TW201305063A - Processing method for collecting waste water containing ammonia and apparatus thereof - Google Patents
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本發明是有關於一種廢水(waste water)的回收處理方法及其設備,且特別是有關於一種含氨(ammonia)廢水的回收處理方法及其設備。The invention relates to a method for recovering waste water and a device thereof, and particularly relates to a method for recycling and treating ammonia-containing wastewater and an apparatus therefor.
隨著氣候變遷日益劇烈,全球各地發生澇災與旱災的機率也逐漸昇高,進而導致越來越不容易有效地保存與利用人類生存所不可或缺的乾淨水資源。更重要的是,全球人口數量急速成長與工業科技的迅速發展,導致人類對於環境污染日益嚴重,更使得水資源的保存與利用問題越來越惡化。因此,如何能夠有效地回收工業廢水(industrial waste water)中的污染物質,以降低污染物質對於環境的污染,已逐漸成為世界各國政府亟待解決的問題之一。With the gradual increase of climate, the chances of disasters and droughts in the world have gradually increased, which has made it increasingly difficult to effectively preserve and utilize the clean water resources that are indispensable for human survival. More importantly, the rapid growth of the global population and the rapid development of industrial technology have led to the increasing environmental pollution of human beings and the worsening of the problem of water conservation and utilization. Therefore, how to effectively recover pollutants in industrial waste water to reduce the pollution of pollutants to the environment has gradually become one of the problems that governments around the world need to solve urgently.
含有高濃度氨(ammonia,化學式為NH3,俗稱為氨氣或者是無水氨,anhydrous ammonia)的特殊廢水常見於光電半導體(optoelectronic semiconductor)、石油煉製(petroleum refining)、煉焦(coking)、肥料(fertilizer)、鋼鐵(iron and steel)和食品(foodstuff)等工業的製程廢水。高濃度氨具有腐蝕性(corrosiveness)、對於水生生物具有毒性並且對人體具有致癌性(carcinogenicity)及致基因突變性(mutagenic)等特性。因此,部分國家已經立法,或者是傾向於立法,來限制廢水中的含氮量。Special wastewater containing high concentrations of ammonia (ammonia, chemical formula NH 3 , commonly known as ammonia or anhydrous ammonia) is commonly found in optoelectronic semiconductor, petroleum refining, coking, and fertilizer. Industrial process wastewater such as (fertilizer), iron (iron and steel) and food (foodstuff). High-concentration ammonia has corrosiveness, is toxic to aquatic organisms, and has carcinogenicity and mutagenic properties to humans. Therefore, some countries have already enacted legislation or are inclined to legislate to limit the nitrogen content in wastewater.
目前市場上通常是利用生物厭氧處理製程(biological anaerobic treatment process)來對含氨廢水進行脫氮(denitrifacation)。然而,傳統生物厭氧處理製程的脫氮效率並不高。因此,亟需提供能夠更有效處理含氨廢水的設備與方法。Currently, the biological anaerobic treatment process is used to denitrify the ammonia-containing wastewater. However, the denitrification efficiency of the conventional biological anaerobic treatment process is not high. Therefore, there is an urgent need to provide an apparatus and method that can more effectively treat ammonia-containing wastewater.
為了解決上述問題,本發明提供了一種含氨廢水的回收處理方法以及一種含氨廢水的回收處理設備,以提高含氨廢水的回收效率。In order to solve the above problems, the present invention provides a method for recovering ammonia-containing wastewater and a recycling treatment device for ammonia-containing wastewater to improve recovery efficiency of ammonia-containing wastewater.
