水溶液111接觸,使該混合氣體1中的氨被該水溶液111吸收,以形成一含氨水溶液112(亦稱為為富氨水溶液)及一預處理氣體(亦稱為預淨處理氣體)2,可選擇將該含氨水溶液導入一再生處理程序13中,以去除該含氨水溶液112中之氨而獲得一再生水溶液131。另可選擇性的將將該再生水溶液131導回至該第一階段淨化程序11中。該預處理氣體2於一第二階段淨化程序12與一磷酸混合液121接觸,使該磷酸混合液121與該預處理氣體反應形成一磷酸銨富液122;對該磷酸銨富液進行一回收處理程序14,以去除該磷酸銨富液122中的一部分氨,而得到一磷酸銨回收液141;以及將該磷酸銨回收液141導回未被處理之預處理氣體2中,使該磷酸銨回收液141吸收該預處理氣體2中之氨,以形成一氨水吸收液供循環使用。本發明將於下文利用第1至2圖逐一詳細說明一實施例之上述各步驟的實施細節及其原理。 Please refer to FIG. 1, an ammonia-containing exhaust gas treatment method according to an embodiment of the present invention mainly includes the following steps: providing a mixed gas 1 containing ammonia; and introducing the mixed gas 1 into a first-stage purification process 11 in contact with an aqueous solution 111, so that the ammonia in the mixed gas 1 is absorbed by the aqueous solution 111 to form an ammonia-containing aqueous solution 112 (also referred to as an ammonia-rich aqueous solution) and a pretreatment gas (also referred to as a pre-cleaning treatment) Gas) 2. The ammonia-containing aqueous solution may optionally be introduced into a regeneration processing program 13 to remove ammonia in the ammonia-containing aqueous solution 112 to obtain a regenerating aqueous solution 131. Alternatively, the regenerated aqueous solution 131 may be selectively returned to the first-stage purification procedure 11. The pre-treatment gas 2 is in contact with a phosphoric acid mixed solution 121 in a second-stage purification process 12 so that the phosphoric acid mixed solution 121 reacts with the pre-treated gas to form an ammonium phosphate rich solution 122; the ammonium phosphate rich solution is recovered A processing procedure 14 to remove a part of ammonia in the ammonium phosphate rich solution 122 to obtain an ammonium phosphate recovery solution 141; and returning the ammonium phosphate recovery solution 141 to the untreated pretreatment gas 2 to make the ammonium phosphate The recovery liquid 141 absorbs ammonia in the pretreatment gas 2 to form an ammonia water absorption liquid for recycling. The present invention will be described in detail below with reference to Figures 1 and 2 for the implementation details and principles of the above steps of an embodiment.

請參照第1圖所示,本發明一實施例之含氨廢氣處理方法首先係:提供連續的一混合氣體1,該混合氣體1中包含氨。在本步驟中,該混合氣體1可以是經由一個二氧化碳吸收塔處理後之含氨氣體。較佳地,該混合氣體1為經由煉鐵熱風爐廢氣或其他製程單元所產生含二氧化碳之氣體經由氨水吸收液吸收二氧化碳後之尾氣。在該含氨氣體中,通常包含 10000ppm至50000ppm(5%)的氨氣。 Referring to FIG. 1, an ammonia-containing exhaust gas treatment method according to an embodiment of the present invention is firstly: providing a continuous mixed gas 1, and the mixed gas 1 includes ammonia. In this step, the mixed gas 1 may be an ammonia-containing gas processed through a carbon dioxide absorption tower. Preferably, the mixed gas 1 is the tail gas after the carbon dioxide-containing gas generated by the ironmaking hot blast furnace exhaust gas or other process units absorbs the carbon dioxide through the ammonia water absorption liquid. The ammonia-containing gas usually contains 10,000 ppm to 50,000 ppm (5%) of ammonia.

