TW452640B - Semi-offline feedback-type ozone water processing system for circulation water of cooling tower - Google Patents
Semi-offline feedback-type ozone water processing system for circulation water of cooling tower Download PDFInfo
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452640 五、發明說明(1) 【發明領域】 本發明係有關冷卻水塔循環水以臭氧作為消毒劑之處 理系統,更特別地係關於一種半離線回分式臭氧水處理系 統。 【發明背景】 一、月吕 · 在許多產業之製程或冷房之冷卻水,經常使用冷卻水 塔與大氣作散熱交換,以便將設備内所交換後之高溫水回 流,冷卻後再循環使用,若因水質劣化時,則作部份排放 ,其間因吸熱蒸發及冷卻水塔運作時亦有部份水損失,這 些循環水量之減少,則另以潔淨之水補充之,如此構成一 冷卻循環之流程。 冷卻水塔循環水在長期運作下,除上述水量平衡問題 以外,尚有水質產生質變之問題,由於冷卻水塔係利用大 氣作熱交換,因此循環水系統在此段必須為開放型態,並 非完全密閉系統,在開放流程段區間,便會有許多問題產 生,一般常見者有: (1) 因熱交換使循環水中酸性物質氣化流出,導致循 環水之pH值上升。 (2) 水份蒸發,循環水中雜質累積,濃度增加,明顯 之水質變化,如離子濃度、電導度濃度及固體濃度上升, 這些對冷卻系統會造成水垢、鍋垢或附著物。 (3 )微生物在冷卻水塔中,因有外來食物源、營養源 及充分溶氧,便容易滋生成長,甚至於因日照充分而有藻452640 V. Description of the Invention (1) [Field of the Invention] The present invention relates to a treatment system for circulating water in a cooling water tower using ozone as a disinfectant, and more particularly, to a semi-offline return-type ozone water treatment system. [Background of the Invention] 1. Yuelu · In many industries, the cooling water of the process or cold room often uses a cooling water tower to exchange heat with the atmosphere to return the high-temperature water exchanged in the equipment and recycle it after cooling. When the water quality deteriorates, it will be partially discharged. During the period, some water will be lost due to heat absorption and evaporation and the cooling water tower operation. The reduction of these circulating water quantities will be supplemented with clean water, which will form a cooling cycle process. In the long-term operation of circulating water of cooling water towers, in addition to the above-mentioned water balance problem, there is still a problem of qualitative changes in water quality. Since the cooling water tower system uses the atmosphere for heat exchange, the circulating water system must be open in this section and not completely closed. In the system, there will be many problems in the open process section. The common ones are: (1) The acidity of the circulating water is caused by the heat exchange, which causes the pH value of the circulating water to rise. (2) Evaporation of water, accumulation of impurities in the circulating water, increase in concentration, and obvious changes in water quality, such as increase in ion concentration, conductivity concentration, and solid concentration, which will cause scale, scale, or deposits on the cooling system. (3) In the cooling water tower, microorganisms are prone to growth due to foreign food sources, nutrition sources and sufficient dissolved oxygen, and even algae due to sufficient sunlight
第4頁 452640 五、發明說明(2) 類、原生動物及蚊蠅滋生,這些生物之殘骸一旦流入循環 系統内,常形成障礙、阻塞或附著、沈積之問題。 (4)水塔内微生物群中,若有病媒細菌存在,則會在 冷卻水塔之熱交換過程附大氣溢出飛散,造成危害,知名 度甚高之「退伍軍人症」便是其中之例。 基於這些原因,冷卻水塔之運作,必須另作殺菌、滅 藻等例行作業,以往以使用價位低廉,效果良好之氯氣作 為消毒劑,但近年來因氣素會與有機物結合,形成致癌之 毒性物質,在許多先進國家及生活水平較高之地區已禁止 使用,WHO (世界衛生組織)亦全面呼籲停用,改用其他替 代性藥劑,例如NaOC 1 (次氯酸鈉),但除消毒效果大幅降 低以外,尚有溶解後所產生Na +、C 1及電解質增加等負面 效應。最近有些系統導入以0處理之方式效能良好,但因 〇是一會自行分解之氣體,其操作成本仍然偏高,而在冷 卻循環水之高水溫、高pH值與大流量等操作條件下,利用 率更低,目前因0具有自行分解作用,無法殘留,注入方 式為連續注入流程中,致使0處理總成本仍然居高不下, 而臭氧所具有之高腐蝕性與毒性,更易為使用者所質疑, 以致實際應用上僅限於特別條件用途之少數,無法普及化 ,因此研發一種低成本、高利用率之有效0處理,是值得 探討之課題。 