TWI636968B - Method for recovering ammonia-containing wastewater - Google Patents

Method for recovering ammonia-containing wastewater Download PDF

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TWI636968B
TWI636968B TW106111007A TW106111007A TWI636968B TW I636968 B TWI636968 B TW I636968B TW 106111007 A TW106111007 A TW 106111007A TW 106111007 A TW106111007 A TW 106111007A TW I636968 B TWI636968 B TW I636968B
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gas
ammonia
wastewater
ammonium chloride
recovering ammonia
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TW201836996A (en
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盧祐增
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超重力有限公司
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Abstract

一種含氨氮廢水的回收方法,該含氨氮廢水為一含有氨的鹼性廢水,該回收方法包含:(a)將該鹼性廢水及一非活性氣體分別引入一第一旋轉填充床,透過氣提得到一含有氨氣的第一氣體及一鹼性廢液;(b)將該第一氣體與稀鹽酸混合並進行反應,以得到一含有氯化銨微粒的第二氣體及一含有氯化銨的第一回收液;及(c)將一製程水及該第二氣體分別引入一第二旋轉填充床,透過捕捉該第二氣體中的氯化銨微粒得到一含有氯化銨的第二回收液。本發明含氨氮廢水的回收方法藉由該氣提、反應及捕捉之步驟,可有效分離出該含氨氮廢水中的氨氮成分並得到含有高濃度氯化銨回收液。 A method for recovering ammonia-containing wastewater, the ammonia-containing nitrogen wastewater is an alkaline wastewater containing ammonia, and the recovery method comprises: (a) introducing the alkaline wastewater and an inert gas into a first rotating packed bed, respectively, through the gas Extracting a first gas containing ammonia gas and an alkaline waste liquid; (b) mixing the first gas with dilute hydrochloric acid and reacting to obtain a second gas containing ammonium chloride particles and a chlorination a first recovery liquid of ammonium; and (c) introducing a process water and the second gas into a second rotating packed bed, respectively, and capturing a second ammonium chloride-containing particle by capturing ammonium chloride particles in the second gas Recycled liquid. The method for recovering ammonia-containing nitrogen wastewater of the present invention can effectively separate the ammonia nitrogen component in the ammonia-containing nitrogen wastewater by the steps of stripping, reacting and capturing, and obtain a high concentration ammonium chloride recovery liquid.

Description

含氨氮廢水的回收方法 Method for recovering ammonia-containing wastewater

本發明是有關於一種廢水的回收方法,特別是指一種含氨氮廢水的回收方法。 The invention relates to a method for recovering wastewater, in particular to a method for recovering ammonia-containing wastewater.

工業產生的含氨氮廢水(例如印刷電路板工廠產生的蝕刻廢液),倘若直接排放至湖泊、河流、海洋等自然界的水體中,不僅可能會有重金屬污染的危險,其中氨氮更會造成優養化的問題,因此需要進行妥善的回收處理。 Industrially produced ammonia-containing wastewater (such as etching waste liquid produced by printed circuit board factories), if directly discharged into water bodies such as lakes, rivers, and oceans, may not only pose a risk of heavy metal pollution, but ammonia nitrogen will cause maintenance. The problem is solved, so it needs to be properly recycled.

現有工業上的含氨氮廢水回收方法一般是以氣提或使用薄膜的方式轉製為硫酸銨進行回收,或使用蒸餾的方式來產生氨水。然而,硫酸銨的產業應用價值偏低,成為大量的二次污染物,同時衍生出龐大的清運費用。另外,產生氨水的製程也有能耗較大的缺點,且受限於廢水中氨氮濃度可能導致氨水濃度低而不具回收效益的問題。 The existing industrial ammonia-containing nitrogen wastewater recovery method is generally carried out by gas stripping or conversion into ammonium sulfate for recycling, or by distillation to produce ammonia water. However, the industrial application value of ammonium sulfate is low, and it has become a large amount of secondary pollutants, and at the same time, a large amount of clear freight is derived. In addition, the process of producing ammonia water also has the disadvantage of large energy consumption, and is limited by the problem that the concentration of ammonia nitrogen in the wastewater may result in low ammonia concentration without recycling benefit.