本發明提供一種含氨廢水的回收處理方法,其包括下列步驟。首先,在一含氨廢水中加入一酸性溶劑(acid solvent),以形成一酸性廢水(acid waste water)。接著,再利用一逆滲透膜(reverse osmosis membrane,RO membrane)將酸性廢水分離為一高濃度廢水以及一低濃度廢水。然後,再將高濃度廢水分離為一含陰離子(anions)廢水以及一含陽離子(cations)廢水,以回收含陽離子廢水。The invention provides a method for recycling ammonia-containing wastewater, which comprises the following steps. First, an acid solvent is added to an ammonia-containing wastewater to form an acid waste water. Then, a reverse osmosis membrane (RO membrane) is used to separate the acidic wastewater into a high concentration wastewater and a low concentration wastewater. Then, the high-concentration wastewater is separated into an anions-containing wastewater and a cation-containing wastewater to recover the cationic wastewater.
在本發明的一實施例中,上述的含氨廢水的成分更包含過氧化氫(hydrogen peroxide,化學式為H2O2,俗稱雙氧水),並且在將酸性溶劑加入含氨廢水中之前,更包括利用一觸媒(catalyst)去除含氨廢水中的過氧化氫。其中,觸媒可為活性碳(activated carbon fibers,ACF)、二氧化錳(manganese dioxide,化學式為MnO2)或者是鐵錳砂(manganese ore)。In an embodiment of the invention, the ammonia-containing wastewater component further comprises hydrogen peroxide (chemical formula H 2 O 2 , commonly known as hydrogen peroxide), and further includes before adding the acidic solvent to the ammonia-containing wastewater. The hydrogen peroxide in the ammonia-containing wastewater is removed using a catalyst. The catalyst may be activated carbon fibers (ACF), manganese dioxide (manufactured by MnO 2 ) or manganese ore (manganese ore).
在本發明的一實施例中,上述的高濃度廢水是利用一電透析模組或者是一離子交換樹脂(ion exchange resin)分離為含陰離子廢水以及含陽離子廢水。In an embodiment of the invention, the high-concentration wastewater is separated into an anion-containing wastewater and a cationic wastewater by using an electrodialysis module or an ion exchange resin.
本發明更提供一種含氨廢水的回收處理設備,其包括一酸鹼值調整槽(pH adjusting tank)、一逆滲透膜、一解離槽(ionization tank)以及一回收槽(collecting tank),其中逆滲透膜配置於酸鹼值調整槽與解離槽之間,並且回收槽連通於解離槽。酸鹼值調整槽用以容納一含氨廢水,並且適於注入一酸性溶劑,以使含氨廢水形成一酸性廢水。逆滲透膜用以將酸性廢水分離為一高濃度廢水以及一低濃度廢水。解離槽用以將高濃度廢水分離為一含陰離子廢水以及一含陽離子廢水。回收槽用以回收含陽離子廢水。The invention further provides a recovery treatment device for ammonia-containing wastewater, which comprises a pH adjusting tank, a reverse osmosis membrane, an ionization tank and a collecting tank, wherein the reverse The permeable membrane is disposed between the pH adjustment tank and the dissociation tank, and the recovery tank is in communication with the dissociation tank. The pH adjustment tank is for containing an ammonia-containing wastewater, and is suitable for injecting an acidic solvent to form an acidic wastewater into the ammonia-containing wastewater. The reverse osmosis membrane is used to separate the acidic wastewater into a high concentration wastewater and a low concentration wastewater. The dissociation tank is used to separate the high concentration wastewater into an anionic wastewater and a cationic wastewater. The recovery tank is used to recover cationic wastewater.
在本發明的一實施例中,上述的含氨廢水的回收處理設備更包括一觸媒,而含氨廢水的成分更包含過氧化氫,並且酸鹼值調整槽配置於觸媒與逆滲透膜之間。而且,在將酸性溶劑注入含氨廢水中之前,先利用觸媒去除含氨性廢水中的過氧化氫。其中,觸媒為活性碳、二氧化錳或者是鐵錳砂。In an embodiment of the present invention, the ammonia-containing wastewater recovery treatment device further includes a catalyst, and the ammonia-containing wastewater component further comprises hydrogen peroxide, and the pH-adjusting tank is disposed on the catalyst and the reverse osmosis membrane. between. Further, the catalyst is used to remove hydrogen peroxide in the ammonia-containing wastewater before the acidic solvent is injected into the ammonia-containing wastewater. Among them, the catalyst is activated carbon, manganese dioxide or iron manganese sand.
