TW460312B - Method and apparatus of regenerative electrolysis/oxidation scrubber - Google Patents
Method and apparatus of regenerative electrolysis/oxidation scrubber Download PDFInfo
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460312 五、發明說明(1) 【發明領域】 本發明係有關於一種整合電解氧化技術於洗滌技術、 可有效去除臭味及/或有機廢氣的方法及其裝置。本發明 之特徵在於將廢氣中的臭味及/或有機物在洗滌塔及電解/ 氧化槽被化學氧化及電解氧化’同時於電解過程中再生氧 化劑供洗滌塔使用。 【發明背景】 傳統洗滌技術可以利用於處理臭味及/或有機廢氣, 但在實際應用上仍有以下缺點: 1. 氧化劑耗用量大、操作成本高。 2. 氧化劑需大量儲存、會產生大量廢水等問題,易造 成工安及環保問題。 3. 使用工業級次氣酸處理例如含HaS廢氣時,易產生 嚴重鈣鹽、鎂鹽結垢問題。 【發明目的與本發明之詳細說明】 基於上述傳統洗滌技術之缺點’本發明的目的乃是要 提供一種廢氣處理的方法及其裝置,以大幅降低操作成 本,並排除設備結垢及工安環保等問題。本發明並提供— 種可以穩定維持洗滌技術之高處理效率的控制方法。 本發明之廢氣處理方法包括以下步驟: a.將進流廢氣導入洗滌塔本體(1 ),與循環至洗滌炫 之洗滌液進行氣液接觸’廢氣因其中污染物被吸收至洗°膝460312 V. Description of the invention (1) [Field of the invention] The present invention relates to a method and a device for integrating electrolytic oxidation technology into washing technology, which can effectively remove odor and / or organic waste gas. The invention is characterized in that the odor and / or organic matter in the exhaust gas are chemically oxidized and electrolytically oxidized 'in the washing tower and the electrolysis / oxidation tank, and the oxidizing agent is regenerated in the electrolysis process for the washing tower. [Background of the Invention] Traditional washing technology can be used to treat odor and / or organic waste gas, but it still has the following disadvantages in practical applications: 1. Large consumption of oxidant and high operating cost. 2. A large amount of oxidants need to be stored, and a large amount of wastewater will be generated, which will easily cause industrial safety and environmental problems. 3. When using industrial-grade inferior acid to treat waste gas containing HaS, it is easy to produce serious calcium and magnesium salt scaling problems. [Objective of the invention and detailed description of the present invention] Based on the disadvantages of the traditional washing technology described above, the purpose of the present invention is to provide an exhaust gas treatment method and a device thereof, so as to greatly reduce operating costs, and eliminate equipment fouling and industrial safety and environmental protection. And other issues. The invention also provides a control method capable of stably maintaining the high processing efficiency of the washing technology. The exhaust gas treatment method of the present invention includes the following steps: a. Incoming exhaust gas is introduced into the washing tower body (1), and is brought into gas-liquid contact with the washing liquid circulating to the washing column.
C:\path\0424-4223~E. ptd i~5~I ' ----- 46031 2 五、發明說明(2) --- 液中而被淨化排放。 b.部分的污染物在上述過程中已被氧化分解,而反應 速率較慢的污染物,則會隨著洗滌液進入電解/氧化槽‘ 中,繼續被氧化劑(次氣酸鈉或過氧化氫)以化學氧化9作用 或/及電解氧化作用分解’ 述電解/氧化槽包括洗滌廢水 儲槽(6)、電解槽(7)、再生洗滌液儲槽(8)等。 c,洗條液在上述電解/氧化槽中,消耗掉的氧化劑會 被電解再生而提高濃度’供循環至洗滌塔本體。 如第1圖所示,本發明之廢氣處理裝置包括: a. 提供廢氣與循環至洗滌塔之洗滌液進行氣液接觸之 裝置’包括洗蘇塔本體(1)、濃水嘴頭(2)、填料(3)、廢 氣處理前入口(4)、廢氣處理後出口(5)等。第1圖顯示為 以立式洗滌塔、氣液逆向流方式進行接觸,實際上洗滌塔 本體(1)可設計為多種形式,如立式或臥式,氣液接觸方 式可為逆向流、同向流或為橫向流。灑水噴頭(2)亦可為 其他液體分配器取代,如V型槽溝、各式溢流管槽。 b. 電解/氧化槽,包括洗滌廢水儲槽(6)、電解槽 (Ό、再生洗滌液儲槽(8)及陰陽極電極板(11)等。陰陽極 電極板係由不鏽鋼'鈦等金屬構成,作為電解再生次氯酸 、電解氧化污染物之用。其電解所需能量來自電源供應器 提供之高電壓、低電流之直流電。其電極板是適合洗滌液 循環流量的規格。