TW 342382公開一種印刷電路板含銅廢液之回收方法,是透過沉澱、分離、強酸型陽離子交換樹脂(RH)、加入添加劑、加溫蒸發、萃取等多道程序將含銅物質回收再生利用,同時回收氯化銨。但離子交換樹脂的價格昂貴,且其加入的添加劑亦為氯化銨、氨水,不僅需要後續耗能的加熱蒸發程序,還會因此增加了原料的成本及廢液中氯化銨的含量。 TW 342382 discloses a method for recovering copper-containing waste liquid of a printed circuit board, which is used for recycling and recycling copper-containing substances through a plurality of procedures such as precipitation, separation, strong acid type cation exchange resin (RH), adding additives, heating and evaporation, and extraction. At the same time, ammonium chloride is recovered. However, the ion exchange resin is expensive, and the added additive is also ammonium chloride and ammonia water, which not only requires a heating and evaporation process of subsequent energy consumption, but also increases the cost of the raw material and the ammonium chloride content in the waste liquid.

因此,本發明之目的,即在提供一種含氨氮廢水的回收方法,可以克服上述先前技術的缺點。 Accordingly, it is an object of the present invention to provide a method for recovering ammonia-containing wastewater which overcomes the disadvantages of the prior art described above.

於是,在本發明含氨氮廢水的回收方法中,該含氨氮廢水為一含有氨的鹼性廢水,該回收方法包含以下步驟:(a)將該鹼性廢水及一非活性氣體分別引入一第一旋轉填充床,透過氣提(gas stripping)得到一含有氨氣的第一氣體及一鹼性廢液;(b)將該第一氣體與稀鹽酸混合並進行反應,以得到一含有氯化銨微粒的第二氣體及一含有氯化銨的第一回收液;及(c)將一製程水(process water)及該第二氣體分別引入一第二旋轉填充床,透過捕捉(trapping)該第二氣體中的氯化銨微粒得到一含有氯化銨的第二回收液。 Therefore, in the method for recovering ammonia-containing wastewater according to the present invention, the ammonia-containing nitrogen wastewater is an alkaline wastewater containing ammonia, and the recovery method comprises the steps of: (a) introducing the alkaline wastewater and an inert gas into the first a rotating packed bed, gas stripping to obtain a first gas containing ammonia gas and an alkaline waste liquid; (b) mixing the first gas with dilute hydrochloric acid and reacting to obtain a chlorination a second gas of ammonium fine particles and a first recovered liquid containing ammonium chloride; and (c) introducing a process water and the second gas into a second rotating packed bed, respectively, by trapping the The ammonium chloride fine particles in the second gas give a second recovered liquid containing ammonium chloride.

本發明之功效在於:本發明含氨氮廢水的回收方法藉由該氣提、反應及捕捉之步驟,可有效分離出氨氮成分並得到含有高濃度氯化銨回收液。 The invention has the effect that the method for recovering ammonia-containing wastewater of the present invention can effectively separate the ammonia nitrogen component by the steps of stripping, reacting and capturing, and obtain a high concentration ammonium chloride recovery liquid.

以下將就本發明內容進行詳細說明:較佳地,該鹼性廢水是以一含有銨離子及重金屬離子的酸性廢水與過量鹼進行中和,並經過濾而得。 Hereinafter, the present invention will be described in detail. Preferably, the alkaline waste water is neutralized by an acidic wastewater containing ammonium ions and heavy metal ions and an excess of alkali, and is obtained by filtration.

較佳地,在該步驟(b)中,該第一氣體是先與冰水混合後,再與該稀鹽酸混合並進行反應。更佳地,該冰水是來自於該步驟(c)的該製程水。 Preferably, in the step (b), the first gas is first mixed with ice water, and then mixed with the diluted hydrochloric acid to carry out a reaction. More preferably, the ice water is the process water from the step (c).

較佳地,在該步驟(c)中,該製程水是該第二回收液與一補充水合併後再回流至該第二旋轉填充床,以繼續對該第二氣體中的氯化銨微粒進行捕捉。 Preferably, in the step (c), the process water is combined with a supplementary water and then returned to the second rotating packed bed to continue the ammonium chloride particles in the second gas. Capture.