在本發明的一實施例中,上述的解離槽中具有一電透析模組或者是一離子交換樹脂,並且高濃度廢水利用電透析模組或者是離子交換樹脂分離為含陰離子廢水以及含陽離子廢水。In an embodiment of the invention, the dissociation tank has an electrodialysis module or an ion exchange resin, and the high concentration wastewater is separated into an anion-containing wastewater and a cationic wastewater by using an electrodialysis module or an ion exchange resin. .
在本發明的一實施例中,上述的解離槽連通於酸鹼值調整槽,用以將含陰離子廢水當作酸性溶劑注入酸鹼值調整槽中。In an embodiment of the invention, the dissociation tank is connected to the pH adjustment tank for injecting the anion-containing wastewater as an acidic solvent into the pH adjustment tank.
在本發明的一實施例中,上述的含氨廢水的回收處理設備更包括一貯存槽(storage tank)。貯存槽連通於酸鹼值調整槽,用以貯存酸性溶劑,並且適於將酸性溶劑注入酸鹼值調整槽中。In an embodiment of the invention, the ammonia-containing wastewater recovery processing apparatus further includes a storage tank. The storage tank is connected to the pH adjustment tank for storing the acidic solvent, and is suitable for injecting the acidic solvent into the pH adjustment tank.
在本發明的一實施例中,上述的酸性廢水的酸鹼值低於6.5。In an embodiment of the invention, the acidic wastewater has a pH of less than 6.5.
在本發明的一實施例中,上述的含氨廢水、酸性溶劑與含陰離子廢水的成分皆包含硫酸根離子(sulfate ion,化學式為SO4 2-)與氯離子(chlorine ion,化學式為Cl-)至少其中之一。In an embodiment of the present invention, the above-mentioned ammoniacal waste water, an acidic solvent with the component containing the anionic waste water are contained sulfate ions (sulfate ion, the formula SO 4 2-) and chloride ions (chlorine ion, the formula Cl - ) at least one of them.
在本發明的一實施例中,上述的含氨廢水的成分更包含鈉離子(sodium ion,化學式為Na+)與銨根離子(ammonium ion,化學式為NH4 +)至少其中之一。In an embodiment of the invention, the ammonia-containing wastewater component further comprises at least one of sodium ion (chemical formula Na + ) and ammonium ion (chemical ion NH 4 + ).
相較於先前技術,本發明對於廢水中氨的回收效率會較高。Compared with the prior art, the present invention has a high efficiency in recovering ammonia in wastewater.
為讓本發明的上述特徵和優點能更明顯易懂,下文特舉多個實施例,並配合所附圖式,作詳細說明如下。The above described features and advantages of the invention will be apparent from the following description.
圖1繪示出根據本發明一個實施例的一種含氨廢水的回收處理方法的流程圖。請參考圖1所示,含氨廢水的回收處理方法包括下列步驟。首先,如步驟S110所示,在一含氨廢水中加入一酸性溶劑,以將原來呈鹼性的含氨廢水的酸鹼值調整至低於6.5,進而形成一酸性廢水。接著,如步驟S120所示,再利用逆滲透膜將酸性廢水分離為一高濃度廢水以及一低濃度廢水。然後,如步驟S130所示,再對高濃度廢水進行解離處理,以將高濃度廢水分離為一含陰離子廢水以及含氨的一含陽離子廢水。如此一來,如步驟S140所示,便能回收含氨的含陽離子廢水。1 is a flow chart showing a method of recycling ammonia-containing wastewater according to an embodiment of the present invention. Referring to FIG. 1, the recovery treatment method of the ammonia-containing wastewater includes the following steps. First, as shown in step S110, an acidic solvent is added to an ammonia-containing wastewater to adjust the pH of the originally alkaline ammonia-containing wastewater to less than 6.5 to form an acidic wastewater. Next, as shown in step S120, the reverse osmosis membrane is used to separate the acidic wastewater into a high concentration wastewater and a low concentration wastewater. Then, as shown in step S130, the high-concentration wastewater is dissociated to separate the high-concentration wastewater into an anion-containing wastewater and a cation-containing wastewater containing ammonia. As a result, as shown in step S140, the ammonia-containing cationic wastewater can be recovered.