二、冷卻水塔方式之循環水流程分析 使用冷卻水塔作散熱裝置之冷卻循環水流程,基本上 是將經過製程設備熱交換後回流之熱水,經由冷卻水塔之Page 4 452640 V. Description of the invention (2) The species, protozoa, and mosquitoes breed. Once the debris of these organisms flows into the circulation system, it often forms problems of obstacles, blockages, attachment, and deposition. (4) In the microbiome in the water tower, if the presence of vector-borne bacteria exists, it will be scattered and attached to the atmosphere during the heat exchange process of the cooling tower, causing harm. The well-known "Veterans' Disease" is one of them. For these reasons, the operation of cooling water towers requires additional routine operations such as sterilization and algae killing. In the past, chlorine gas, which has a low price and good effect, was used as a disinfectant. However, in recent years, gas has been combined with organic substances to form carcinogenic toxicity. Substances have been banned in many advanced countries and areas with higher living standards. WHO (World Health Organization) has also urged to stop using other alternative agents, such as NaOC 1 (sodium hypochlorite), but in addition to the significant reduction in disinfection effect There are still negative effects such as Na +, C 1 and electrolyte increase after dissolution. Recently, some systems have introduced the 0 treatment method with good performance, but because 0 is a gas that will decompose on its own, its operating cost is still high, and under the operating conditions of high circulating temperature, high pH and large flow of cooling water, etc. The utilization rate is lower. At present, 0 has a self-decomposition effect and cannot be left. The injection method is a continuous injection process, so that the total cost of 0 treatment is still high. The high corrosiveness and toxicity of ozone are easier for users. It is questioned, so that the practical application is limited to a small number of special conditions and cannot be popularized. Therefore, the development of an effective treatment with low cost and high utilization rate is a topic worthy of discussion. Second, the analysis of the circulating water flow of the cooling water tower method The cooling circulating water flow using the cooling water tower as a heat sink is basically the hot water that is returned after heat exchange through the process equipment and passes through the cooling water tower.
第5頁 452640 五、發明說明¢3) 散水及與大氣對流進行熱交換,由空氣將熱能帶出,被氣 體所冷卻之水,則在匯集過濾後,經由加壓抽水機送入製 程再作冷卻使用,如此構成一連續性之循環流程。 在主要循環流程以外,因為水溫上升之蒸發與大氣挾 帶而有水份之損失,因蒸發水份而使水中含有成分之濃縮 ,以及外來物質之累積,導致水質劣化,必須加以排放及 稀釋,如此必須有潔淨之外水加以補充,這些排放水與補 充水之輔助措施,亦成為循環流程中不可或缺之一部份。 由循環系統外介入之污雜物,水中所生成之微生物, 以及在氧化與高溫下反應生成物,因累積集結成為較大粒 徑之固形物,會在循環流路中沈降、附著,形成水垢、壁 垢而妨礙或阻塞循環流路,降低熱交換效率,因此一般常 用過濾以移除這些固形物。 另外,因溫度上升而使水質中之pH值上升,電解質因 溫度而形成結垢(SCALE),微生物滋生而影響衛生等,通 常有添加中和劑、抑止劑及消毒劑等加藥裝置。 在冷卻水塔中,由頂部流入之連續性回流水,係經過 冷卻水塔分流散水,形成水滴,而以自由落體方式往下掉 落,在掉落之行程空間中導入大氣,與水滴進行熱交換, 而升溫之氣體則流出水塔外,散發於空氣中,下落之水滴 經收集後加壓,再以連續性之壓力流送入製程熱交換裝置 ,作為冷卻之用,在此特別須注意者,乃是冷卻水塔區段 中之水體並非連續水體,其作用與連續流路有所差異" 就冷卻水塔之特性而言,其實與一般以散水方式之反Page 5 452640 V. Description of the invention ¢ 3) Dispersed water and heat exchange with the atmosphere, the heat energy is taken out by the air, and the water cooled by the gas is collected and filtered, and then sent to the process through a pressurized pumping machine for cooling Use, so constitute a continuous cycle process. Outside of the main circulation process, there is water loss due to evaporation of rising water temperature and atmospheric carryover. Concentration of components contained in water due to evaporation of water and accumulation of foreign substances cause water quality degradation, which must be discharged and diluted. Therefore, it must be supplemented by