較佳地,在該步驟(b)中,該稀鹽酸是該第一回收液與濃鹽酸合併而得,以與該第一氣體進行反應。 Preferably, in the step (b), the dilute hydrochloric acid is obtained by combining the first recovered liquid with concentrated hydrochloric acid to react with the first gas.

較佳地,在該步驟(c)得到該第二回收液的同時,伴隨得到一第三氣體,且該第三氣體是與該步驟(a)中的非活性氣體合併後進行循環,以繼續進行該步驟(a)。 Preferably, in the step (c), the second recovered liquid is obtained, accompanied by obtaining a third gas, and the third gas is combined with the inert gas in the step (a) and then circulated to continue Carry out this step (a).

較佳地,在該步驟(a)中,該鹼性廢液是回流至該第一旋轉填充床。 Preferably, in the step (a), the alkaline waste liquid is refluxed to the first rotating packed bed.

較佳地,該步驟(b)是在一洗滌塔(scrubber)或一第三旋轉填充床中進行反應。 Preferably, step (b) is carried out in a scrubber or a third rotating packed bed.

更佳地,該經過濾而得的該鹼性廢水的pH值為11以上,以確保該鹼性廢水中的氨氮主要是以氨分子(NH3(aq))的形式存在。 More preferably, the pH of the alkaline wastewater obtained by filtration is 11 or more to ensure that the ammonia nitrogen in the alkaline wastewater is mainly in the form of ammonia molecules (NH 3 (aq) ).

較佳地,該步驟(b)中的該稀鹽酸的pH值為6以下。更佳地,該步驟(b)中的該稀鹽酸的pH值為2~6。 Preferably, the pH of the dilute hydrochloric acid in the step (b) is 6 or less. More preferably, the pH of the dilute hydrochloric acid in the step (b) is 2-6.

較佳地,在該步驟(b)中,該第一氣體與該稀鹽酸的混合流量比為10:1至1000:1。若流量比例過低,表示稀鹽酸的流量過大而會造成設備與操作成本增加;若流量比例過高,該第一氣體中的氨氣反應形成氯化銨的效率會偏低。 Preferably, in the step (b), the mixing flow ratio of the first gas to the dilute hydrochloric acid is from 10:1 to 1000:1. If the flow ratio is too low, it means that the flow rate of dilute hydrochloric acid is too large, which will cause an increase in equipment and operation cost; if the flow rate ratio is too high, the efficiency of ammonia reaction in the first gas to form ammonium chloride will be low.

較佳地,在該步驟(c)中,該第二氣體與該製程水的混合流量比為3:1至500:1。若流量比例過低,表示該製程水的流量過大而會造成設備所需體積與操作成本增加;若流量比例過高,氯化銨顆粒被捕捉至該第二回收液中的效率會偏低。 Preferably, in the step (c), the mixing flow ratio of the second gas to the process water is from 3:1 to 500:1. If the flow ratio is too low, it means that the flow rate of the process water is too large, which will increase the required volume and operation cost of the equipment; if the flow rate ratio is too high, the efficiency of capturing the ammonium chloride particles into the second recovered liquid will be low.

1‧‧‧鹼性廢水 1‧‧‧Alkaline wastewater

2‧‧‧非活性氣體 2‧‧‧Inactive gases

3‧‧‧第一旋轉填充床 3‧‧‧First rotating packed bed

31‧‧‧第一氣體 31‧‧‧First gas

32‧‧‧鹼性廢液 32‧‧‧Alkaline waste liquid

4‧‧‧濃鹽酸 4‧‧‧Concentrated hydrochloric acid

41‧‧‧稀鹽酸 41‧‧‧Diluted hydrochloric acid

5‧‧‧洗滌塔 5‧‧‧ Washing tower

51‧‧‧第二氣體 51‧‧‧second gas

52‧‧‧第一回收液 52‧‧‧First recovery liquid

6‧‧‧製程水 6‧‧‧Process water

7‧‧‧第二旋轉填充床 7‧‧‧Second rotating packed bed

71‧‧‧第三氣體 71‧‧‧ Third gas

72‧‧‧第二回收液 72‧‧‧Second recovery liquid

8‧‧‧補充水 8‧‧‧Supply water

9‧‧‧冰水吸收裝置 9‧‧‧Ice water absorption device

a~c‧‧‧步驟 a~c‧‧‧step

本發明之其他的特徵及功效,將於參照圖式的實施方式中清楚地呈現,其中:〔圖1〕是一配置示意圖,說明本發明之第一實施例的回收方法。 Other features and effects of the present invention will be apparent from the following description of the drawings, wherein: FIG. 1 is a schematic view showing a recycling method of the first embodiment of the present invention.