接著,本發明一實施例之含氨廢氣處理方法係將該混合氣體1與一水溶液111接觸,以進行第一階段淨化程序11,使該混合氣體1中一部分氨氣被去除。該混合氣體1中的氨被該水溶液111吸收,因而該水溶液111吸收氨氣後形成一含氨水溶液112,以及該混合氣體1去除一部分氨氣後形成一預處理氣體2。較佳的,以體積(或重量)百分比計,該混合氣體1去除的氨氣部份係佔該混合氣體1內原總氨氣含量的80至98%。該水溶液可以為純水,或經過再生處理過後含有氨之再生水。經過該水溶液處理後,混合氣體1中的部分氨氣溶解於水中成為銨離子。於本實施例中,經第一階段淨化程序處理過後之預處理氣體2,已可將預處理氣體2中的氨氣含量初步降至1000~5000ppm;由於該氨氣含量並不需很低,因此所使用的該水溶液之潔淨度要求較低(例如,水溶液中銨的含量)且操作溫度可以較高,因而可以降低操作成本。應可理解的是,如需較佳的處理效率,第一階段淨化程序可操作於一低溫操作條件,以緩和氨氣逸散之問題。 Next, an ammonia-containing exhaust gas treatment method according to an embodiment of the present invention is to contact the mixed gas 1 with an aqueous solution 111 to perform a first-stage purification process 11 so that a part of the ammonia gas in the mixed gas 1 is removed. The ammonia in the mixed gas 1 is absorbed by the aqueous solution 111, so that the aqueous solution 111 absorbs the ammonia gas to form an ammonia-containing aqueous solution 112, and the mixed gas 1 removes a part of the ammonia gas to form a pretreatment gas 2. Preferably, in terms of volume (or weight) percentage, the ammonia gas removed by the mixed gas 1 accounts for 80 to 98% of the original total ammonia content in the mixed gas 1. The aqueous solution may be pure water or regenerated water containing ammonia after the regeneration treatment. After the aqueous solution treatment, part of the ammonia gas in the mixed gas 1 is dissolved in water to become ammonium ions. In this embodiment, the pre-treatment gas 2 after the first-stage purification process has been able to reduce the ammonia content in the pre-treatment gas 2 to 1000 to 5000 ppm initially; since the ammonia content is not required to be very low, Therefore, the cleanliness requirements of the aqueous solution used are low (for example, the content of ammonium in the aqueous solution) and the operating temperature can be higher, so the operating cost can be reduced. It should be understood that if better treatment efficiency is required, the first-stage purification process can be operated at a low temperature operating condition to alleviate the problem of ammonia gas escape.

本發明一實施例之含氨廢氣處理方法於第一階段淨化程序11後,隨後進行第二階段淨化程序12,其係將該預處理氣體2與一磷酸混合液121接觸,使該磷酸混合液121與該預處理氣體2反應形成一磷酸銨富液122(即,NH3/H3PO4莫爾比大於1.4)。如此,經處理過後的預處理氣體2中的大部分氨氣與磷酸混合液反應,形成磷酸銨而去除,最後將處理完後之尾氣3排出。於本實施例中,經過第一階段淨化程序11及第二階段淨化程序12,尾氣中之氨氣濃度可降至小於50ppm。該磷酸混合液121可以是磷酸與水組成之溶液,或是磷酸、磷酸銨及水組成之混合液,例如為含有磷酸5至40wt%之磷酸水溶液。因磷酸為三質子酸,具有較多的氫基可以被銨基取代,因而能夠吸收較多的氨氣,且生成的該磷酸銨富液122具有H3PO4、(NH4)H2PO4、(NH4)2HPO4及(NH4)3PO4等成分可做為肥料使用,也可再生循環使用。該磷酸銨富液122以重量百分比計例如包含5至40wt%的H3PO4。而一般以該溶液中原始NH3與H3PO4摩爾數比率做為吸收飽和指標,磷酸混合液141中NH3/H3PO4摩爾數比率為1~1.4,磷酸銨富液122中NH3/H3PO4摩爾數比率則小於1.8。 An ammonia-containing exhaust gas treatment method according to an embodiment of the present invention is followed by a first-stage purification procedure 11 and then a second-stage purification procedure 12, which involves contacting the pretreatment gas 2 with a phosphoric acid mixed solution 121 to make the phosphoric acid mixed solution 121 reacts with the pretreatment gas 2 to form ammonium monophosphate rich liquid 122 (ie, the NH 3 / H 3 PO 4 molar ratio is greater than 1.4). In this way, most of the ammonia gas in the treated pretreatment gas 2 reacts with the phosphoric acid mixed solution to form ammonium phosphate and is removed. Finally, the tail gas 3 after the treatment is discharged. In this embodiment, after the first-stage purification process 11 and the second-stage purification process 12, the ammonia gas concentration in the exhaust gas can be reduced to less than 50 ppm. The phosphoric acid mixed solution 121 may be a solution composed of phosphoric acid and water, or a mixed solution composed of phosphoric acid, ammonium phosphate, and water, for example, an aqueous phosphoric acid solution containing 5 to 40 wt% of phosphoric acid. Because phosphoric acid is a triprotic acid, it has more hydrogen groups that can be replaced by ammonium groups, so it can absorb more ammonia gas, and the produced ammonium phosphate rich solution 122 has H 3 PO 4 and (NH 4 ) H 2 PO 4 , (NH 4 ) 2 HPO 4 and (NH 4 ) 3 PO 4 and other components can be used as fertilizer, can also be recycled and used. The ammonium phosphate rich liquid 122 contains, for example, 5 to 40% by weight of H 3 PO 4 . Generally, the molar ratio of the original NH 3 to H 3 PO 4 in the solution is used as an absorption saturation index. The molar ratio of NH 3 / H 3 PO 4 in the phosphoric acid mixed solution 141 is 1 to 1.4. The molar ratio of 3 / H 3 PO 4 is less than 1.8.