clean water, and these auxiliary measures of discharge and make-up water have also become an integral part of the circulation process. Dirt and debris intervening outside the circulation system, microorganisms generated in the water, and reaction products formed under oxidation and high temperature, will accumulate and become solids with larger particle sizes, which will settle and adhere in the circulation flow path to form scale. Fouling and fouling can hinder or block the circulation flow path and reduce the heat exchange efficiency. Therefore, filtration is generally used to remove these solids. In addition, due to temperature rise, the pH value in water quality rises, electrolyte scale (SCALE) is formed due to temperature, and the growth of microorganisms affects hygiene. Generally, there are medicating devices such as neutralizers, inhibitors and disinfectants. In the cooling water tower, the continuous return water flowing from the top is divided by the cooling water tower to disperse the scattered water to form water droplets, and it drops down in a free-fall manner. The atmosphere is introduced into the travel space of the drop to exchange heat with the water droplets. The warmed gas flows out of the water tower and is distributed in the air. The falling water droplets are collected and pressurized, and then sent to the process heat exchange device for continuous pressure flow for cooling. It is that the water body in the cooling water tower section is not a continuous water body, and its role is different from that of a continuous flow path. As far as the characteristics of the cooling water tower are concerned, it is actually contrary to the general method of scattered water.
第6頁 452640 五、發明說明(4) 應裝置較為相近,如洗 之水理類似,僅其目的 冷卻水塔處理時,必須 冷卻水塔與大氣進 有外物介入、氣流挾帶 、污雜物及微生物、細 度、溶解所產生之物理 下,便會形成諸多不利 以化解。 微生物在水中,因 源之提供很容易滋長, 些微生物群在水塔内流 化之懸浮物,主要利用 生物膜方式棲居,理論 生物濾床),但因接觸 集結形成大塊體,在脫 礙物質,因此一向成為 在連續性注入消毒 存而喪失生物膜淨化處 可看出其有限之淨化能 中,增多介質之接觸表 三、0處理方式之探討 1 . 0炙特性 臭氧應用於水處理 蔣:器(S T R I P P E R )、滴濾.床或接觸床 用途為熱交換而有所分別。故在作 考量其水理作用。 行熱交換,必須為開放式,因而會 物等進入循環系統中,例如:土砂 菌等,這些物質在水中因流力、溫 、化學及生化反應,在長時間運作 之問題1因此在運作上必須適時加 有營養源、食物源、氧氣及曰光能 尤其在冷卻水塔之適合環境中,這 程,並非受到連續水體而成為流體 冷卻水塔中之構造物為介質,生成 上這些生物膜有利於水質之淨化( 表面積不大,成果有限,且因累積 落介質後進入冷卻製程中,形成障 運作上之麻煩製造者。 殺菌劑之方式中,因微生物無法生 理之作用,在批次加藥殺菌時,便 力,因此如果能在冷卻水塔之環境 面積,則可使生化處理作用提升。 已有多年之歷史,主要基於下列特Page 6 452640 V. Description of the invention (4) The devices should be similar. If the water treatment is similar, the cooling water tower is only used for the purpose of cooling water tower. The cooling water tower must be exposed to the atmosphere, foreign matter, air flow, dirt and debris. Under the physics of microbe, fineness and dissolution, many disadvantages will be formed to resolve. Microorganisms in the water, because of the source, it is easy to grow. The suspended matter that these microbiota fluidize in the water tower mainly uses the biofilm method to inhabit, theoretic biological filter bed. Therefore, it has always become a place where continuous injection of sterilization and loss of biofilm purification can be seen in its limited purification energy. Increasing the contact of the medium. Table III. Discussion of the treatment methods 1.0. Characteristics of ozone applied to water treatment : The device (STRIPPER), trickle filter, bed or contact bed uses are different for heat exchange. Therefore, its hydrological effect is being considered. For heat exchange, it must be open, so meeting things and other materials enter the circulation