當洗滌液循環至電解/氧化槽時,其中 反應速率較慢的污染物會在槽中繼續被氧化劑以化學氧化 作用或/及被陰陽極電極板所提供的電解氧化作用分解;C: \ path \ 0424-4223 ~ E. Ptd i ~ 5 ~ I '----- 46031 2 V. Description of the invention (2) --- It is purified and discharged in the liquid. b. Some pollutants have been oxidized and decomposed in the above process, while pollutants with slower reaction rate will enter the electrolysis / oxidation tank with the washing liquid and continue to be oxidized (sodium hypoxia or hydrogen peroxide). ) Decomposed by chemical oxidation 9 or / and electrolytic oxidation. The electrolysis / oxidation tank includes a washing wastewater storage tank (6), an electrolytic tank (7), a regeneration washing liquid storage tank (8), and the like. c. In the electrolysis / oxidation tank described above, the consumed oxidant will be regenerated by electrolysis to increase the concentration 'for circulation to the washing tower body. As shown in Figure 1, the exhaust gas treatment device of the present invention includes: a. A device for providing gas-liquid contact between the exhaust gas and the washing liquid circulating to the washing tower, including a washing tower body (1), a concentrated water nozzle (2) , Filler (3), inlet (4) before exhaust gas treatment, outlet (5) after exhaust gas treatment, etc. Figure 1 shows the contact with the vertical washing tower and gas-liquid countercurrent flow. In fact, the washing tower body (1) can be designed in various forms, such as vertical or horizontal. The gas-liquid contact method can be countercurrent, Directional or lateral flow. The sprinkler (2) can also be replaced by other liquid distributors, such as V-shaped grooves and various overflow pipe grooves. b. Electrolysis / oxidation tank, including washing wastewater storage tank (6), electrolytic tank (Ό, regeneration washing liquid storage tank (8), cathode and anode electrode plate (11), etc.) The anode and cathode electrode plate is made of stainless steel, titanium, etc. The structure is used for electrolytic regeneration of hypochlorous acid and electrolytic oxidation pollutants. The energy required for electrolysis comes from the high voltage and low current DC power provided by the power supply. Its electrode plate is suitable for the circulating flow rate of the washing liquid. When the washing liquid When circulating to the electrolysis / oxidation tank, the pollutants with a slower reaction rate will continue to be decomposed by the oxidant in the tank by chemical oxidation or / and by the electrolytic oxidation provided by the cathode and anode electrode plates;
第6頁 C:\path\0424-4223-E. ptd 46031Page 6 C: \ path \ 0424-4223-E. Ptd 46031
解再生而提高濃度,供循環 而其中消耗掉的氧化劑會被電 至洗滌塔本體。 陽二==行至電解/氧化槽中的陰 β廢亂地理監控系統(1 6 ),電解/氧化槽中洗滌液水 質水1監測及調整控制,電源供應器(12)電流、電壓強度 的調整控制等,皆可藉助於廢氣處理監控系統(16)進行。 廢氣處理監控系統包含多項監測控制設備,例如監測洗滌 液水質水量之pH meter、0RP meter、液位計,監測電解 效果之電流、電壓計等。 e.加藥(包括食鹽水、氫氧化鈉)系統14)及軟水 (或純水)供應系統(1 5 ),提供上述溶液以調整進入電解/ 氧化槽之洗滌液水質。 洗條塔本體(1)可如圖中所示與下方之電解/氧化槽(6 )〜(8)合為一體,亦可分開建造為兩獨立設備。廢氣處理 後出口( 5)後端可視情況加裝第二段洗滌塔以去除多餘之 漂白水味道。收集廢氣的風車可視情況而安裝於廢氣處理 前入口(4)前端、或廢氣處理後出口(5)後端。 本發明在電解/氧化槽中,利用電解作用再生氧化劑 及分解污染物。其氧化劑再生反應程序之原理說明如下, 以食鹽水電解產生次氯酸為例,在陰極及陽極分別可將 Na+及CT還原或氧化為Na及Cl2,其中Na很快地與1〇反應生 成NaOH,隨後NaOH與Cl2反應產生次氣酸。