在本發明被詳細描述之前,應當注意在以下的說明內容中,類似的元件是以相同的編號來表示。 Before the present invention is described in detail, it should be noted that in the following description, similar elements are denoted by the same reference numerals.

本發明將就以下實施例來作進一步說明,但應瞭解的是,該等實施例僅為例示說明之用,而不應被解釋為本發明實施之限制。 The invention is further described in the following examples, but it should be understood that these examples are for illustrative purposes only and are not to be construed as limiting.

參閱圖1,本發明含氨氮廢水的回收方法之第一實施例包含以下步驟: Referring to Figure 1, a first embodiment of the method for recovering ammonia-containing wastewater of the present invention comprises the following steps:

[前處理][pre-processing]

將一含有銨離子及重金屬離子的酸性廢水與過量鹼進行中和,並經過濾而得到一鹼性廢水1。在本實施例中,該酸性廢水是含有氯化銨(NH4Cl)及鈷離子的稀鹽酸(HCl)廢水。該鹼為氫氧化鈉(NaOH)水溶液,以使該經過濾而得的鹼性廢水的pH值為11以上。 An acidic wastewater containing ammonium ions and heavy metal ions is neutralized with an excess of alkali, and filtered to obtain an alkaline wastewater 1. In this embodiment, the acidic wastewater is dilute hydrochloric acid (HCl) wastewater containing ammonium chloride (NH 4 Cl) and cobalt ions. The base is an aqueous solution of sodium hydroxide (NaOH) so that the pH of the filtered alkaline wastewater is 11 or more.

[氣提步驟(a)][Air stripping step (a)]

將上述的鹼性廢水1及一非活性氣體2分別以15L/min及30m3/min的流量引入一第一旋轉填充床3(填充床內徑為370mm,填充床外徑為670mm,填充床軸向高度為315mm,轉速為1100rpm,填充物為不鏽鋼網,不鏽鋼網的比表面積為850m2/m3),透過氣提得到一含有氨氣的第一氣體31及一鹼性廢液 32,藉以使該鹼性廢水1中的氨氮以氨氣(NH3(g))的形式被氣提至該第一氣體31中。 The above alkaline wastewater 1 and an inert gas 2 are introduced into a first rotating packed bed 3 at a flow rate of 15 L/min and 30 m 3 /min, respectively (the inner diameter of the packed bed is 370 mm, and the outer diameter of the packed bed is 670 mm, packed bed). The axial height is 315 mm, the rotational speed is 1100 rpm, the filler is a stainless steel mesh, and the stainless steel mesh has a specific surface area of 850 m 2 /m 3 ), and a first gas 31 containing ammonia gas and an alkaline waste liquid 32 are obtained by gas stripping. The ammonia nitrogen in the alkaline wastewater 1 is thereby stripped into the first gas 31 in the form of ammonia gas (NH 3 (g) ).

在本實施例中,該非活性氣體2是空氣。該鹼性廢液32可再進行回流至該第一旋轉填充床3,以提高氣提的效率,之後再進行廢液排放。 In the present embodiment, the inert gas 2 is air. The alkaline waste liquid 32 can be further refluxed to the first rotating packed bed 3 to increase the efficiency of stripping, followed by waste liquid discharge.

