TW201425236A - Method for treating wastewater - Google Patents
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- TW201425236A TW201425236A TW101148264A TW101148264A TW201425236A TW 201425236 A TW201425236 A TW 201425236A TW 101148264 A TW101148264 A TW 101148264A TW 101148264 A TW101148264 A TW 101148264A TW 201425236 A TW201425236 A TW 201425236A
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Abstract
Description
本發明係有關一種廢水處理方法,尤指一種含氨氮廢水之厭氧氨氧化處理方法。 The invention relates to a wastewater treatment method, in particular to an anaerobic ammonium oxidation treatment method for ammonia-containing wastewater.
高氨氮低有機物濃度之氨氮廢水,通常存在於高科技產業,如半導體製造業或LED製造業等。由於其製程中,主要係利用氨氣或氨水,產生之高濃度氨氮廢水則排入廢水處理廠進行處理。就目前傳統硝化/脫氮程序現況,同時硝化之效率較低,設備佔地面積較大,因此不易達到法規管制之放流水標準。 Ammonia nitrogen wastewater with high ammonia nitrogen and low organic matter concentration is usually found in high-tech industries such as semiconductor manufacturing or LED manufacturing. Because of its process, mainly using ammonia gas or ammonia water, the high concentration ammonia nitrogen wastewater generated is discharged into the wastewater treatment plant for treatment. As for the current status of the traditional nitrification/denitrification process, the efficiency of nitrification is relatively low, and the equipment covers a large area, so it is difficult to meet the discharge water standard regulated by regulations.
傳統氨氮生物處理方式為硝化-脫硝法,必須經過一連串之生物反應,包含氨氮氧化菌(ammonia oxidation bacteria,AOB)將氨氮氧化成亞硝酸氮;後接續由亞硝酸氮氧化菌(nitrite oxidation bacteria,NOB)將亞硝酸氮氧化成硝酸氮;最後則由脫氮菌將亞硝酸氮還原成氮氣處理完成。惟,該處理方式之整體操作較為耗能,且運作成本較高。 The traditional ammonia nitrogen biological treatment method is nitrification-denitration, which must undergo a series of biological reactions, including ammonia oxidation bacteria (AOB) to oxidize ammonia nitrogen to nitrite nitrogen; followed by nitrite oxidation bacteria , NOB) oxidizes nitrite to form nitrate nitrogen; finally, the reduction of nitrite to nitrogen by denitrifying bacteria is completed. However, the overall operation of the processing method is relatively energy intensive and the operating cost is high.
另一種氨氮處理方式為厭氧氨氧化程序(anammox process),該微生物於厭氧狀態下利用自然界存在的二氧化碳(CO2)作為碳源,直接將氨氮作為電子供給者,亞硝酸鹽氮作為電子接受者,進行三價電子傳送反應生成氮氣的過程,不必如傳統的除氮程序需要額外耗費多餘的成本以及能量,不需提供大量氧氣將氨氮轉化成硝酸氮,亦不 需提供有機碳源進行脫硝反應。該厭氧氨氧化之生化反應為:NH4 ++1.32NO2 -+0.066HCO3 -+0.13H+→1.02N2+0.26NO3 -+0.066CH2O0.5N0.15+2.03H2O Another ammonia nitrogen treatment method is the anammox process, which uses carbon dioxide (CO 2 ) existing in nature as a carbon source under anaerobic conditions, directly using ammonia nitrogen as an electron supplier, and nitrite nitrogen as an electron. Recipients, the process of trivalent electron transport reaction to generate nitrogen, does not have to cost extra cost and energy as the traditional nitrogen removal process, without the need to provide a large amount of oxygen to convert ammonia nitrogen into nitrate nitrogen, and does not need to provide organic carbon source. Denitrification reaction. The biochemical reaction of anaerobic ammonium oxidation is: NH 4 + +1.32NO 2 - +0.066HCO 3 - +0.13H + →1.02N 2 +0.26NO 3 - +0.066CH 2 O 0.5 N 0.15 +2.03H 2 O
惟,上述生化反應在厭氧氨氧化裝置進行後,通常需額外設置一脫氮裝置,降低硝酸氮之濃度,確保處理水可以符合總氮或硝酸氮之法規標準。由於脫氮裝置需要額外添加有機物作為脫氮碳源,因此無法透過單一沉澱裝置作固液分離與回收污泥,由於污泥需經馴養,若無法有效回收污泥則降低廢水處理的效率並提高成本。 However, after the above biochemical reaction is carried out in the anaerobic ammonium oxidation unit, an additional nitrogen removal unit is usually required to reduce the concentration of the nitrogen nitrate to ensure that the treated water can meet the regulatory standards of total nitrogen or nitrate nitrogen. Since the denitrification device requires additional organic matter as a denitrification carbon source, it is not possible to separate solid and liquid sludge through a single sedimentation device. Since the sludge needs to be domesticated, if the sludge cannot be effectively recovered, the efficiency of wastewater treatment is improved and the wastewater is improved. cost.