Decompose and regenerate to increase the concentration for recycling and the oxidant consumed in it will be charged to the scrubber body. Yang Er == Go to the negative beta waste geographical monitoring system (1 6) in the electrolytic / oxidation tank, monitor and adjust the control of the washing water quality and water in the electrolytic / oxidation tank, and adjust the current and voltage intensity of the power supply (12) Control and the like can be performed by means of an exhaust gas treatment monitoring system (16). The exhaust gas treatment monitoring system includes a number of monitoring and control equipment, such as pH meter, ORP meter, liquid level meter to monitor the water quality and quantity of washing liquid, current, voltage meter to monitor the effect of electrolysis, etc. e. Dosing system (including brine, sodium hydroxide) system 14) and soft water (or pure water) supply system (15), provide the above solution to adjust the water quality of the washing liquid entering the electrolysis / oxidation tank. The washing bar body (1) can be integrated with the electrolysis / oxidation tanks (6) to (8) below as shown in the figure, or it can be constructed separately as two independent devices. After the exhaust gas treatment (5), the rear end of the outlet (5) may be installed with a second stage washing tower to remove the excess bleach taste. The windmill collecting the exhaust gas may be installed at the front end of the inlet (4) before the exhaust gas treatment, or at the rear end of the outlet (5) after the exhaust gas treatment, as appropriate. The present invention uses electrolysis to regenerate oxidants and decompose pollutants in an electrolysis / oxidation tank. The principle of the oxidant regeneration reaction procedure is explained as follows. Take hypochlorous acid produced by electrolysis of brine as an example. Na + and CT can be reduced or oxidized to Na and Cl2 respectively at the cathode and anode, where Na reacts quickly with 10 to form NaOH Then, NaOH reacts with Cl2 to produce hypogas acid.
C:\path\0424-4223-E. ptd 第7頁 46〇312 五、發明說明(4) 陰極(-):2 Na+(aq) + 2e~ 2 Na(s) 2 Na(s) + 2 H20 - 2 NaOH(aq) + H2(g) 陽極(+) : 2 Cl (aq) — Cl2(g) + 2e-C: \ path \ 0424-4223-E. Ptd Page 7 46〇312 V. Description of the invention (4) Cathode (-): 2 Na + (aq) + 2e ~ 2 Na (s) 2 Na (s) + 2 H20-2 NaOH (aq) + H2 (g) Anode (+): 2 Cl (aq) — Cl2 (g) + 2e-
Cl2 +2 NaOH — NaOCl +H20 十 NaCl 電解及氧化劑氧化分解污染物原理說明如下,以 sulfoxides的電解氧化破壞為例,經過電解之後會產生醇 類(R0H)及硫醇類(RSH)產物。醇類、硫醇類最後會被氧化 劑,如次氣酸分解為C02、H20及無機鹽類。 + 2 R%R1 2 hr OIS + R1 2 hr 〇ls+ R1 十 2 hr 〇ls- R1 oxidentThe principle of Cl2 +2 NaOH — NaOCl + H20 and NaCl electrolysis and oxidant decomposition of pollutants are explained below. Taking the electrolytic oxidation destruction of sulfoxides as an example, alcohol (R0H) and thiol (RSH) products will be produced after electrolysis. Alcohols and thiols are finally decomposed into CO2, H20 and inorganic salts by oxidizing agents such as hypogas. + 2 R% R1 2 hr OIS + R1 2 hr 〇ls + R1 ten 2 hr 〇ls- R1 oxident
◦H R1 + r2S0H C〇2 + H20 +S〇4*"+ COOH R^R2 oxident ,2◦H R1 + r2S0H C〇2 + H20 + S〇4 * " + COOH R ^ R2 oxident, 2
R-|SH + R2〇H ......,C〇2 + H2〇十 S04 z + COOH 在本發明所處理之臭味及/或有機廢氣廢氣中’含臭 味廢氣之臭咮成份係指分子結構中含氮、硫元素,造成— 般認知之異味成份,如硫化氫、甲硫醇、乙硫醇、二甲基R- | SH + R2〇H ......, Co 2 + H 2 0 S04 z + COOH In the odor and / or organic exhaust gas treated by the present invention, the odor component of the odorous exhaust gas Refers to nitrogen and sulfur elements in the molecular structure, which cause odors that are generally recognized, such as hydrogen sulfide, methyl mercaptan, ethyl mercaptan, dimethyl