更詳細而言,氨可能會以帶正電的銨根離子(NH4+)形式存在於溶液中。由於酸性液體會使逆滲透膜帶正電,因而會有利於逆滲透膜排斥同樣是帶正電的銨根離子,進而在高濃度廢水中保留更多的銨根離子。因此,於此實施例中會先進行步驟S110,以藉由酸性溶劑將原來呈鹼性的含氨廢水調整為酸性廢水。接著,在進行步驟S120,以利用逆滲透膜將酸性廢水分離為高濃度廢水以及低濃度廢水時,便能夠提高高濃度廢水中的銨根離子含量。此時,銨根離子含量極低的低濃度廢水便能夠回收再利用,或者是排放至廢水處理廠進行後續的一般廢水處理製程。In more detail, ammonia may be present in the solution as a positively charged ammonium ion (NH 4+ ). Since the acidic liquid will positively charge the reverse osmosis membrane, it will facilitate the reverse osmosis membrane to repel the positively charged ammonium ions, thereby retaining more ammonium ions in the high concentration wastewater. Therefore, in this embodiment, step S110 is first performed to adjust the originally alkaline ammonia-containing wastewater to acidic wastewater by an acidic solvent. Next, in step S120, when the acidic wastewater is separated into high-concentration wastewater and low-concentration wastewater by the reverse osmosis membrane, the ammonium ion content in the high-concentration wastewater can be increased. At this time, the low-concentration wastewater with extremely low ammonium ion content can be recycled or reused, or discharged to a wastewater treatment plant for subsequent general wastewater treatment processes.
然後,如步驟S130所示,再利用一電透析模組或者是一離子交換樹脂來對高濃度廢水進行解離處理,以將高濃度廢水分離為含陰離子廢水以及含陽離子廢水。然後,便能如步驟S140所示回收含氨的含陽離子廢水。相較於先前技術以生物厭氧製程來對含氨廢水進行脫氮,此實施例以先濃縮再解離的方式來處理含氨廢水,能夠具有較高的氨回收效率。Then, as shown in step S130, an electrodialysis module or an ion exchange resin is used to dissociate the high-concentration wastewater to separate the high-concentration wastewater into an anion-containing wastewater and a cationic wastewater. Then, the ammonia-containing cationic wastewater can be recovered as shown in step S140. Compared with the prior art, the ammonia-containing wastewater is denitrified by a biological anaerobic process. This embodiment treats the ammonia-containing wastewater by first concentrating and dissociating, and has a high ammonia recovery efficiency.
值得注意的是,為了簡化上述製程中的低濃度廢水、含陰離子廢水以及含陽離子廢水等副產物的後續處理作業,酸性溶劑中所含有的陰離子成分最好是與含氨廢水中所含有的主要陰離子成分相同,以避免上述副產物中的主要成分太過複雜。It is worth noting that in order to simplify the subsequent treatment of low-concentration wastewater, anion-containing wastewater, and by-products including cationic wastewater in the above process, the anion component contained in the acidic solvent is preferably mainly contained in the ammonia-containing wastewater. The anionic components are the same to avoid the main components of the above by-products being too complicated.