在本實施例中,經過吸收後的該磷酸銨富液122會導出至進一回收處理程序14,以進一步去除該磷酸銨富液122中的一部分氨,而得到一磷酸銨回收液141。於本實施例中,該磷酸混合液121與該磷酸銨回收液141為相同之溶液,兩者僅銨的含量不同。於其他實施例中,該磷酸混合液121為該磷酸銨回收液141再添加磷酸調整磷酸含量之溶液。於本實施例中,所述回收處理程序14可以為利用一水蒸氣將該磷酸銨富液122中的銨還原成氣態氨,而去除該磷酸銨富液122中的一部分氨,其中磷酸混合液141中NH3/H3PO4摩爾數比率為1~1.4,磷酸銨富液122中NH3/H3PO4摩爾數比率則小於1.8。於本實施例中,該水蒸氣可利用煉鋼熱風爐或煉焦爐所產生之廢熱對水加溫所生成,如此可以降低操作成本。其他可將該磷酸銨富液122中銨去除方式也在考量之內。 In this embodiment, the ammonium phosphate rich solution 122 after being absorbed is exported to a recovery processing program 14 to further remove a part of ammonia in the ammonium phosphate rich solution 122 to obtain an ammonium phosphate recovery solution 141. In this embodiment, the phosphoric acid mixed solution 121 and the ammonium phosphate recovery solution 141 are the same solution, and only the ammonium content of the two is different. In other embodiments, the phosphoric acid mixed solution 121 is a solution in which the phosphoric acid content is adjusted by adding phosphoric acid to the ammonium phosphate recovery solution 141. In this embodiment, the recovery process 14 may be to reduce ammonium in the ammonium phosphate rich solution 122 to gaseous ammonia by using a water vapor, and remove a part of the ammonia in the ammonium phosphate rich solution 122, wherein the phosphoric acid mixed solution the NH 3 / H 3 PO 4 molar ratio of the number 141 is 1 to 1.4, the rich ammonium phosphate solution NH 3 / H 3 PO 4 ratio of 122 moles of less than 1.8. In this embodiment, the water vapor can be generated by heating the water with waste heat generated from a steelmaking hot blast stove or a coke oven, so that the operating cost can be reduced. Other ways to remove ammonium from the ammonium phosphate rich solution 122 are also considered.

在本實施例中,經過回收處理過後之該磷酸銨回收液141最後可以導回另一尚未處理之預處理氣體2中,使該磷酸銨回收液吸收該另一預處理氣體中之氨,因而形成一氨水吸收液供循環使用,例如應用於處理經由煉鋼熱風爐或煉焦爐所產生之廢氣以吸收其二氧化碳,該廢氣被吸收二氧化碳之後剩下的尾氣也就成為本實施例一開始提供之混合氣體1。 In this embodiment, the recovered ammonium phosphate recovery liquid 141 can be finally returned to another unprocessed pretreatment gas 2 after the recovery treatment, so that the ammonium phosphate recovery liquid absorbs ammonia in the other pretreatment gas, so An ammonia water absorbing solution is formed for recycling, for example, it is used to treat the exhaust gas generated by a steelmaking hot blast stove or a coke oven to absorb its carbon dioxide, and the exhaust gas remaining after the exhaust gas is absorbed by the carbon dioxide is also provided at the beginning of this embodiment. Mixed gas 1.

如上所述,在一實施例中,進行第一階段淨化程序後,該混合氣體1中的氨被該水溶液111吸收形成一含氨水溶液112,可選擇將該含氨水溶液導入一再生處理程序13中,以去除該含氨水溶液112中之氨而獲得一再生水溶液131。於本實施例中,所述再生處理程序13可以為利用一水蒸氣將該含氨水溶液112中的銨還原成氣態氨,而去除該含氨水溶液112中的一部分氨。於本實施例中,該水蒸氣可利用生產過程中所產生之廢熱對水加溫所生成(例如:煉鋼熱風爐或煉焦爐所產生之廢熱),如此可以降低操作成本。其他可將該含氨水溶液112中氨去除方式也在考量之內。 As described above, in one embodiment, after the first-stage purification process is performed, the ammonia in the mixed gas 1 is absorbed by the aqueous solution 111 to form an ammonia-containing aqueous solution 112, and the ammonia-containing aqueous solution may optionally be introduced into a regeneration processing program 13 In order to remove the ammonia in the ammonia-containing aqueous solution 112, a regenerated aqueous solution 131 is obtained. In this embodiment, the regeneration process 13 may be to reduce ammonium in the ammonia-containing aqueous solution 112 to gaseous ammonia by using a water vapor, and remove a part of the ammonia in the ammonia-containing aqueous solution 112. In this embodiment, the water vapor can be generated by heating the water with waste heat generated during the production process (for example, waste heat generated from a steelmaking hot air furnace or a coke oven), which can reduce operating costs. Other ways to remove ammonia from the ammonia-containing aqueous solution 112 are also considered.