C:\path\0424-4223-E. ptd 第8胃C: \ path \ 0424-4223-E. Ptd stomach 8
4 δ Ο 3 Ί 五 '發明說明(5) 硫化物及類似含硫之化合物’含氮者如氨、— 基胺及類似含氮之化合物。而揮發性有機物/甲基胺、甲 下蒸氣壓在O.lromHg以上之有機化合物,如自/、心吊遷常壓 醛類、醇類、酮類、有機醆類及芳香族化人9類、鰱類、 本發明之應用領域包括: "" ° 1. 皮革業廢水池含硫化氫廢氣之處理。 2. 飼料(食品加工下腳料)化製廠惡臭 3. 其他採厭氧生物處理廢水池含硫化氯廢氣3理 4. 都市污水處理場、垃圾掩埋臭味氣體之處理。。 I ί:Ϊ硫化氫、硫醇類、胺類、氨等廢氣之處理。 硫化氫時,氧化每克硫化氫所需廢氣所含污染物為 布凡 C虱所茗的次氣酸為4〜9克,其平 均操作電流為130〜160安培。 為讓本發明之上述和立他目沾 顯易懂,下文特舉一較:實::的托特徵、和優點能更明 細說明如下: 較佳實細例’並配合所附圖式’作詳 【圖式之簡單說明】 第1圖為本發明之再生式電解 示意圖。 第2圖繪示本發明實施例中對 去除率。 【符號說明】 氧化洗滌系統之裝置之 不同進氣濃度範圍的h2s4 δ Ο 3 Ί 5 'Explanation of the invention (5) Sulfides and similar sulfur-containing compounds' Nitrogen-containing ones such as ammonia, -amino and similar nitrogen-containing compounds. Volatile organic compounds / methylamines, organic compounds with vapor pressure above 0.1 romHg, such as atmospheric pressure aldehydes, alcohols, ketones, organic amidines, and aromatic humans The application fields of the invention include: " " ° 1. Treatment of hydrogen sulfide-containing waste gas in the leather industry wastewater pond. 2. Foul odor in feed plants (residues for food processing) 3. Other anaerobic biological treatment wastewater treatment tanks containing chlorine sulfide waste gas. 3. Treatment of odorous gases in urban sewage treatment plants and landfills. . I ί: Ϊ Treatment of waste gases such as hydrogen sulfide, mercaptans, amines, and ammonia. In the case of hydrogen sulfide, the amount of pollutants contained in the exhaust gas required for oxidizing hydrogen sulfide per gram is 4-9 grams, and the average operating current is 130-160 amps. In order to make the above-mentioned and other objectives of the present invention comprehensible, the following special comparison is made: The characteristics and advantages of the support can be described in more detail as follows: [Simplified description of the diagram] FIG. 1 is a schematic diagram of the regenerative electrolysis of the present invention. Fig. 2 shows the removal rate in the embodiment of the present invention. [Symbol description] The h2s of different inlet concentration range of the device of the oxidation washing system
第9頁 C:\path\0424-4223-E. ptd 460312 五、發明說明(6) 1〜洗務塔本體;2〜·:ϋ & ^ 入口 ; 5〜廢氣處理後出^水嗔頭;3〜填料〜廢氣處理前 槽;8〜再生洗滌液儲槽.〇’ :為洗滌廢水儲槽;7〜電解 液流量計;1卜陰陽極電極:洗滌液循環幫浦:1 0 ~洗滌 加藥系統:15〜軟水(或純^极12〜電源供應器;13、14〜 糸絲.1 7 #% /純水)供應系統;1 6〜廢氣處理監控 系統,17廢洗滌液或污泥排放口。 【實施例】 本發明之實施例乃針對皮革業廢水處理廠含硫化氫廢 氣進行測試,設備操作條件為:(Α).廢氣進流風量4CMM、 硫化氫濃度範圍為0〜2 0 0ppm以上;(b ).洗滌液循環流量 15〜20 lpm ; (C).電源供應器提供75〜180 a、5〜10 V之 直流電源;(D).控制進入電解槽之洗滌液PH值於8以上; (E )·連續測試期間,現場分析項目包括:每3分鐘以 online GC/FPD分析一組廢氣處理前後H2S濃度,每0.5-1 分鐘以on line pH/ORP controller記錄一組洗滌液於廢氣 處理前後之pH及0RP值’每1 5分鐘〜30分鐘以滴定法分析 一組洗滌液於廢氣處理前後之有效氣濃度’並記錄電解設 備電源供應器輸出之電壓、電流值。 表1、實驗測試結果Page 9 C: \ path \ 0424-4223-E. Ptd 460312 V. Description of the invention (6) 1 ~ washing tower body; 2 ~ ·: ϋ & ^ inlet; 5 ~ water outlet after exhaust gas treatment 3 ~ filler ~ tank before exhaust gas treatment; 8 ~ regeneration washing liquid storage tank. 