更詳細而言,來自於半導體產業或者是其他產業的含氨廢水的主要成分通常不會只包含有銨根離子,可能還會包含有硫酸根離子或者是氯離子等陰離子。舉例來說,含氨廢水的主要成分可為硫酸銨(ammonium sulphate,化學式為(NH4)2SO4)廢水或者是氯化銨(ammonium chloride,化學式為NH4Cl)廢水。此時,酸性溶劑的主要成分便可為硫酸(sulfuric acid,化學式為H2SO4)溶液或者是氫氯酸(hydrochloric acid,化學式為HCl,俗稱鹽酸)溶液。More specifically, the main components of ammonia-containing wastewater from the semiconductor industry or other industries usually do not contain only ammonium ions, and may also contain sulfate ions or anions such as chloride ions. For example, the main component of the ammonia-containing wastewater may be ammonium sulphate (chemical formula (NH 4 ) 2 SO 4 ) wastewater or ammonium chloride (chemical formula NH 4 Cl) wastewater. In this case, the main component of the acidic solvent may be a sulfuric acid (chemical formula H 2 SO 4 ) solution or a hydrochloric acid (hydrochloric acid, chemical formula HCl, commonly known as hydrochloric acid) solution.
另外,當含氨廢水的主要成分包含有硫酸根離子或者是氯離子時,在步驟S130中所產生的含陰離子廢水的主要成分中,亦會包含有硫酸根離子與氯離子至少其中之一。此時,含陰離子廢水便可被當作用來調整含氨廢水酸鹼值的酸性溶劑,以進行重複利用。Further, when the main component of the ammonia-containing wastewater contains sulfate ions or chloride ions, at least one of the sulfate ion and the chloride ion may be contained in the main component of the anion-containing wastewater generated in the step S130. At this time, the anion-containing wastewater can be used as an acidic solvent for adjusting the pH value of the ammonia-containing wastewater for reuse.
除此之外,於此實施例中,含氨廢水的成分更可包含鈉離子。因此,在回收含陽離子廢水時,除了可回收到氨之外,更可一併回收到鈉化合物(sodium compound)。In addition to this, in this embodiment, the component containing ammonia wastewater may further contain sodium ions. Therefore, in the recovery of the cation-containing wastewater, in addition to the recovery of ammonia, a sodium compound can be recovered together.
圖2繪示出根據本發明另一個實施例的一種含氨廢水的回收處理方法的流程圖。請參考圖2所示,此實施例中的含氨廢水的回收處理方法與前一實施例中的含氨廢水的回收處理方法相似,二者不同之處在於此實施例中的含氨廢水的主要成分更包含過氧化氫。因此,在進行步驟S110,以在將酸性溶劑注入含氨廢水中而形成酸性廢水之前,更包括進行步驟S100,以利用一觸媒去除含氨廢水中的過氧化氫。其中,觸媒可為活性碳、二氧化錳或者是鐵錳砂。其他步驟與前一實施例相同,於此不再贅述。2 is a flow chart showing a method of recycling ammonia-containing wastewater according to another embodiment of the present invention. Referring to FIG. 2, the ammonia-containing wastewater recovery treatment method in this embodiment is similar to the ammonia-containing wastewater recovery treatment method in the previous embodiment, and the difference is in the ammonia-containing wastewater in this embodiment. The main component further contains hydrogen peroxide. Therefore, in step S110, before the acidic solvent is injected into the ammonia-containing wastewater to form the acidic wastewater, the step S100 is further included to remove the hydrogen peroxide in the ammonia-containing wastewater by using a catalyst. Among them, the catalyst may be activated carbon, manganese dioxide or iron manganese sand. The other steps are the same as in the previous embodiment, and are not described herein again.
為了讓本技術領域中具有通常知識者能夠更容易理解上述含氨廢水的回收處理方法。以下將以具體實施例進一步揭露一種含氨廢水的回收處理設備。然而,上述含氨廢水的回收處理方法並非只能利用下述含氨廢水的回收處理設備才能進行。In order to make it easier for those skilled in the art to understand the above-mentioned ammonia-containing wastewater recovery treatment method. Hereinafter, a recycling treatment apparatus for ammonia-containing wastewater will be further disclosed by a specific embodiment. However, the above-mentioned ammonia-containing wastewater recovery treatment method cannot be carried out only by using the following ammonia-containing wastewater recovery treatment equipment.