請參照第2圖所示,其示出了在不同溫度下氨氣的熱力學平衡特性。當水溶液與氨氣接觸溫度太高時,氨氣容易自水溶液中逸散出來,而造成吸收效率不佳。因此,為符合環保需求,在一實施例中,第一階段淨化程序11時,將該混合氣體1與該水溶液111接觸,該水溶液111之一操作溫度可能為0℃至60℃,經由降低水溶液131的潔淨度(即允許較高氨 濃度)與增加淨化程序11溫度,可大幅降低操作成本,雖會增加預處理氣體2中氨之濃度;預處理氣體2中的氨則能再由淨化程序12予以去除至環保要求。應可理解的是,當第一階段淨化程序11需要較佳的氨氣去除效率時,可以額外施加能源使該水溶液111之操作溫度低於室溫。 Please refer to FIG. 2, which shows the thermodynamic equilibrium characteristics of ammonia gas at different temperatures. When the contact temperature between the aqueous solution and the ammonia gas is too high, the ammonia gas easily escapes from the aqueous solution, resulting in poor absorption efficiency. Therefore, in order to meet environmental protection requirements, in one embodiment, in the first stage purification process 11, the mixed gas 1 is contacted with the aqueous solution 111, and one of the aqueous solutions 111 may have an operating temperature of 0 ° C to 60 ° C. Cleanliness of 131 (i.e. allows higher ammonia Concentration) and increasing the temperature of the purification process 11 can greatly reduce the operating cost, although the ammonia concentration in the pretreatment gas 2 can be increased; the ammonia in the pretreatment gas 2 can be removed by the purification process 12 to environmental protection requirements. It should be understood that when the first-stage purification process 11 requires better ammonia gas removal efficiency, additional energy can be applied to make the operating temperature of the aqueous solution 111 lower than room temperature.

請參照第3圖所示,其示出了根據熱力學計算NH3-H3PO4-H2O系統之氣液相熱力平衡圖。本實施例為使用7mole/L之磷酸,於圖示中可以理解使用磷酸吸收氨氣在高溫下也可以有符合預期的淨化效果,而不需額外施加能源降低操作溫度。再者,先進行第一階段淨化程序11,使用該水溶液111吸收部分之氨氣,於第二階段淨化程序12中可以使用較少量之磷酸銨水溶液,降低操作成本及操作危險性。該磷酸銨富液122包含H3PO4、(NH4)H2PO4、(NH4)2HPO4及(NH4)3PO4,且較佳的操作條件為上述化合物總重量佔該磷酸銨回收液141之整體重量的5%至40%。為求有足夠的氫基與銨根交換並具有較佳的操作效率,該磷酸銨回收液141中的NH3/H3PO4莫爾比控制為小於1.4(亦可稱之為磷酸銨貧液)。且為維持較佳淨化能力,該磷酸銨富液122中的NH3/H3PO4莫爾比控制為小於1.8。 Please refer to FIG. 3, which shows the gas-liquid-phase thermodynamic equilibrium diagram of the NH 3 -H 3 PO 4 -H 2 O system calculated according to thermodynamics. In this embodiment, 7mole / L phosphoric acid is used. It can be understood in the figure that the use of phosphoric acid to absorb ammonia gas can also meet the expected purification effect at high temperatures without additional energy to reduce the operating temperature. Furthermore, the first-stage purification procedure 11 is first performed, and a part of the ammonia gas is absorbed by using the aqueous solution 111. In the second-stage purification procedure 12, a smaller amount of an ammonium phosphate aqueous solution can be used to reduce the operation cost and the operation danger. The ammonium phosphate rich solution 122 contains H 3 PO 4 , (NH 4 ) H 2 PO 4 , (NH 4 ) 2 HPO 4, and (NH 4 ) 3 PO 4 , and the preferred operating conditions are that the total weight of the compound accounts for the 5% to 40% of the entire weight of the ammonium phosphate recovery liquid 141. In order to obtain sufficient hydrogen group exchange with ammonium radical and have better operation efficiency, the NH 3 / H 3 PO 4 Mole ratio in the ammonium phosphate recovery liquid 141 is controlled to be less than 1.4 (also called ammonium phosphate liquid). And in order to maintain better purification ability, the NH 3 / H 3 PO 4 molar ratio in the ammonium phosphate rich liquid 122 is controlled to be less than 1.8.