〇 ': washing wastewater storage tank; 7 ~ electrolyte flowmeter; 1 anode cathode: washing liquid circulation pump: 1 0 ~ washing Dosing system: 15 ~ soft water (or pure ^ pole 12 ~ power supply; 13, 14 ~ reel. 1 7 #% / pure water) supply system; 16 ~ exhaust gas monitoring system, 17 waste washing liquid or dirty Mud drain. [Examples] The examples of the present invention are tested for hydrogen sulfide-containing waste gas in a leather industry wastewater treatment plant. The operating conditions of the equipment are: (A). The exhaust gas inlet air flow is 4CMM, and the concentration of hydrogen sulfide is in the range of 0 to 200 ppm. (B). Circulating flow of washing liquid 15 ~ 20 lpm; (C). Power supply provides DC power of 75 ~ 180 a, 5 ~ 10 V; (D). Control the pH of washing liquid entering the electrolytic tank above 8 (E) · During continuous testing, the on-site analysis items include: An online GC / FPD analysis of H2S concentration before and after a group of exhaust gas treatments every 3 minutes, and an on-line pH / ORP controller every 0.5-1 minutes to record a group of washing liquids in the exhaust gas The pH and 0RP values before and after the treatment 'analyze the effective gas concentration of a set of washing liquid before and after the exhaust gas treatment by titration every 15 minutes to 30 minutes' and record the voltage and current values output by the power supply of the electrolytic equipment. Table 1. Experimental test results
第10頁 C:\path\0424-4223-E. ptd 4 6 0 3:: 五、發明說明(7) 實驗 次序 累計拣作 時 fel(hi) H2s平均 遠JL滾度 tea) 平岣操作 電流(A) IfeS爷均 士徐孪ο) 有效氮消 耗查/h2s 去除董 (重壘比) 有效氣消 粍查/H2S 去徐董 (mole tb) 1 7 22.4 83 98 15.1 9.6 2 10 57.7 109 96 12.0 7.7 3 12 74.2 133 97 8.1 5.2 4 4.8 147.2 157 92 4.9 3.1 上述實驗測試結果顯示如表1,對不同進氣濃度範圍 的處理前後濃度、處理效率平均值如第2圖所示。由低濃 度範圍至高濃度範圍的進氣條件均可獲得高於95%的處理 效率。且得到以下結果:a.去除1 mole的H2S會消耗3. 1到 9_6 mole的有效氣及1.8 mole的NaOH°b.若以耗電量估 計’則去除1 mole H2S平均消耗電力為丨.ikWhr。 根據上述實驗結果,若以每天操作24小時之情形計算 ’例如當處理硫化氫濃度為〇· 18g/s(廢氣風量2〇〇CMM、硫 化氫濃度4〇0口111)之廢氣時’次氣酸需求量為1.981^/(1&丫。 而提供前述氧化劑之電解設備規格包括:a·陽極極板面積 需要7·5〜17‘5 m2及b·可提供至少7500〜17500安培之電源 供應器。Page 10 C: \ path \ 0424-4223-E. Ptd 4 6 0 3: 3: Fifth, description of the invention (7) Experiment order cumulative fel (hi) H2s average far JL roll tea) leveling operation current (A) IfeS Ye Junshi Xu Quan.) Effective nitrogen consumption check / h2s removal of Dong (weight barrier ratio) Effective gas elimination check / H2S to Xu Dong (mole tb) 1 7 22.4 83 98 15.1 9.6 2 10 57.7 109 96 12.0 7.7 3 12 74.2 133 97 8.1 5.2 4 4.8 147.2 157 92 4.9 3.1 The above experimental test results are shown in Table 1. The average concentration and treatment efficiency before and after treatment for different ranges of intake air concentration are shown in Figure 2. Intake conditions from low concentration range to high concentration range can achieve treatment efficiency higher than 95%. And get the following results: a. Removing 1 mole of H2S will consume 3.1 to 9_6 moles of effective gas and 1.8 moles of NaOH ° b. If the power consumption is estimated, the average power consumption of removing 1 mole of H2S is 丨 .ikWhr . According to the above experimental results, if the operation is performed for 24 hours a day, for example, when treating an exhaust gas with a hydrogen sulfide concentration of 0.018 g / s (exhaust air volume of 200 CMM, hydrogen sulfide concentration of 4,000 port 111), the secondary gas The acid demand is 1.981 ^ / (1 & ah. The specifications of the electrolytic equipment that provides the aforementioned oxidants include: a. The anode plate area requires 7.5 to 17'5 m2 and b. A power supply of at least 7,500 to 17,500 amps can be provided Device.