[反應步驟(b)][Reaction step (b)]

將上述氣提步驟(a)得到的第一氣體31導入一冰水吸收裝置9中與冰水混合,以將該第一氣體31中的部分氨氣吸收至冰水中,排出的該第一氣體31再以30m3/min的流量引入一濕式洗滌塔5(洗滌塔直徑為600mm,洗滌塔高度為3.5m,填充物為塑膠材料,塑膠材料的比表面積為168m2/m3)的底部,並將稀鹽酸41(pH值為2~6)以250L/min的流量引入該洗滌塔5的頂部,該稀鹽酸41在該洗滌塔5流下的過程中與該逆流而上的第一氣體31接觸混合並進行反應(HCl+NH3→NH4Cl),以得到一含有氯化銨微粒的第二氣體51(呈白煙狀)及一含有氯化銨的第一回收液52。該第二氣體51自該洗滌塔5的頂端排出。該第一回收液52自該洗滌塔5的底端排出,並可經熱交換後收集含氯化銨的溶液。 The first gas 31 obtained in the stripping step (a) is introduced into an ice water absorption device 9 and mixed with ice water to absorb a part of the ammonia gas in the first gas 31 into the ice water, and the first gas discharged. 31 and then introduced into a wet scrubber 5 (washing tower diameter of 600 mm, washing tower height of 3.5 m, filling material of plastic material, plastic material specific surface area of 168 m 2 /m 3 ) at a flow rate of 30 m 3 /min And dilute hydrochloric acid 41 (pH 2 to 6) is introduced into the top of the scrubbing tower 5 at a flow rate of 250 L/min, and the dilute hydrochloric acid 41 flows down the scrubbing tower 5 with the first gas in the countercurrent flow The mixture was contacted with 31 and reacted (HCl + NH 3 → NH 4 Cl) to obtain a second gas 51 (white smoke) containing ammonium chloride particles and a first recovery liquid 52 containing ammonium chloride. This second gas 51 is discharged from the top end of the washing tower 5. The first recovered liquid 52 is discharged from the bottom end of the washing column 5, and a solution containing ammonium chloride is collected after heat exchange.

在本實施例中,該冰水吸收裝置9為一旋轉填充床。該第一回收液52排出該洗滌塔5後與該濃鹽酸4合併後得到稀鹽酸41進行回流,以繼續在該洗滌塔5中與該第一氣體31進行反應,藉此提升該第一回收液52中氯化銨的濃度。 In the present embodiment, the ice water absorption device 9 is a rotating packed bed. After the first recovery liquid 52 is discharged from the washing column 5 and combined with the concentrated hydrochloric acid 4, dilute hydrochloric acid 41 is obtained to be refluxed to continue the reaction with the first gas 31 in the washing column 5, thereby lifting the first recovery. The concentration of ammonium chloride in liquid 52.

[捕捉步驟(c)][Capture Step (c)]

將一製程水6及上述反應步驟(b)得到的第二氣體51分別以600L/min及30m3/min的流量引入一第二旋轉填充床7(填充 床規格、轉速及填充物與該第一旋轉填充床3相同),透過氣液接觸來捕捉該第二氣體51中的細小顆粒,使該第二氣體51中的氯化銨微粒被捕捉至液相中,以得到一含有氯化銨的第二回收液72,同時伴隨得到一第三氣體71。 Introducing a process water 6 and the second gas 51 obtained in the above reaction step (b) into a second rotating packed bed 7 at a flow rate of 600 L/min and 30 m 3 /min, respectively (packing bed size, rotation speed, and filling and the first a rotating packed bed 3 is the same), the fine particles in the second gas 51 are captured by gas-liquid contact, and the ammonium chloride particles in the second gas 51 are captured into the liquid phase to obtain an ammonium chloride-containing solution. The second recovered liquid 72 is accompanied by a third gas 71.