圖3繪示出根據本發明一個實施例的一種含氨廢水的回收處理設備的結構示意圖。請參考圖3所示,含氨廢水的回收處理設備100a包括一個酸鹼值調整槽110、一個逆滲透膜120、一個解離槽130以及一個回收槽140。其中,逆滲透膜120配置於酸鹼值調整槽110與解離槽130之間,並且回收槽140連通於解離槽130。3 is a schematic view showing the structure of a recycling treatment apparatus for ammonia-containing wastewater according to an embodiment of the present invention. Referring to FIG. 3, the ammonia-containing wastewater recovery processing apparatus 100a includes a pH adjustment tank 110, a reverse osmosis membrane 120, a dissociation tank 130, and a recovery tank 140. The reverse osmosis membrane 120 is disposed between the pH adjustment tank 110 and the dissociation tank 130 , and the recovery tank 140 is in communication with the dissociation tank 130 .
酸鹼值調整槽110用以容納含氨廢水,並且適於注入酸性溶劑,以將原來呈鹼性的含氨廢水調整為酸性廢水。然後,再利用逆滲透膜120將酸性廢水分離為高濃度廢水以及低濃度廢水。其中,氨含量極低的低濃度廢水能夠回收再利用,或者是排放至廢水處理廠進行後續的一般廢水處理製程,而氨含量極高的高濃度廢水則會注入解離槽130中,以利用解離槽130中的電透析模組或者是離子交換樹脂進一步分離為含陰離子廢水以及含陽離子廢水。之後,再將含陽離子廢水注入回收槽140進行回收。相同地,相較於先前技術以生物厭氧製程來對含氨廢水進行脫氮,此實施例以先濃縮再解離的方式來處理含氨廢水,能夠具有較高的回收效率。The pH adjusting tank 110 is for accommodating ammonia-containing wastewater, and is suitable for injecting an acidic solvent to adjust the originally alkaline ammonia-containing wastewater to acidic wastewater. Then, the reverse osmosis membrane 120 is used to separate the acidic wastewater into high-concentration wastewater and low-concentration wastewater. Among them, low-concentration wastewater with extremely low ammonia content can be recycled or reused, or discharged to a wastewater treatment plant for subsequent general wastewater treatment process, and high-concentration wastewater with extremely high ammonia content is injected into the dissociation tank 130 to utilize dissociation. The electrodialysis module or ion exchange resin in the tank 130 is further separated into an anionic wastewater and a cationic wastewater. Thereafter, the cation-containing wastewater is injected into the recovery tank 140 for recovery. Similarly, the ammonia-containing wastewater is denitrified by a biological anaerobic process compared to the prior art. This embodiment treats the ammonia-containing wastewater by first concentrating and dissociating, and can have a high recovery efficiency.
另外,當含氨廢水的主要成分還包含有硫酸根離子或者是氯離子等陰離子時,可選擇上述陰離子的氫化物(如硫酸與氫氯酸)來做為酸性溶劑的主要成分,以便簡化低濃度廢水、含陰離子廢水以及含陽離子廢水等副產物的後續處理作業。而且,於此實施例中,解離槽130亦可連通於酸鹼值調整槽110。此時,還能夠直接將含陰離子廢水當做用來調整含氨廢水酸鹼值的酸性溶劑來注入酸鹼值調整槽110中,以進行重複利用。In addition, when the main component of the ammonia-containing wastewater further contains an anion such as a sulfate ion or a chloride ion, a hydride of the above anion (such as sulfuric acid and hydrochloric acid) may be selected as a main component of the acidic solvent, so as to simplify the low. Subsequent processing operations for concentration wastewater, anion-containing wastewater, and by-products such as cationic wastewater. Moreover, in this embodiment, the dissociation groove 130 may also communicate with the pH adjustment groove 110. At this time, it is also possible to directly inject the anion-containing wastewater as an acidic solvent for adjusting the pH value of the ammonia-containing wastewater, and inject it into the pH adjustment tank 110 for reuse.