system, such as soil sand bacteria, etc. These substances in the water due to fluid force, temperature, chemical and biochemical reactions, the problem of long-term operation1 is therefore in operation Nutrient sources, food sources, oxygen and light energy must be added in a timely manner. Especially in the suitable environment of the cooling water tower, this process does not receive continuous water and becomes the structure in the fluid cooling water tower as a medium. The formation of these biofilms is beneficial Purification of water quality (Small surface area, limited results, and the trouble caused by the barrier operation due to the accumulation of falling media into the cooling process. In the way of bactericides, because microorganisms cannot physiologically function, sterilization is added in batches. Time, it is convenient, so if it can be in the environmental area of the cooling water tower, the biochemical treatment effect can be enhanced. It has a history of many years, mainly based on the following characteristics
第7頁 452640 五、發明說明(5) 點: (1 )殺菌滅藻能力極強,在達到必要濃度時,其劑量 約為氣氣之千分之一,殺菌時間僅在數秒間便可 達到不活化性化9 9 . 9 %。 (2)脫色、脫臭能力很高,可分解多種高分子物質及 降解COD。 (3 )反應機制為統括反應,不必因用途對象而分別處 理。 。泥 物污 產生 副產 應少 反減 之, 害水 有或 生體 伴氣 不為 亦成 1 多 性大 害質 毒物 留之 殘後 具應 不反 XI/ 4 5 XIV Γν ?--ίϊ 處 續 後 之 泥 污 於 利 性 水 脫 及 性 降 沈 泥 污 。 善 量改 2 .冷卻循環水用0處理之困難 基本上0洞於冷卻循環水流程,亦可以收到上述效果 ,但實際上由於冷卻循環水原為閉路系統,卻間夾一 區段之開放系統,因此所得效益降低,且0處理對冷 卻循環水有下列問題存在: (1 )冷卻水循環流量很大,達到必要之0濃度所須產 生0漆量很大。 (2 ) 0產生成本仍然偏高,連續注入運轉費很高。 (3 ) 0有自行分解之特性,過剩量無法在循環系統中 再利用^ (4 ) 0氨體有溶解反應所需之時間,而自行分解量亦Page 7 452640 V. Description of the invention (5) Points: (1) The ability to kill algae is extremely strong. When the necessary concentration is reached, the dose is about one-thousandth of the gas, and the sterilization time can be achieved in only a few seconds. Inactivation 99.9%. (2) High decoloring and deodorizing ability, it can decompose many kinds of high molecular substances and degrade COD. (3) The reaction mechanism is a unified reaction, and it is not necessary to deal with it separately for the purpose of use. . The by-products produced by mud pollution should be reduced, and the harmful water or the living body's associated air should not be reduced. After the residue of the poisonous poisonous substance is left, it should not be reversed. XI / 4 5 XIV Γν?-Ίϊ Subsequent mud sludge is beneficial for water removal and sludge reduction. Good quantity change 2. The difficulty of treating cooling circulating water with 0 is basically 0 holes in the cooling circulating water flow, and the above effect can also be obtained, but in fact, because the cooling circulating water is originally a closed circuit system, an open system of a section is sandwiched in between. Therefore, the benefits obtained are reduced, and zero treatment has the following problems with the cooling circulating water: (1) The cooling water circulating flow is very large, and the amount of 0 paint required to reach the necessary 0 concentration is large. (2) The production cost is still high, and the continuous injection operation cost is high. (3) 0 has the characteristic of self-decomposition, and the excess amount cannot be reused in the circulation system ^ (4) 0 the ammonia body has the time required for the dissolution reaction, and the self-decomposed amount is also