在本實施例中,該第三氣體71是與上述氣提步驟(a)中的空氣合併後進行循環,以繼續在該第一旋轉填充床3中進行上述氣提步驟(a),藉此避免可能存在於該第三氣體71中的微量氯化銨微粒、微量氨氣、微量氯化氫蒸氣或水氣逸散至外界環境,並有效提高氨氮的回收率。該製程水6是該第二回收液72與一補充水(H2O)8合併並經熱交換後所得到,並再回流至該第二旋轉填充床7,以繼續對該第二氣體51中的細小顆粒進行捕捉,藉此提升本發明含氨氮廢水的回收方法之氨氮回收率。同時,在本實施例中,可將部分該製程水6導入該冰水吸收裝置9中,以作為冰水吸收該第一氣體31中的部分氨氣。 In the present embodiment, the third gas 71 is circulated after being combined with the air in the stripping step (a) to continue the stripping step (a) in the first rotating packed bed 3, whereby A trace amount of ammonium chloride fine particles, a trace amount of ammonia gas, a trace amount of hydrogen chloride vapor or water vapor which may be present in the third gas 71 is avoided to escape to the external environment, and the recovery rate of ammonia nitrogen is effectively improved. The process water 6 is obtained by combining the second recovery liquid 72 with a make-up water (H 2 O) 8 and undergoing heat exchange, and is returned to the second rotating packed bed 7 to continue the second gas 51. The fine particles in the medium are captured, thereby increasing the ammonia nitrogen recovery rate of the recovery method of the ammonia-containing nitrogen wastewater of the present invention. Meanwhile, in the present embodiment, a part of the process water 6 may be introduced into the ice water absorption device 9 to absorb part of the ammonia gas in the first gas 31 as ice water.

[回收率計算][Recovery calculation]

以含有約15000ppm氨氮的酸性廢水為例,進行上述第一實施例的含氨氮廢水的回收方法600min後,可得到不含鈷離子且含有30wt%氯化銨的回收液約1600kg,計算得氨氮的回收率大約為94%。 Taking the acidic wastewater containing about 15000 ppm of ammonia nitrogen as an example, after the ammonia nitrogen-containing wastewater recovery method of the above first embodiment is performed for 600 minutes, about 1600 kg of a recovery liquid containing no cobalt ions and containing 30% by weight of ammonium chloride can be obtained, and the ammonia nitrogen is calculated. The recovery rate is approximately 94%.

本發明含氨氮廢水的回收方法之第二實施例與上述第一實施例類以,差異之處在於為使用三個相同規格的旋轉填充床分別進行該氣提步驟(a)、該反應步驟(b)(取代該洗滌塔5)與該捕捉步驟(c)(填充床內徑為22mm,填充床外徑為140mm填充床軸向高度為20mm,轉速為1200rpm,填充物為不鏽鋼網,不鏽鋼網 的比表面積為850m2/m3):將上述第一實施例的鹼性廢水1及非活性氣體2(空氣)分別以0.1L/min及6L/min的流量引入一第一旋轉填充床3進行氣提步驟(a),將氣提得到的第一氣體31以6L/min的流量引入一第三旋轉填充床,並將稀鹽酸41(pH值為4~6)以0.5L/min的流量引入該第三旋轉填充床進行反應步驟(b),以得到第二氣體51(呈白煙狀)及第一回收液52。再將一製程水6及反應得到的第二氣體51分別以2L/min及6L/min的流量引入一第二旋轉填充床7進行捕捉步驟(c),藉以使該第二氣體51中的氯化銨微粒被捕捉至該第二回收液72中。以處理60L含有約26600ppm氨氮的酸性廢水為例,進行上述第二實施例的含氨氮廢水的回收方法540min後,可得到不含鈷離子且含有30wt%氯化銨的回收液約18kg,計算得氨氮的回收率大約為90%。 The second embodiment of the method for recovering ammonia-containing nitrogen wastewater of the present invention is different from the above-described first embodiment in that the stripping step (a) and the reaction step are separately performed using three rotating packed beds of the same specification ( b) (instead of the washing tower 5) and the capturing step (c) (the inner diameter of the packed bed is 22 mm, the outer diameter of the packed bed is 140 mm, the axial height of the packed bed is 20 mm, the rotational speed is 1200 rpm, the filling is stainless steel mesh, stainless steel mesh The specific surface area is 850 m 2 /m 3 ): the alkaline wastewater 1 and the inert gas 2 (air) of the first embodiment described above are introduced into a first rotating packed bed at a flow rate of 0.1 L/min and 6 L/min, respectively. Performing the stripping step (a), introducing the first gas 31 obtained by stripping into a third rotating packed bed at a flow rate of 6 L/min, and diluting hydrochloric acid 41 (pH 4-6) at 0.5 L/min. The flow rate is introduced into the third rotating packed bed to carry out the reaction step (b) to obtain a second gas 51 (in the form of white smoke) and a first recovered liquid 52. Then, a process water 6 and a second gas 51 obtained by the reaction are respectively introduced into a second rotating packed bed 7 at a flow rate of 2 L/min and 6 L/min to perform a capturing step (c), whereby the chlorine in the second gas 51 is made. The ammonium phosphate particles are captured into the second recovery liquid 72. Taking 60 L of acidic wastewater containing about 26,600 ppm of ammonia nitrogen as an example, after the 540 min recovery method of the ammonia-containing nitrogen wastewater of the second embodiment described above, about 18 kg of a recovery liquid containing no cobalt ions and containing 30 wt% of ammonium chloride can be obtained. The recovery of ammonia nitrogen is approximately 90%.