4 6 0 3 五、發明說明(8) 以含次氣酸洗滌液洗滌含硫化氫廢氣後,可能會以下 產物(Bonnin,Odor and Deoder i za t i on in the environment, 1994): S3'+4C10^SO;'+4a·4 6 0 3 V. Description of the invention (8) After washing the hydrogen sulfide-containing waste gas with a sub-gas acid cleaning solution, the following products may be produced (Bonnin, Odor and Deoder i za ti on in the environment, 1994): S3 '+ 4C10 ^ SO; '+ 4a ·
Bonnin指出理論上處理1 mole的H2S會消耗4 mole的 有效氣。Bonn in並曾在pH控制於9的條件下,以模庭設備 處理含有濃度5-10mg/m3之HZS的廢氣,實驗結果可以達到 99.8%以上的I^S去除率’該實驗並得到去除1 mole的Hs 將會消耗5.2 111〇16(^12及5 111〇16^011的結論。 表1實驗測試結果顯示’四次實驗之氧化劑消耗量有 隨污染物進氣濃度提高而降低的趨勢。由第3次實驗結果 得知,其氧化劑消耗量等於前述文獻以直接添加氧化劑方 式實驗之消耗量。至第4次實驗結果則顯示,其氧化劑消 耗量已遠低於前述文獻以直接添加氧化劑方式實驗之消耗 量甚至已遠低於理論上直接添加氧化劑方式之消耗量。 上述第4次實驗結果顯示,在理想操作條件下,以電解再 生方式所供應的氧化劑較理論值為低,也就證實了在化學 氧化之外,電解作用亦提供了對污染物氧化分解的Bonnin pointed out that theoretically processing 1 mole of H2S would consume 4 moles of effective gas. Bonn in also used the mold chamber equipment to treat the exhaust gas containing HZS with a concentration of 5-10mg / m3 under the condition that the pH was controlled at 9. The experimental results can reach an I ^ S removal rate of more than 99.8%. The Hs of mole will consume 5.2 111〇16 (^ 12 and 5 111〇16 ^ 011). Table 1 experimental test results show that the consumption of oxidants in the four experiments has a tendency to decrease with the increase of the concentration of pollutants. From the results of the third experiment, it is known that the consumption of oxidant is equal to the consumption of the previous literature by adding the oxidant directly. The results of the fourth experiment show that its consumption of oxidant is much lower than that of the previous literature by adding the oxidant directly. The consumption of the experiment is much lower than the theoretical consumption of direct oxidant. The results of the fourth experiment show that under ideal operating conditions, the oxidant supplied by electrolytic regeneration is lower than the theoretical value, which proves that In addition to chemical oxidation, electrolysis also provides
理論上電解過程所產生每一mole電子,其氧化 為次氯酸的1/2。 於此刀J 在整個廢氣處理系統的控制方面 由實驗過裎中得知Theoretically, each mole of electrons generated during the electrolytic process is oxidized to 1/2 of hypochlorous acid. Here the knife J is known from the experimental experience in the control of the entire exhaust gas treatment system.