參照第4圖所示,本發明之一種含氨廢氣處理裝置,其包含一第一處理單元41,用以容納一水溶液以及一混合氣體1,該混合氣體1中至少包含氨,其中該水溶液411透過淋洗與該混合氣體1接觸,該水溶液411和該混合氣體1反應後將該混合氣體1中的氨氣吸收形成一含氨水溶液412及一預處理氣體2,該含氨水溶液經由一第一導出管413導出,可選擇性地於設備中設置含氨水溶液儲存槽(未圖示)以存放該含氨水溶液412或直接輸送至一再生單元43,該再生單元43用以收集被導出之該含氨水溶液412並處理該含氨水溶液412以除去部分之銨離子,以產生一再生水溶液431以及一氨氣,經處理後的該再生水溶液431經由一第一導入管432導回至該第一處理單元41。如此,該再生水溶液431可循環利用於該第一處理單元41以初步去除該混合氣體1中的氨氣。在本實施例中,可設置一純水儲存槽46存放純水,當該再生水溶液431之純淨度不符合需求時,該純水儲存槽46經由一純水輸送管461輸送純水至該再生水溶液431以提高該再生水溶液431的純淨度。為降低操作成本,該第一處理單元41可操作於 室溫(例如,20℃至50℃)。 Referring to FIG. 4, an ammonia-containing exhaust gas treatment device according to the present invention includes a first processing unit 41 for containing an aqueous solution and a mixed gas 1. The mixed gas 1 includes at least ammonia, and the aqueous solution 411 It comes into contact with the mixed gas 1 through rinsing. After the aqueous solution 411 and the mixed gas 1 react, the ammonia gas in the mixed gas 1 is absorbed to form an ammonia-containing aqueous solution 412 and a pretreatment gas 2. The ammonia-containing aqueous solution passes through a first A lead-out tube 413 leads out, and an ammonia-containing aqueous solution storage tank (not shown) can be optionally set in the equipment to store the ammonia-containing aqueous solution 412 or directly sent to a regeneration unit 43 for collecting the discharged The ammonia-containing aqueous solution 412 is processed to remove part of the ammonium ions to generate a regenerated aqueous solution 431 and an ammonia gas. The treated regenerated aqueous solution 431 is guided back to the first via a first introduction pipe 432. A processing unit 41. In this way, the regenerated aqueous solution 431 can be recycled to the first processing unit 41 to initially remove the ammonia gas in the mixed gas 1. In this embodiment, a pure water storage tank 46 may be provided to store pure water. When the purity of the regenerated aqueous solution 431 does not meet the requirements, the pure water storage tank 46 sends pure water to the regeneration through a pure water delivery pipe 461. The aqueous solution 431 improves the purity of the regenerated aqueous solution 431. In order to reduce the operation cost, the first processing unit 41 can be operated at Room temperature (for example, 20 ° C to 50 ° C).

經過初步處理的一該混合氣體1後形成的該預處理氣體2通過一第一輸送管輸送至一第二處理單元42,於該第一輸送管可選擇性的設置一第一泵以調整該預處理氣體2進入該第二處理單元42的流量,該第二處理單元42用以容納一磷酸混合液421以及該預處理氣體2,且該預處理氣體2中至少包含氨。於本實施例中,該磷酸混合液421淋洗該預處理氣體2以使該磷酸混合液421和該預處理氣體2反應形成一淨化混合氣體及一磷酸銨富液422,其中該磷酸銨富液422吸收該預處理氣體2中所含之氨氣,經反應過後的該磷酸銨富液422經由一第二導出管423導出,可選擇性地於設備中設置磷酸銨富液儲存槽(未圖示)以存放該磷酸銨富液422,或直接輸送至一回收處理單元44。該回收處理單元44,用以收集被導出之該磷酸銨富液422並處理該磷酸銨富液422以除去部分之銨離子,以產生一磷酸銨回收液441以及一氨氣,經處理後的該磷酸銨回收液441經由一第二導入管442導回至該第二處理單元42。如此,該磷酸銨回收液441可循環利用於該第二處理單元42以去除預處理氣體2中的氨氣至目標值以下,而成為該淨化混合氣體,以達到環保需求。 The pretreatment gas 2 formed after the preliminary processing of the mixed gas 1 is transported to a second processing unit 42 through a first conveying pipe, and a first pump can be optionally set in the first conveying pipe to adjust the The flow rate of the pretreatment gas 2 entering the second processing unit 42. The second processing unit 42 is configured to contain a phosphoric acid mixed solution 421 and the pretreatment gas 2, and the pretreatment gas 2 includes at least ammonia. In this embodiment, the phosphoric acid mixed solution 421 rinses the pretreatment gas 2 so that the phosphoric acid mixed solution 421 and the pretreatment gas 2 react to form a purified mixed gas and an ammonium phosphate rich solution 422, wherein the ammonium phosphate is rich The liquid 422 absorbs the ammonia gas contained in the pretreatment gas 2 and the reacted ammonium phosphate rich liquid 422 is led out through a second outlet pipe 423. An ammonium phosphate rich liquid storage tank (not (Illustrated) to store the ammonium phosphate rich solution 422 or directly deliver it to a recovery processing unit 44. The recovery processing unit 44 is configured to collect the exported ammonium phosphate rich solution 422 and process the ammonium phosphate rich solution 422 to remove a part of ammonium ions to generate an ammonium phosphate recovery solution 441 and an ammonia gas. The ammonium phosphate recovery liquid 441 is returned to the second processing unit 42 through a second introduction pipe 442. In this way, the ammonium phosphate recovery liquid 441 can be recycled to the second processing unit 42 to remove the ammonia gas in the pretreatment gas 2 to a target value or less, and become the purified mixed gas to meet environmental protection requirements.