本揭露提供一種廢水處理方法,係包括:將含氨氮廢水與亞硝酸氮導入一內部具有彼此連通之厭氧氨氧化區及脫氮區之生物反應器(biological rector)中,該厭氧氨氧化區及脫氮區係藉由分離結構隔開,且該厭氧氨氧化區中具有自營生物,該脫氮區中具有異營生物,其中,該含氨氮廢水與亞硝酸氮係被導入該厭氧氨氧化區進行反應,以產生氮氣與硝酸氮;以及使該經反應的含氨氮廢水自該厭氧氨氧化區進入該脫氮區,並使該硝酸氮進入該脫氮區以進行脫氮反應。 The present disclosure provides a wastewater treatment method comprising: introducing ammonia-containing wastewater and nitrite into a biological rector having an anaerobic ammonium oxidation zone and a denitrification zone connected to each other, the anaerobic ammonium oxidation The zone and the denitrification zone are separated by a separation structure, and the anaerobic ammonium oxidation zone has a self-operated organism, and the denitrification zone has a heterotrophic organism, wherein the ammonia-nitrogen-containing wastewater and the nitrite nitrogen system are introduced into the zone The anaerobic ammonium oxidation zone is reacted to generate nitrogen and nitrogen nitrate; and the reacted ammonia-containing nitrogen wastewater is introduced into the denitrification zone from the anammox zone, and the nitrate nitrogen is introduced into the denitrification zone for removal Nitrogen reaction.
以下藉由特定的具體實施例說明實施方式,熟悉此技藝之人士可由本說明書所揭示之內容輕易地瞭解本發明之其他優點及功效。 Other embodiments of the present invention will be readily understood by those skilled in the art from this disclosure.
請參閱第1圖,係說明廢水處理方法之示意圖。 Please refer to Figure 1 for a schematic diagram of the wastewater treatment method.
本揭露提供之廢水處理方法係於一內部具有彼此連通之厭氧氨氧化區10及脫氮區12之生物反應器1中進行,該單一生物反應器1中之厭氧氨氧化區10及脫氮區12係藉由分離結構14隔開。該廢水處理方法包括將含氨氮廢水W與亞硝酸氮導入該厭氧氨氧化區10進行反應,以產生氮氣與硝酸氮;以及使該經反應的含氨氮廢水W’自該厭氧氨氧化區10進入該脫氮區12,並使該硝酸氮進入該脫氮區12以進行脫氮反應。 The wastewater treatment method provided by the present disclosure is carried out in a bioreactor 1 having an anaerobic ammonium oxidation zone 10 and a denitrification zone 12 which are connected to each other, and the anaerobic ammonium oxidation zone 10 in the single bioreactor 1 The nitrogen zone 12 is separated by a separation structure 14. The wastewater treatment method comprises introducing ammonia-containing wastewater W and nitrite into the anammox zone 10 to produce nitrogen and nitrate nitrogen; and reacting the reacted ammonia-containing wastewater W' from the anammox zone 10 enters the denitrification zone 12 and causes the nitric acid nitrogen to enter the denitrification zone 12 for a denitrification reaction.
於一具體實施例中,該含氨氮廢水與亞硝酸氮之莫耳比係為等比例,或如1:1.32。 In a specific embodiment, the molar ratio of the ammonia-nitrogen-containing wastewater to the nitrite nitrogen is in an equal ratio, or is 1:1.32.