綜上所述,本發明含氨氮廢水的回收方法藉由該氣提步驟(a)、該反應步驟(b)及該捕捉步驟(c),僅需使用該非活性氣體2、該濃鹽酸4、該補充水8等低成本的原料,即可以徹底分離廢水中的重金屬離子,有效回收得到含有高濃度氯化銨的第一回收液52,且可避免排放含有氯化銨微粒、氨氣、氯化氫的廢氣,並適於工業化的連續處理程序,故確實能達成本發明之目的。 In summary, the method for recovering ammonia-containing nitrogen wastewater of the present invention, by using the stripping step (a), the reacting step (b), and the capturing step (c), only using the inert gas 2, the concentrated hydrochloric acid 4, The low-cost raw material such as the supplementary water 8 can completely separate the heavy metal ions in the waste water, effectively recover the first recovered liquid 52 containing a high concentration of ammonium chloride, and can avoid the discharge of ammonium chloride particles, ammonia gas, hydrogen chloride. The exhaust gas is suitable for industrial continuous processing, so that the object of the present invention can be achieved.

惟以上所述者,僅為本發明之實施例而已,當不能以此限定本發明實施之範圍,凡是依本發明申請專利範圍及專利說明書內容所作之簡單的等效變化與修飾,皆仍屬本發明專利涵蓋之範圍內。 However, the above is only the embodiment of the present invention, and the scope of the invention is not limited thereto, and all the equivalent equivalent changes and modifications according to the scope of the patent application and the patent specification of the present invention are still The scope of the invention is covered.

Claims (12)