第8頁 五、發明說明(6) 隨時間而增加,如何掌握時效以提升利用率成為 重要之關鍵。 (5 )冷卻循環水之水溫、ρ Η值,加速0 3自行分解速度 ,皆可能減低0有效之利用率。 3 . 0痒入方式 目前0择入冷卻循環水中反應,仍以氣相進入液相之 方式為主,但因在液體中之氣泡會上升至液表溢散而 失效,以及注入點之0氨壓必須能克服液體之背壓等 限制,使得實際上氣液接觸,僅在0森泡由底部上升 至液表之時間及行程内,才有接觸反應作用,故其效 果有限,目前注入方式有二種: (1 )連續注入方式 可以採用較低之濃度0. 3mg/ 1〜1. Omg/ 1連續注入 ,其優點為產生Ο Θ裝置容量較小,及可隨時抑 止問題之發生,缺點為每日注入量很大。 (2)批次注入方式 每天約二次,每次1 5分鐘,濃度約在1. 0mg/ I左 右,其優點為運轉費用較低,缺點為產生03之裝 置容量大,暖機時間浪費之動力多。 4. 0夂注入點 Ο A注入點主要之考量有在(a )回流水進入冷卻水塔 之前、(b )冷卻水塔後匯集水輸送至製程之前、(c )冷 卻水塔底槽處作部份循環水注入,兹加以分析如後, 至於從冷卻塔中非連續流體注入,或製程冷卻系統中Page 8 V. Description of the invention (6) As time increases, how to master the time limit to improve the utilization rate becomes an important key. (5) The water temperature and ρ Η value of the cooling circulating water can accelerate the self-decomposition rate of 0 3, which may reduce the effective utilization rate of 0. 3.0 Itching method At present, the reaction is selected in the cooling circulating water, and the gas phase enters the liquid phase, but it will fail because the bubbles in the liquid will rise to the surface of the liquid, and it will fail at the injection point. The pressure must be able to overcome the limitation of the back pressure of the liquid, so that the gas-liquid contact actually has a contact reaction effect only within the time and stroke of the 0 sen bubble rising from the bottom to the liquid surface, so its effect is limited. Two types: (1) Continuous injection can use a lower concentration of 0.3mg / 1 ~ 1. Omg / 1 continuous injection, which has the advantages of producing 0 Θ smaller device capacity, and can stop the problem at any time, the disadvantage is Daily injections are large. (2) The batch injection method is about twice a day, 15 minutes each time, and the concentration is about 1.0 mg / I, which has the advantage of lower operating costs, the disadvantage is that the capacity of the device generating 03 is large, and the warm-up time is wasted. More motivation. 4. 0 夂 injection point 0 The main considerations of the A injection point are (a) before the return water enters the cooling water tower, (b) after the cooling water tower collects the water and sends it to the process, and (c) the cooling water tower bottom tank is partially circulated. Water injection, which will be analyzed later, as for discontinuous fluid injection from cooling towers, or process cooling systems
-4 5 2 6 4 0 五、發明說明(7) 注入,則因效用不佳,不被考量。 (1 )回流水中注入 回流水注入0 3可以對冷卻水塔中進行處理,使因 冷卻水塔所產生之問題得到因應,是為較有效之 注入位置,但因回流水之水溫、pH值均高,使無 效自行分解率增加,必須採用較多之0 3,目前鮮 有成功之案例。 (2 )冷卻水塔底槽中注入 由於其為連續性流體,混合反應效果較佳,且水 溫、pH值較回流水為低,因此可保有較好之利用 率,但在循環時間較長,或製程熱交換裝置為高 溫時,水中溶存0 3可能迅速分解而失效,冷卻水 塔内部之處理亦難有效維持,因而此一注入點漸 不被採用,或僅限少數條件吻合之處採用。 (3 )在冷卻水塔底槽處,作部份循環水注入〇 3 此法係以游泳池0處理之觀念而加以應用,亦即 由底槽中抽入部份水量,作為加入旁路,具 有溶存水,再回流入底槽中,由於操作簡單 ,技術為習知,故雖然效果尚有限,但目前大多 數以此種方式為主。 5.對0處理冷卻循環水之阻力與質疑 雖然在學理及實驗室中對於使用0拃為冷卻循環水之 處理,在0夂特性與效果方面均給於相當高之評價, 但在實務應用上,目前在技術面及經濟面仍然存在著-4 5 2 6 4 0 V. Description of the invention (7) Injection is not considered because of poor utility. (1) Injecting reflux water into the reflux water can be treated in the cooling water tower, so that the problems caused by the cooling water tower can be dealt with. It is a more effective injection location, but the temperature and pH of the return water are high. In order to increase the invalid self-decomposition rate, more 0 3 must be used. At present, there are few successful cases. (2) Injected into the bottom tank of the cooling water tower. Because it is a continuous fluid, the mixing reaction effect is better, and the water temperature and pH value are lower than the reflux water, so it can maintain a good utilization rate, but the cycle time is longer. When the process heat exchange device