另一方面,因經厭氧氨氧化之生化反應後,殘存之硝酸氮為總氮之1/8左右,在生物反應器中,該脫氮區12之體積可小於該厭氧氨氧化區10之體積。 On the other hand, after the biochemical reaction by anaerobic ammonium oxidation, the remaining nitrate nitrogen is about 1/8 of the total nitrogen, and in the bioreactor, the volume of the denitrification zone 12 can be smaller than the anaerobic ammonium oxidation zone 10 The volume.
在進行廢水處理時,該厭氧氨氧化區中具有自營生物,例如厭氧氨氧化微生物,該脫氮區中具有異營生物,例如,脫氮菌等。於一具體實施例中,該自營生物係存在於非顆粒化污泥或厭氧顆粒化污泥。此外,並先進行污泥馴養至可進行廢水處理的程度。由於該馴養的方法為本領域具有通常知識者所知悉者,故不於本文中贅述。 In the wastewater treatment, the anaerobic ammonium oxidation zone has a self-supporting organism, such as an anaerobic ammonium oxidizing microorganism, and the denitrification zone has a meta-organism, for example, a denitrifying bacteria. In a specific embodiment, the self-operated organism is present in non-granulated sludge or anaerobic granular sludge. In addition, the sludge is domesticated to the extent that it can be treated with wastewater. Since the method of domestication is known to those of ordinary skill in the art, it is not described herein.
於含氨氮廢水W導入該厭氧氨氧化區10後,係以8至18m/hr的流速使該經反應的含氨氮廢水W’自該厭氧氨氧化區10進入該脫氮區12。通常來說,可以進流廢水泵搭配回流水泵之總水量達到預設之流速值。 After the ammonia-containing nitrogen wastewater W is introduced into the anaerobic ammonium oxidation zone 10, the reacted ammonia-containing nitrogen wastewater W' is introduced into the denitrification zone 12 from the anammox zone 10 at a flow rate of 8 to 18 m/hr. Generally speaking, the total amount of water that can be fed into the wastewater pump and the return pump can reach the preset flow rate value.
於一具體實施例中,該自營生物係存在於非顆粒化污泥,且該非顆粒化污泥包括複數活性碳顆粒。該非顆粒化污泥中包括複數活性碳顆粒,可作為自營生物之載體,避免該自營生物的重量過輕被帶至該脫氮區12。 In a specific embodiment, the self-operated organism is present in the non-granulated sludge, and the non-granulated sludge comprises a plurality of activated carbon particles. The non-granulated sludge comprises a plurality of activated carbon particles, which can be used as a carrier for self-supporting organisms, and the weight of the self-operated organisms is prevented from being brought to the denitrification zone 12.
於一具體實施例中,該複數活性碳顆粒之粒徑介於15至25mesh。 In one embodiment, the plurality of activated carbon particles have a particle size between 15 and 25 mesh.
於一具體實施例中,當該自營生物係存在於非顆粒化污泥,係控制以13至18m/hr的流速使該經反應的含氨氮廢水W’自該厭氧氨氧化區10進入該脫氮區12。 In a specific embodiment, when the self-operated biological system is present in the non-granulated sludge, the reacted ammonia-containing nitrogen wastewater W' is controlled to enter the anaerobic ammonium oxidation zone 10 at a flow rate of 13 to 18 m/hr. The denitrification zone 12.
於另一具體實施例中,該自營生物係存在於厭氧顆粒化污泥,且係以8至12m/hr的流速使該經反應的含氨氮廢水自該厭氧氨氧化區進入該脫氮區。 In another embodiment, the self-operated biological system is present in the anaerobic granular sludge, and the reacted ammonia-containing nitrogen wastewater is introduced into the anaerobic ammonium oxidation zone at a flow rate of 8 to 12 m/hr. Nitrogen zone.
於又一具體實施例中,該異營生物,例如脫氮微生物係存在於非顆粒化污泥及/或顆粒化污泥中。 In yet another embodiment, the meta-organism, such as a denitrifying microorganism, is present in the non-granulated sludge and/or the granulated sludge.