4 6 0 :; ^ 五、發明說明(Q) • 電解/氧化槽中ρΗ值的變化恰好反應了廢氣進流濃度 的商低’ b.不宜以0RP作為氧化劑濃度高低的指標,因〇Rp 測值僅在氡化劑濃度較低範圍呈線性關係、在高濃度時 0RP值變動不明顯,且0RP測值易受"值影響。但在氧化劑 已大量消耗、補充不足時0RP測值會有較顯著的下降。因 此’ pH值可以作為電解設備運轉的主要控制參數,〇Rp值 適合作為輔助pH值控制的次要控制參數。 無論是以直接補注氧化劑方式或採用電解再生氡化劑 方式’若監測並控制洗滌液於進入電解槽前之pH值於固定 辜巳圍’如8〜1〇之間。當廢氣進氣濃度越高,此一 pH值變動 頻率越高、鹼的補充量也會越多。此時可提高直接補注氧 化劑之供應量或提高電解再生方式之電流強度β在利用次 氯酸處理硫化氫廢氣之系統,添加之鹼可先將硫化氫以酸 鹼中和反應(硫化氫上氫離子移轉至氫氧根離子形成水分 子)吸收入洗滌液’再以次氣酸氧化劑將之氧化成穩定的 硫酸根離子(負二價硫離子失去八個電子,氧化成含正六 價硫之硫酸根離子)。 於進入電解槽前監測所得之洗滌液0Rp值並未如ρΗ般 有明顯變動,但其ORP測值在氧化劑已大量消耗、未能及 時補充時會有較顯著的下降趨勢。ORP控制範圍在〜900 mv之間’而以70 0〜9 0 0mv為較適當的範圍,即〇Rp測值低於 700〜900 mv時即應提高氧化劑供應量,直到〇Rp測值回升。 因此,在實廠廢氣處理上可降低設備之初設成本的作 法是不須針對曉間高濃度、而僅針對平均濃度進行提供氧4 6 0 :; ^ V. Description of the invention (Q) • The change of ρΗ value in the electrolysis / oxidation tank just reflects the low quotient of the exhaust gas inflow concentration 'b. It is not appropriate to use 0RP as an indicator of the level of oxidant concentration. The values only have a linear relationship in the lower range of the osmotic agent concentration, the 0RP value does not change significantly at high concentrations, and the 0RP measurement value is susceptible to the " value. However, when the oxidant has been consumed in large quantities and supplemented insufficiently, the measured value of 0RP will decrease significantly. Therefore, the pH value can be used as the main control parameter for the operation of the electrolytic equipment, and the 〇Rp value is suitable as the secondary control parameter for auxiliary pH control. Either by direct replenishment of oxidant or by electrolytic regeneration of rhenium, ‘if monitoring and controlling the pH of the washing liquid before entering the electrolytic cell is fixed at 巳 巳,’ such as between 8 ~ 10. When the exhaust gas intake concentration is higher, the higher the frequency of this pH change, the more the alkali replenishment will be. At this time, you can increase the supply of direct replenishing oxidant or increase the current intensity of electrolytic regeneration. In a system that uses hypochlorous acid to treat hydrogen sulfide waste gas, the added alkali can first neutralize the hydrogen sulfide with acid and alkali (hydrogen sulfide on hydrogen) The ions are transferred to hydroxide ions to form water molecules. They are absorbed into the washing solution, and then oxidized to hyposulfite oxidants to form stable sulfate ions (negative divalent sulfur ions lose eight electrons and oxidize to positive hexavalent sulfur containing ions). Sulfate ion). Before entering the electrolytic cell, the ORP value of the washing solution has not changed significantly as ρΗ, but its ORP value will have a significant downward trend when the oxidant has been consumed in large quantities and cannot be replenished in a timely manner. The ORP control range is between ~ 900 mv 'and 70 ~ 900 mv is a more appropriate range. That is, when the measured value of ORP is less than 700 ~ 900 mv, the oxidant supply should be increased until the measured value of ORP rises. Therefore, in the actual plant exhaust gas treatment, the method of reducing the initial installation cost of the equipment is not to provide oxygen for the high concentration of Xiaojian, but only for the average concentration.