在一實施例中,該再生單元43及該回收處理單元44分別為一蒸餾器,且該再生單元43及該回收處理單元44係經由水蒸氣將該含氨水溶液412及該磷酸銨富液422中的銨去除形成該再生水溶液431及該磷酸銨回收液441。該水蒸氣可利用生產過程中所產生之廢熱對水加溫所生成(例如:煉鋼熱風爐或煉焦爐所產生之廢熱),如此可以降低操作成本。該第一處理單元41及該第二處理單元42可分別為一淋洗塔,例如填充式洗滌塔或文氏洗滌塔。在本實施例中,較佳的操作條件為H3PO4、(NH4)H2PO4、(NH4)2HPO4及(NH4)3PO4為上述化合物總重量佔該磷酸銨回收液441之整體重量的5%至40%。在本實施例中,可設置一磷酸儲存槽47存放磷酸,當H3PO4佔該磷酸銨回收液441之整體重量小於5%時,該磷酸儲存槽47經由一磷酸輸送管471輸送磷酸至該磷酸銨回收液441。為求有足夠的氫基與銨根交換並具有較佳的操作效率,該磷酸銨回收液441中的NH3/H3PO4莫爾比控制為小於1.4。且為為維持較佳淨化能力,該磷酸銨富液422中的NH3/H3PO4 莫爾比控制為小於1.8。 In one embodiment, the regeneration unit 43 and the recovery processing unit 44 are respectively a distiller, and the regeneration unit 43 and the recovery processing unit 44 are the ammonia-containing aqueous solution 412 and the ammonium phosphate rich solution 422 via water vapor. Removal of ammonium from the solution forms the regenerated aqueous solution 431 and the ammonium phosphate recovery solution 441. The water vapor can be generated by heating the water with the waste heat generated in the production process (for example, waste heat generated from a steelmaking hot blast stove or a coke oven), which can reduce operating costs. The first processing unit 41 and the second processing unit 42 may be a leaching tower, such as a packed washing tower or a Venturi washing tower. In this embodiment, the preferred operating conditions are H 3 PO 4 , (NH 4 ) H 2 PO 4 , (NH 4 ) 2 HPO 4 and (NH 4 ) 3 PO 4. The total weight of the above compounds accounts for the ammonium phosphate. 5% to 40% of the total weight of the recovery liquid 441. In this embodiment, a phosphoric acid storage tank 47 may be provided to store phosphoric acid. When H 3 PO 4 accounts for less than 5% of the total weight of the ammonium phosphate recovery solution 441, the phosphoric acid storage tank 47 transfers phosphoric acid to This ammonium phosphate recovery liquid 441. In order to obtain sufficient hydrogen group exchange with ammonium radicals and have better operation efficiency, the NH 3 / H 3 PO 4 molar ratio in the ammonium phosphate recovery liquid 441 is controlled to be less than 1.4. In order to maintain a better purification ability, the NH 3 / H 3 PO 4 molar ratio in the ammonium phosphate rich solution 422 is controlled to be less than 1.8.

在一實施例中,該混合氣體1為經由一個二氧化碳吸收塔45經氨水吸收法捕捉碳處理後之含氨氣體,並經由一第二輸送管451輸送至該第一處理單元41。該第二輸送管可裝有一第二泵452,以輸送該混合氣體1進入該第一處理單元41。 In one embodiment, the mixed gas 1 is an ammonia-containing gas that has been carbon-treated by a carbon dioxide absorption tower 45 through an ammonia water absorption method, and is transported to the first processing unit 41 through a second conveying pipe 451. The second conveying pipe may be provided with a second pump 452 to convey the mixed gas 1 into the first processing unit 41.