此外,本揭露之廢水處理方法中,復包括於該脫氮區12添加碳源。例如,利用一管路15將甲醇或異丙醇加入該脫氮區12,以作為脫氮微生物所需之碳源。 In addition, in the wastewater treatment method of the present disclosure, a carbon source is added to the denitrification zone 12. For example, methanol or isopropanol is added to the denitrification zone 12 using a line 15 to serve as a carbon source for the denitrification microorganism.
請參閱第2圖,係說明廢水處理方法之另一具體實施例。 Referring to Figure 2, another embodiment of a wastewater treatment process is illustrated.
如第2圖所示,該生物反應器係一豎設之塔槽或管柱,該生物反應器2中,亦由分離結構14隔開該厭氧氨氧化區10及脫氮區12。是以,在本實施例中,該厭氧氨氧化區10係位於該脫氮區12下方。 As shown in Fig. 2, the bioreactor is a erected column or column in which the anaerobic ammonium oxidation zone 10 and the denitrification zone 12 are also separated by a separation structure 14. Therefore, in the present embodiment, the anaerobic ammonium oxidation zone 10 is located below the denitrification zone 12.
此外,該脫氮區12之體積小於該厭氧氨氧化區10之 體積。例如,該脫氮區12之體積與該厭氧氨氧化區10之體積比為1:8至1:10。 In addition, the volume of the denitrification zone 12 is smaller than the anaerobic ammonium oxidation zone 10 volume. For example, the volume ratio of the volume of the denitrification zone 12 to the anammox zone 10 is from 1:8 to 1:10.
又於非限制性之實施例中,該生物反應器2復具有另一分離結構14’,使該脫氮區12位於該二分離結構14,14’之間。 In still another non-limiting embodiment, the bioreactor 2 has a further separation structure 14' such that the denitrification zone 12 is located between the two separation structures 14, 14'.
於具體實施例中,該分離結構14,14’包括:固定於該生物反應器2內壁之板體140,係具有複數貫穿之孔洞1401;複數阻氣管141,各該阻氣管141係對應連接該孔洞1401;以及複數阻檔件142,係對應設於該阻氣管141下方,且令該阻氣管141與該阻檔件142間具有間隙d。 於該分離結構14,14’之具體實施上,該阻檔件142係可固定於板體140或該生物反應器2內壁,並可由細長的金屬件或塑料連接件作固定(未圖示)。 In a specific embodiment, the separation structure 14, 14' includes: a plate body 140 fixed to the inner wall of the bioreactor 2, having a plurality of holes 1401; a plurality of gas barrier tubes 141, each of the gas barrier tubes 141 being connected The hole 1401; and the plurality of blocking members 142 are correspondingly disposed under the gas blocking tube 141, and have a gap d between the gas blocking tube 141 and the blocking member 142. In the specific implementation of the separating structure 14, 14', the blocking member 142 can be fixed to the plate body 140 or the inner wall of the bioreactor 2, and can be fixed by an elongated metal member or a plastic connecting member (not shown). ).
請參閱第3圖,係以立體圖說明所示之板體140及阻氣管141,各該阻氣管141係對應連接該孔洞1401而設於該板體140底面。 Referring to FIG. 3, the plate body 140 and the gas barrier tube 141 are illustrated in a perspective view, and each of the gas barrier tubes 141 is disposed on the bottom surface of the plate body 140 correspondingly to the hole 1401.
於第2圖之非限制性實施例中,該生物反應器2復具有傾斜板16,使該脫氮區12位於該分離結構14與傾斜板16之間,其中,該傾斜板16可阻檔固體,例如脫氮汙泥,而液體則可通過該傾斜板16。 In a non-limiting embodiment of FIG. 2, the bioreactor 2 has a sloping plate 16 such that the denitrification zone 12 is located between the separation structure 14 and the sloping plate 16, wherein the sloping plate 16 is damped A solid, such as a denitrified sludge, is passed through the inclined plate 16.