C:\path\0424-4223-E. ptd 第13頁 4 6 0 31 五、發明說明(ίο) 化劑之設計。在前述提供氧化劑的條件下,當廢氣進氣濃 度偏高時,可藉助酸鹼中和反應先將污染物吸收入洗滌液 中’當廢氣進氣濃度偏低時,則因氧化劑需求量亦較低, 因此多餘的氧化劑可累積作為高濃度時之用。如此可避免 在氧化劑高濃度時,電解效率降低所導致之高操作成本。 本案發明於洗滌液經電解區前後分別安裝一套酸鹼值 (Ρ Η)感測器及乳化還原電位(〇 R P )感測器,比較洗蘇液與 含硫化氫廢氣接觸前後之pH及ORP變化,做為維持整合設 備穩定高處理效率的控制因子;特別是應用於高濃度負荷 及高濃度變動激烈之含硫化氫廢氣處理的場合時,可利用 上述酸鹼中和較八個電子移轉快速之特性,以添加氫氧化 納調整洗滌液之pH值方式先將硫化氫洗滌下來。 表2比較了次氣酸電解再生溼式洗滌設備與傳統加藥 方式之溼式洗滌設備,同時處理風量2〇〇CMM、平均H2S進 流濃度40 ppm的廢氣之成本。若使用工業級次氣酸,每年 將須多支付約1 5 0萬元的氧化劑購置成本。而電解方式則 較加藥方式多支出300萬的設備成本’約相當於加藥方式 操作2年期間購置氧化劑所須多支出的成本,也就是約2年 時間即可回收在電解設備所投資的成本。 表2、洗務技術之成本比較C: \ path \ 0424-4223-E. Ptd Page 13 4 6 0 31 V. Description of the invention (ίο) Design of chemical agents. Under the aforementioned conditions for providing oxidant, when the exhaust gas inlet concentration is high, the pollutants can be absorbed into the washing liquid by means of acid-base neutralization reaction. When the exhaust gas inlet concentration is low, the demand for oxidant is also relatively low. Low, so excess oxidant can be accumulated for high concentrations. This avoids high operating costs due to reduced electrolysis efficiency at high oxidant concentrations. In the present invention, a set of pH value sensors and emulsification reduction potential (〇RP) sensors are respectively installed before and after the washing solution passes through the electrolysis zone, and the pH and ORP of the washing solution before and after contact with the hydrogen sulfide-containing exhaust gas are compared. Change, as a control factor to maintain the stability and high processing efficiency of the integrated equipment; especially when it is used in the treatment of high concentration load and high concentration fluctuating hydrogen sulfide-containing waste gas, the above acid and base can be used to neutralize eight electron transfers The fast characteristic is to wash the hydrogen sulfide first by adding sodium hydroxide to adjust the pH value of the washing solution. Table 2 compares the cost of the secondary gas acid electrolytic regeneration wet scrubbing equipment with the traditional dosing wet scrubbing equipment, while processing the waste air with an air volume of 2000 CMM and an average H2S inflow concentration of 40 ppm. If industrial grade secondary gas is used, it will have to pay about 15 million yuan more for oxidant purchase cost each year. The electrolysis method costs 3 million more equipment costs than the dosing method, which is equivalent to the additional cost of purchasing the oxidant during the two-year operation of the dosing method, that is, the investment in the electrolytic equipment can be recovered in about two years. cost. Table 2. Cost comparison of washing technology
第14頁 C:\path\0424-4223-E. ptd A6031? 五、發明說明(11) (以廢氣風董200CMM,H2S濃度40ppm概估) 次氣酸 電解生 it:式洗務 次Μ 澄式克條 次嫌電縣生软備 300 _ Γ4无) 兩段规掩職備 320 320 祕作成本 供應氣(洲成本 108 267 難作成本 199 358 雖然本發明已以較佳實施例揭露如上,然其並非用以 限定本發明,任何熟習此技藝者,在不脫離本發明之精神 和範圍内,當可作各種之更動與潤飾,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。Page 14 C: \ path \ 0424-4223-E. Ptd A6031? V. Description of the invention (11) (Estimated by exhaust gas wind 200CMM, H2S concentration 40ppm) Secondary gas acid electrolysis it: type washing service It is suspected that the electric power of the county ’s soft preparation is 300 _ Γ4 None. The two-stage regulation covers 320 320 secret cost supply gas (Continent cost 108 267 Difficult cost 199 358) Although the present invention has been disclosed above in a preferred embodiment, However, it is not intended to limit the present invention. Any person skilled in the art can make various modifications and retouches without departing from the spirit and scope of the present invention. Therefore, the protection scope of the present invention shall be regarded as the scope of the attached patent application. Defined shall prevail.
第15頁 C:\path\0424-4223-E.ptdPage 15 C: \ path \ 0424-4223-E.ptd
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