在一實施例中,該第一處理單元之一操作溫度為0℃至60℃,該第二處理單元之一操作溫度為10℃至100℃。 In an embodiment, an operating temperature of one of the first processing units is 0 ° C to 60 ° C, and an operating temperature of one of the second processing units is 10 ° C to 100 ° C.

如上所述,相較於習用技術,本發明之含氨廢氣處理方法及裝置係利用兩階段去除尾氣中所含之氨氣,確實可以降低尾氣所含之氨氣含量,進而提升空氣品質且符合環保法規;且本發明之含氨廢氣處理方法及裝置係利用一水溶液先行吸收尾氣中部分之氨氣含量,再使用磷酸銨溶液進行吸收,除了可以降低尾氣所含之氨氣含量外,亦可進一步提高含氨廢氣處理效率,顯著降低操作費用。 As described above, compared to conventional technology, the method and device for treating ammonia-containing exhaust gas of the present invention uses two stages to remove ammonia gas contained in the exhaust gas, which can indeed reduce the ammonia gas content of the exhaust gas, thereby improving air quality and conforming to Environmental protection regulations; and the method and device for treating ammonia-containing exhaust gas of the present invention use an aqueous solution to first absorb the ammonia content in the exhaust gas, and then use an ammonium phosphate solution to absorb, in addition to reducing the ammonia gas content in the exhaust gas, it can also Further improve the efficiency of ammonia-containing waste gas treatment and significantly reduce operating costs.

雖然本發明已以較佳實施例揭露,然其並非用以限制本發明,任何熟習此項技藝之人士,在不脫離本發明之精神和範圍內,當可作各種更動與修飾,因此本發明之保護範圍當視後附之申請專利範圍所界定者為準。 Although the present invention has been disclosed in a preferred embodiment, it is not intended to limit the present invention. Any person skilled in the art can make various changes and modifications without departing from the spirit and scope of the present invention. The scope of protection shall be determined by the scope of the attached patent application.

Claims (10)