此外,於一實施例中,該自營生物係存在於厭氧汙泥中,是以,該生物反應器中之該脫氮區12底部,亦即該分離結構14上方具有第一回流管路18,並可透過泵P之輸送,俾將上升至該脫氮區12之厭氧汙泥回流至該厭氧氨氧 化區10。 In addition, in an embodiment, the self-operated biological system is present in the anaerobic sludge, so that the bottom of the denitrification zone 12 in the bioreactor, that is, the first return line above the separation structure 14 18, and through the transport of the pump P, the anaerobic sludge rising to the denitrification zone 12 is returned to the anaerobic ammonia Zone 10.
又,該異營生物係存在於脫氮汙泥中,是以,該脫氮區12頂部具有第二回流管路19,並可透過泵P之輸送,俾將上升至該另一分離結構14’上之脫氮汙泥回流至該脫氮區12。另一方面,用作碳源之甲醇或異丙醇亦可透過第二回流管路19加入該脫氮區12,以作為脫氮微生物所需之碳源。 Moreover, the heterogeneous organism is present in the denitrification sludge, so that the top of the denitrification zone 12 has a second return line 19 and can be transported through the pump P, and the helium will rise to the other separation structure 14 The upper denitrified sludge is returned to the denitrification zone 12. On the other hand, methanol or isopropyl alcohol used as a carbon source can also be introduced into the denitrification zone 12 through the second reflux line 19 to serve as a carbon source required for the denitrification microorganism.
利用一包含厭氧氨氧化區(體積為40 L)及位於該氧氨氧化反應區上方之脫氮區(體積為5 L)之生物反應器進行廢水處理測試,其中,厭氧氨氧化區中植入厭氧氨氧化微生物(如Candidatus Kuenenia stuttgartiensis;Candidatus Anammoxoglobus propionicus;Candidatus Jettenia asiatica;Candidatus Brocadia fulgida;Candidatus Brocadia anammoxidans等菌屬),其係馴養於厭氧顆粒化污泥;而脫氮區植入脫氮微生物,其係馴養於非顆粒化污泥或厭氧顆粒化污泥。並以8 m/hr的流速使該經反應的含氨氮廢水自該厭氧氨氧化區進入該脫氮區,其中,待處理之含氨氮廢水的氨氮濃度與亞硝酸氮濃度為240 mg/L以及260 mg/L。生物反應器之平均處理量為60 mL/min,換算成總氮負荷為約1 kg N/m3-d。此廢水經過本發明之生物反應器之進出流水各項污染物濃度指標如第4圖所示,其中,每週分析一次數據,得到6組結果。 Wastewater treatment test using a bioreactor containing an anaerobic ammonium oxidation zone (40 L in volume) and a denitrification zone (5 L in volume) above the oxyammoxidation zone, wherein the anaerobic ammonium oxidation zone Implanted anaerobic ammonium oxidizing microorganisms (such as Candidatus Kuenenia stuttgartiensis; Candidatus Anammoxoglobus propionicus; Candidatus Jettenia asiatica; Candidatus Brocadia fulgida; Candidatus Brocadia anammoxidans and other genus), which are domesticated in anaerobic granular sludge; A denitrifying microorganism that is domesticated in non-granulated sludge or anaerobic granular sludge. And the reacted ammonia-containing nitrogen wastewater is introduced into the denitrification zone from the anaerobic ammonium oxidation zone at a flow rate of 8 m/hr, wherein the ammonia nitrogen concentration and the nitrite nitrogen concentration of the ammonia-nitrogen-containing wastewater to be treated are 240 mg/L. And 260 mg/L. The average treatment capacity of the bioreactor was 60 mL/min, which was converted to a total nitrogen load of about 1 kg N/m 3 -d. The concentration index of the pollutants in the inflow and outflow water of the bioreactor according to the present invention is as shown in Fig. 4, wherein the data is analyzed once a week to obtain six sets of results.