一種含氨氮廢水的回收方法,該含氨氮廢水為一含有氨的鹼性廢水,包含以下步驟:(a)將該鹼性廢水及一非活性氣體分別引入一第一旋轉填充床,透過氣提得到一含有氨氣的第一氣體及一鹼性廢液;(b)將該第一氣體與稀鹽酸混合並進行反應,以得到一含有氯化銨微粒的第二氣體及一含有氯化銨的第一回收液,其中,該稀鹽酸是該第一回收液與濃鹽酸合併而得,以與該第一氣體進行反應;及(c)將一製程水及該第二氣體分別引入一第二旋轉填充床,透過捕捉該第二氣體中的氯化銨微粒得到一含有氯化銨的第二回收液。 A method for recovering ammonia-containing wastewater, the ammonia-containing wastewater is an alkaline wastewater containing ammonia, comprising the steps of: (a) introducing the alkaline wastewater and an inert gas into a first rotating packed bed, respectively, through gas stripping Obtaining a first gas containing ammonia gas and an alkaline waste liquid; (b) mixing the first gas with dilute hydrochloric acid and reacting to obtain a second gas containing ammonium chloride particles and one containing ammonium chloride The first recovered liquid, wherein the diluted hydrochloric acid is obtained by combining the first recovered liquid and concentrated hydrochloric acid to react with the first gas; and (c) introducing a process water and the second gas into the first A second rotating packed bed is obtained by capturing ammonium chloride particles in the second gas to obtain a second recovered liquid containing ammonium chloride. 如請求項1所述的含氨氮廢水的回收方法,其中,該鹼性廢水是以一含有銨離子及重金屬離子的酸性廢水與過量鹼進行中和,並經過濾而得。 The method for recovering ammonia-containing wastewater according to claim 1, wherein the alkaline wastewater is neutralized by an acidic wastewater containing ammonium ions and heavy metal ions and an excess of alkali, and is obtained by filtration. 如請求項1所述的含氨氮廢水的回收方法,其中,在該步驟(b)中,該第一氣體是先與冰水混合後,再與該稀鹽酸混合並進行反應。 The method for recovering ammonia-containing wastewater according to claim 1, wherein in the step (b), the first gas is first mixed with ice water, and then mixed with the diluted hydrochloric acid to carry out a reaction. 如請求項1所述的含氨氮廢水的回收方法,其中,在該步驟(c)中,該製程水是該第二回收液與一補充水合併後回流至該第二旋轉填充床,以繼續對該第二氣體中的氯化銨微粒進行捕捉。 The method for recovering ammonia-containing wastewater according to claim 1, wherein in the step (c), the process water is combined with a supplementary water and returned to the second rotating packed bed to continue The ammonium chloride microparticles in the second gas are captured. 如請求項3所述的含氨氮廢水的回收方法,其中,該冰水是來自於該步驟(c)的該製程水。 The method for recovering ammonia-containing wastewater according to claim 3, wherein the ice water is the process water from the step (c). 如請求項1所述的含氨氮廢水的回收方法,其中,在該步驟(c)得到該第二回收液的同時,伴隨得到一第三氣體,且該第三氣體是與該步驟(a)中的非活性氣體合併後進行循環,以繼續進行該步驟(a)。 The method for recovering ammonia-containing nitrogen wastewater according to claim 1, wherein, in the step (c), the second recovered liquid is obtained, accompanied by obtaining a third gas, and the third gas is associated with the step (a) The inactive gases in the mixture are combined and recycled to continue the step (a). 如請求項1所述的含氨氮廢水的回收方法,其中,在該步驟(a)中,該鹼性廢液是回流至該第一旋轉填充床。 The method for recovering ammonia-containing wastewater according to claim 1, wherein in the step (a), the alkaline waste liquid is refluxed to the first rotating packed bed. 如請求項1所述的含氨氮廢水的回收方法,其中,該步驟(b)是在一洗滌塔或一第三旋轉填充床中進行反應。 The method for recovering ammonia-containing wastewater according to claim 1, wherein the step (b) is carried out in a washing column or a third rotating packed bed. 如請求項2所述的含氨氮廢水的回收方法,其中,該經過濾而得的該鹼性廢水的pH值為11以上。 The method for recovering ammonia-containing wastewater according to claim 2, wherein the pH of the alkaline wastewater obtained by filtration is 11 or more. 如請求項1所述的含氨氮廢水的回收方法,其中,該步驟(b)中的該稀鹽酸的pH值為6以下。 The method for recovering ammonia-containing wastewater according to claim 1, wherein the pH of the dilute hydrochloric acid in the step (b) is 6 or less. 如請求項1所述的含氨氮廢水的回收方法,其中,在該步驟(b)中,該第一氣體與該稀鹽酸的混合流量比為10:1至1000:1。 The method for recovering ammonia-containing wastewater according to claim 1, wherein in the step (b), the mixing flow ratio of the first gas to the dilute hydrochloric acid is from 10:1 to 1000:1. 如請求項1所述的含氨氮廢水的回收方法,其中,在該步驟(c)中,該第二氣體與該製程水的混合流量比為3:1至500:1。 The method for recovering ammonia-containing wastewater according to claim 1, wherein in the step (c), the mixing flow ratio of the second gas to the process water is from 3:1 to 500:1.
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CN104310426A (en) * 2014-10-09 2015-01-28 中国有色集团(广西)平桂飞碟股份有限公司 Process of recovering ammonia from ammonia-nitrogen wastewater and exhaust gas of tungsten metallurgy

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Publication number Priority date Publication date Assignee Title
CN104310426A (en) * 2014-10-09 2015-01-28 中国有色集团(广西)平桂飞碟股份有限公司 Process of recovering ammonia from ammonia-nitrogen wastewater and exhaust gas of tungsten metallurgy

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Title
2013年5月24日,蔡志楹等,"以超重力旋轉填充床進行水中氨氮的氣提試驗",網址: http://ir.lib.ncut.edu.tw/bitstream/987654321/4146/2/C16.pdf *
2013年5月24日,蔡志楹等,"以超重力旋轉填充床進行水中氨氮的氣提試驗",網址: http://ir.lib.ncut.edu.tw/bitstream/987654321/4146/2/C16.pdf。

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