值得注意的是,部分的陰離子會在上述製程中隨著低濃度廢水被排放掉,因此含陰離子廢水中的陰離子含量可能不足以在後續製程中將含氨廢水調整至所需酸鹼值。因此,此實施例中的含氨廢水的回收處理設備100a更可包括連通於酸鹼值調整槽110,並且用以貯存酸性溶劑的一個貯存槽150,以便根據需求量將酸性溶劑從貯存槽150注入酸鹼值調整槽110中。It is worth noting that some of the anions will be discharged with the low concentration of wastewater in the above process, so the anion content in the anion-containing wastewater may not be sufficient to adjust the ammonia-containing wastewater to the desired pH in the subsequent process. Therefore, the ammonia-containing wastewater recovery treatment apparatus 100a in this embodiment may further include a storage tank 150 connected to the pH adjustment tank 110 and used to store the acidic solvent, so as to remove the acidic solvent from the storage tank 150 according to the demand. It is injected into the pH adjustment tank 110.
此外,含氨廢水的回收處理設備100a還可包括複數個泵浦160、170以及180。其中,泵浦160可連接於酸鹼值調整槽110與逆滲透膜120之間,用以將酸性廢水從酸鹼值調整槽110輸送至逆滲透膜120。再者,泵浦170可連接於逆滲透膜120與解離槽130之間,用以將高濃度廢水從逆滲透膜120注入解離槽130。另外,泵浦180則可連接於貯存槽150與酸鹼值調整槽110之間,用以將酸性溶劑從貯存槽150注入至酸鹼值調整槽110。Further, the ammonia treatment wastewater recovery treatment apparatus 100a may further include a plurality of pumps 160, 170, and 180. The pump 160 may be connected between the pH adjustment tank 110 and the reverse osmosis membrane 120 for transporting the acidic wastewater from the pH adjustment tank 110 to the reverse osmosis membrane 120. Furthermore, the pump 170 can be connected between the reverse osmosis membrane 120 and the dissociation tank 130 for injecting high concentration wastewater from the reverse osmosis membrane 120 into the dissociation tank 130. In addition, the pump 180 may be connected between the storage tank 150 and the pH adjustment tank 110 for injecting the acidic solvent from the storage tank 150 into the pH adjustment tank 110.
除此之外,於此實施例中,含氨廢水的成分更可包含鈉離子。因此,在回收含陽離子廢水時,除了可回收到氨之外,更可一併回收到鈉化合物。In addition to this, in this embodiment, the component containing ammonia wastewater may further contain sodium ions. Therefore, in the recovery of the cation-containing wastewater, in addition to the recovery of ammonia, the sodium compound can be recovered together.
圖4繪示出根據本發明另一個實施例的一種含氨廢水的回收處理設備的結構示意圖。請參考圖4所示,此實施例中的含氨廢水的回收處理設備100b與前一實施例中的含氨廢水的回收處理設備100a相似,二者不同之處在於此實施例中的含氨廢水的主要成分更包含過氧化氫,因此含氨廢水的回收處理設備100b更可包括一個觸媒190,並且酸鹼值調整槽110配置於觸媒190與逆滲透膜120之間。其中,觸媒190可為活性碳、二氧化錳或者是鐵錳砂,用以在將酸性溶劑注入含氨廢水中之前,先去除酸性廢水中的過氧化氫。其他元件的功能及連接關係與前一實施例相同,於此不再贅述。4 is a schematic view showing the structure of a recycling treatment apparatus for ammonia-containing wastewater according to another embodiment of the present invention. Referring to FIG. 4, the ammonia-containing wastewater recovery treatment device 100b in this embodiment is similar to the ammonia-containing wastewater recovery treatment device 100a in the previous embodiment, and the difference is in the ammonia content in this embodiment. The main component of the wastewater further contains hydrogen peroxide. Therefore, the ammonia treatment wastewater recovery apparatus 100b may further include a catalyst 190, and the pH adjustment tank 110 is disposed between the catalyst 190 and the reverse osmosis membrane 120. The catalyst 190 may be activated carbon, manganese dioxide or iron manganese sand for removing hydrogen peroxide in the acidic wastewater before injecting the acidic solvent into the ammonia-containing wastewater. The functions and connection relationships of other components are the same as those of the previous embodiment, and will not be described herein.