如第4圖所示之結果,即使進流水之氨氮與亞硝酸氮濃度高達260 mg/L及300 mg/L,反應器出流水之氨氮與亞硝酸氮濃度分別降低至30 mg/L以下,目標污染物之去除率可達90%以上。又,此反應理論上應產生約56 mg/L之硝酸氮,但由本揭露之方法,反應器出流水之硝酸氮僅約2 mg/L。 As shown in Figure 4, even if the ammonia nitrogen and nitrite concentrations in the influent water are as high as 260 mg/L and 300 mg/L, the ammonia nitrogen and nitrite nitrogen concentrations in the reactor outlet water are reduced to less than 30 mg/L, respectively. The target pollutant removal rate can reach more than 90%. Further, this reaction theoretically produces about 56 mg/L of nitrate nitrogen, but by the method of the present disclosure, the nitrate nitrogen in the reactor outlet water is only about 2 mg/L.
上述實施例係用以例示性說明本揭露之原理及其功效,而非用於限制本揭露。任何熟習此項技藝之人士均可在不違背本揭露之精神及範疇下,對上述實施例進行修改。因此本揭露之權利保護範圍,應如後述之申請專利範圍所列。 The above embodiments are intended to illustrate the principles of the disclosure and its functions, and are not intended to limit the disclosure. Any person skilled in the art can modify the above embodiments without departing from the spirit and scope of the disclosure. Therefore, the scope of protection of the present disclosure should be as set forth in the scope of the patent application described later.
1,2‧‧‧生物反應器 1,2‧‧ bioreactor
10‧‧‧厭氧氨氧化區 10‧‧‧ Anaerobic ammonium oxidation zone
12‧‧‧脫氮區 12‧‧‧Denitration zone
14,14’‧‧‧分離結構 14,14’‧‧ separate structure
140‧‧‧板體 140‧‧‧ board
1401‧‧‧孔洞 1401‧‧‧ holes
141‧‧‧阻氣管 141‧‧‧Stem tube
142‧‧‧阻檔件 142‧‧‧blocks
15‧‧‧管路 15‧‧‧pipe
16‧‧‧傾斜板 16‧‧‧ sloping plate
18‧‧‧第一回流管路 18‧‧‧First return line
19‧‧‧第二回流管路 19‧‧‧Second return line
W‧‧‧含氨氮廢水 W‧‧‧Ammonia-nitrogen wastewater
W’‧‧‧經反應的含氨氮廢水 W’‧‧‧Reacted ammonia-containing wastewater
d‧‧‧間隙 D‧‧‧ gap
P‧‧‧泵 P‧‧‧ pump
第1圖係本揭露廢水處理方法之示意圖;以及第2圖係說明本揭露一具體實施例之廢水處理方法;第3圖係顯示該分離結構之板體及阻氣管之立體圖;以及第4圖係顯示經本揭露廢水處理方法處理後之汙染物濃度。 1 is a schematic view showing a wastewater treatment method; and FIG. 2 is a schematic view showing a wastewater treatment method according to an embodiment of the present invention; and FIG. 3 is a perspective view showing a plate body and a gas barrier pipe of the separation structure; and FIG. The concentration of the pollutants treated by the disclosed wastewater treatment method is shown.
1‧‧‧生物反應器 1‧‧‧Bioreactor
10‧‧‧厭氧氨氧化區 10‧‧‧ Anaerobic ammonium oxidation zone
12‧‧‧脫氮區 12‧‧‧Denitration zone
14‧‧‧分離結構 14‧‧‧Separate structure
15‧‧‧管路 15‧‧‧pipe
W‧‧‧含氨氮廢水 W‧‧‧Ammonia-nitrogen wastewater
W’‧‧‧經反應的含氨氮廢水 W’‧‧‧Reacted ammonia-containing wastewater
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TWI784103B (en) * | 2017-12-13 | 2022-11-21 | 學校法人東洋大學 | Carrier for maintaining anammox bacteria (Anammox) flora for wastewater treatment, anammox flora attachment, and wastewater treatment device using the attachment |
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CN100526233C (en) * | 2007-01-19 | 2009-08-12 | 华南理工大学 | Anerobic ammoxidation and denitrification synergistic denitrification method for garbage leachate |
CN101050026B (en) * | 2007-04-17 | 2010-11-03 | 北京市环境保护科学研究院 | Deepness denitrogenation method for treating organic wastewater in high concentration |
CN101759320A (en) * | 2008-12-26 | 2010-06-30 | 财团法人工业技术研究院 | Treating system and method of ammonia nitrogen wastewater |
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