一種含氨廢氣處理方法,其包含步驟:(a)提供一混合氣體,該混合氣體中包含氨;(b)將該混合氣體與一水溶液接觸,使該混合氣體中的氨被該水溶液吸收,以形成一含氨水溶液及一預處理氣體;(c)將該預處理氣體與一磷酸混合液接觸,使該磷酸混合液與該預處理氣體反應形成一磷酸銨富液;(d)對該磷酸銨富液進行一回收處理程序,以去除該磷酸銨富液中的一部分氨,而得到一磷酸銨回收液;以及(e)將該磷酸銨回收液導回步驟(c)使該磷酸銨回收液吸收該步驟(b)之預處理氣體中之氨。A method for treating ammonia-containing exhaust gas, comprising the steps of: (a) providing a mixed gas containing ammonia; (b) contacting the mixed gas with an aqueous solution so that ammonia in the mixed gas is absorbed by the aqueous solution, To form an ammonia-containing aqueous solution and a pretreatment gas; (c) contacting the pretreatment gas with a phosphoric acid mixed solution, causing the phosphoric acid mixed solution to react with the pretreatment gas to form an ammonium phosphate rich solution; (d) the The ammonium phosphate rich solution is subjected to a recovery process to remove a portion of the ammonia in the ammonium phosphate rich solution to obtain an ammonium phosphate recovery solution; and (e) the ammonium phosphate recovery solution is returned to step (c) to cause the ammonium phosphate The recovery liquid absorbs ammonia in the pretreatment gas of step (b). 如申請專利範圍第1項所述之含氨廢氣處理方法,其中在步驟(b)之後更包含:(b1)將該含氨水溶液導入一再生處理程序,以去除該含氨水溶液中之氨而獲得一再生水溶液。The method for treating ammonia-containing exhaust gas according to item 1 of the scope of patent application, wherein after step (b), it further comprises: (b1) introducing the ammonia-containing aqueous solution into a regeneration treatment program to remove ammonia from the ammonia-containing aqueous solution; A regenerated aqueous solution was obtained. 如申請專利範圍第1項所述之含氨廢氣處理方法,其中在步驟(b)中,該水溶液之一操作溫度為0℃至60℃。The method for treating ammonia-containing exhaust gas according to item 1 of the scope of patent application, wherein in step (b), an operating temperature of one of the aqueous solutions is 0 ° C to 60 ° C. 如申請專利範圍第3項所述之含氨廢氣處理方法,其中該磷酸混合液之操作溫度為10℃至100℃。The method for treating ammonia-containing exhaust gas as described in item 3 of the scope of patent application, wherein the operating temperature of the phosphoric acid mixture is 10 ° C to 100 ° C. 如申請專利範圍第1項所述之含氨廢氣處理方法,其中在步驟(c)中,該磷酸銨富液包含H3PO4、(NH4)H2PO4、(NH4)2HPO4及(NH4)3PO4,且上述化合物總重量佔該磷酸銨回收液之整體重量的5%至40%。The method for treating ammonia-containing exhaust gas according to item 1 of the scope of patent application, wherein in step (c), the ammonium phosphate rich solution contains H 3 PO 4 , (NH 4 ) H 2 PO 4 , (NH 4 ) 2 HPO 4 and (NH 4 ) 3 PO 4 , and the total weight of the above compounds accounts for 5% to 40% of the total weight of the ammonium phosphate recovery solution. 如申請專利範圍第1項所述之含氨廢氣處理方法,其中在進行步驟(d)後,該磷酸銨回收液中的NH3/H3PO4莫爾比小於1.4,及在進行步驟(c)後,及該磷酸銨富液中的NH3/H3PO4莫爾比小於1.8。The method for treating ammonia-containing exhaust gas according to item 1 of the scope of patent application, wherein after step (d) is performed, the NH 3 / H 3 PO 4 molar ratio in the ammonium phosphate recovery liquid is less than 1.4, and the step ( c), and the NH 3 / H 3 PO 4 molar ratio in the ammonium phosphate rich solution is less than 1.8. 一種含氨廢氣處理裝置,其包含:一第一處理單元,用以容納一水溶液以及一混合氣體,該混合氣體中至少包含氨,其中該水溶液和該混合氣體反應形成一含氨水溶液及一預處理氣體,該含氨水溶液經由一第一導出管導出;一再生單元,用以收集被導出之該含氨水溶液並處理該含氨水溶液,以產生一再生水溶液以及一氨氣,該再生水溶液經由一第一導入管導回至該第一處理單元;一第二處理單元,用以容納一磷酸混合液以及該預處理氣體,該預處理氣體中至少包含氨,其中該磷酸混合液和該預處理氣體反應形成一磷酸銨富液,該磷酸銨富液經由一第二導出管導出;以及一回收處理單元,用以收集被導出之該磷酸銨富液並處理該磷酸銨富液,以產生一磷酸銨回收液以及一氨氣,該磷酸銨回收液經由一第二導入管導回至該第二處理單元。An ammonia-containing exhaust gas treatment device includes: a first processing unit for containing an aqueous solution and a mixed gas, the mixed gas including at least ammonia, wherein the aqueous solution and the mixed gas react to form an ammonia-containing aqueous solution and a pretreatment A processing gas, the ammonia-containing aqueous solution is led through a first outlet pipe; a regeneration unit for collecting the led-out ammonia-containing aqueous solution and processing the ammonia-containing aqueous solution to generate a regenerating aqueous solution and an ammonia gas, and the regenerating aqueous solution passes through A first introduction pipe leads back to the first processing unit; a second processing unit is configured to contain a phosphoric acid mixed solution and the pretreatment gas, and the pretreatment gas contains at least ammonia, wherein the phosphoric acid mixed solution and the pretreatment gas The processing gas reacts to form an ammonium phosphate rich solution, which is discharged through a second outlet pipe; and a recovery processing unit for collecting the exported ammonium phosphate rich solution and processing the ammonium phosphate rich solution to produce An ammonium phosphate recovery liquid and an ammonia gas, the ammonium phosphate recovery liquid is led back to the second processing unit through a second introduction pipe. 如申請專利範圍第7項所述之含氨廢氣處理裝置,其中該再生單元及該回收處理單元分別為一蒸餾器,且該第一處理單元及該第二處理單元分別為一淋洗塔。The ammonia-containing exhaust gas treatment device according to item 7 of the scope of the patent application, wherein the regeneration unit and the recovery treatment unit are each a distiller, and the first treatment unit and the second treatment unit are respectively a rinse tower. 如申請專利範圍第7項所述之含氨廢氣處理裝置,其中該混合氣體為經由一個二氧化碳吸收塔處理後之含氨氣體。The ammonia-containing exhaust gas treatment device according to item 7 of the scope of the patent application, wherein the mixed gas is an ammonia-containing gas processed through a carbon dioxide absorption tower. 如申請專利範圍第7項所述之含氨廢氣處理裝置,其中該第一處理單元之一操作溫度為0℃至60℃,該第二處理單元之一操作溫度為10℃至100℃。The ammonia-containing exhaust gas treatment device according to item 7 of the scope of the patent application, wherein one of the first processing unit has an operating temperature of 0 ° C to 60 ° C, and one of the second processing unit has an operating temperature of 10 ° C to 100 ° C.
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