綜合上述,由於酸性液體會使逆滲透膜帶正電,因而會有利於逆滲透膜排斥銨根離子,以便在高濃度廢水中保留更多的銨根離子。因此,本發明先將含氨廢水的酸鹼值調整為酸性,然後在利用逆滲透膜將酸性廢水分離為高濃度廢水以及低濃度廢水時,便能提高逆滲透膜對於銨根離子的回收效率。然後,再對高濃度廢水進行處理,以將其分離為含陰離子廢水以及含陽離子廢水。之後,便能回收含有氨的含陽離子廢水。因此,相較於先前技術,本發明對於氨的回收效率會較高。In summary, since the acidic liquid causes the reverse osmosis membrane to be positively charged, it is advantageous for the reverse osmosis membrane to repel the ammonium ion to retain more ammonium ions in the high concentration wastewater. Therefore, the present invention first adjusts the acidity and alkalinity of the ammonia-containing wastewater to be acidic, and then, when the acidic wastewater is separated into high-concentration wastewater and low-concentration wastewater by using a reverse osmosis membrane, the recovery efficiency of the reverse ion membrane for the ammonium ion can be improved. . Then, the high-concentration wastewater is treated to separate it into an anionic wastewater and a cationic wastewater. After that, the cationic wastewater containing ammonia can be recovered. Therefore, the present invention is more efficient in recovering ammonia than the prior art.
雖然本發明已以實施例揭露如上,然其並非用以限定本發明,任何所屬技術領域中具有通常知識者,在不脫離本發明的精神和範圍內,當可作些許的更動與潤飾,因此本發明的保護範圍當視後附的申請專利範圍所界定者為準。Although the present invention has been disclosed in the above 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 the invention is defined by the scope of the appended claims.
100a、100b...含氨廢水的回收處理設備100a, 100b. . . Recycling equipment for ammonia-containing wastewater
110...酸鹼值調整槽110. . . pH adjustment tank
120...逆滲透膜120. . . Reverse osmosis membrane
130...解離槽130. . . Dissociation slot
140...回收槽140. . . Recovery tank
150...貯存槽150. . . Storage tank
160、170、180...泵浦160, 170, 180. . . Pump
190...觸媒190. . . catalyst
S100、S110、S120、S130、S140...步驟S100, S110, S120, S130, S140. . . step
圖1繪示出根據本發明一個實施例的一種含氨廢水的回收處理方法的流程圖。1 is a flow chart showing a method of recycling ammonia-containing wastewater according to an embodiment of the present invention.
圖2繪示出根據本發明另一個實施例的一種含氨廢水的回收處理方法的流程圖。2 is a flow chart showing a method of recycling ammonia-containing wastewater according to another embodiment of the present invention.
圖3繪示出根據本發明一個實施例的一種含氨廢水的回收處理設備的結構示意圖。3 is a schematic view showing the structure of a recycling treatment apparatus for ammonia-containing wastewater according to an embodiment of the present invention.
圖4繪示出根據本發明另一個實施例的一種含氨廢水的回收處理設備的結構示意圖。4 is a schematic view showing the structure of a recycling treatment apparatus for ammonia-containing wastewater according to another embodiment of the present invention.
S110、S120、S130、S140...步驟S110, S120, S130, S140. . . step
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