is at a high temperature, the dissolved 0 3 in the water may quickly decompose and fail, and the internal treatment of the cooling water tower is also difficult to maintain effectively. Therefore, this injection point is gradually not used, or it is used only in a few conditions. (3) Part of circulating water is injected at the bottom tank of the cooling water tower. This method is applied with the concept of 0 treatment in the swimming pool, that is, part of the water is pumped from the bottom tank as a bypass, which has storage. Water flows back into the bottom tank. Because the operation is simple and the technology is well-known, although the effect is still limited, most of them are mainly in this way. 5. Resistance and questioning of 0 cooling cooling water treatment Although the use of 0% cooling cooling water treatment in science and laboratory has been given a high evaluation in terms of 0% characteristics and effects, but in practical applications , Still exists in the technical and economic aspects
第10頁 五、發明說明(8) 很大之阻力與質疑,其關鍵在於〇 3自行分解之特性與 時效之掌握’以及對〇極強氧化力所形成之腐蝕性及 毒害性產生質疑,茲擇一般要項略作分析: (I ) 0 A注入量 0及應所需之理論值與實務上差距太大,此乃是 基於0在溶解接觸、反應之過程中受到自行分解 ’而成為低效之〇 2’使有效〇利用之比例偏低, 因此成本很高,然而若以改善流程參數或操作條 件以提高0利用率之方式,所須付出之代價更為 可觀’因此實際有效之〇利用率不及注入量半數 ’亦即實務應用之0盪常較學理高以倍計。 (2 ) 0痒入率之操控 〇 A反應需要量一般可以推估,即使有變數存在 之水處理流程’但實際上流程參數及操作條件, 不僅影響〇炙溶解、接觸、反應率,同時亦對自 行分解率亦會有重大影響’故在理論推估〇表注 入量時,一旦流程參數及操作條件有變化時,則 0疯效反應比率便會巨幅變化。而實務上要對這 些變數(包括時間因子)能夠充分掌握者並非容易 ,過量之〇添加’不僅增加處理成本,且有腐蝕 與毒害之問題產生。 (3)對〇展應衍生效應之質疑 向來水處理所使用之藥劑,未有如〇般極強之氧 化力,以及僅有之自行分解特質,因此在反應過Page 10 V. Description of the invention (8) A lot of resistance and doubt, the key lies in the mastery of the self-decomposition characteristics and aging 'and the question of the corrosiveness and toxicity caused by the strong oxidizing power. Select general items for analysis: (I) 0 A injection amount 0 and the theoretical value required should be too far from the actual value. This is based on the fact that 0 is self-decomposed in the process of dissolution, contact and reaction, and becomes inefficient. 〇2 'makes the ratio of effective 〇 utilization low, so the cost is high, but if you improve the process parameters or operating conditions to increase the utilization rate of 0, the price to be paid is more considerable' 'so practical 〇 utilization The rate is less than half of the injection volume, that is, the zero swing of practical applications is often multiples of science. (2) Control of 0 itching rate. The reaction demand of A can generally be estimated. Even if there are variables in the water treatment process, the actual process parameters and operating conditions not only affect the solubility, contact, and reaction rate, but also It will also have a significant impact on the self-decomposition rate. Therefore, when theoretically estimating the injection amount of the table, once the process parameters and operating conditions have changed, the response rate of the crazy response will change greatly. In practice, it is not easy for those who can fully grasp these variables (including the time factor). Adding an excessive amount of ’not only increases the processing cost, but also causes problems of corrosion and poisoning. (3) Questions about the effect of the derivation of 〇Zan. The chemicals used in water treatment have not been as strong as oxidizing power and have only the characteristics of self-decomposition.
4 ο 2 6 4 Ο 五、發明說明(9) 程中,可能遭遇之問題便紛紛出籠,例如排放氣 體中0威分溶存水_ 0戒分,反應伴生氣體及反 應後生成物等對設備及人體可能造成之腐蝕性與 毒害性,以及既有設備、流程條件等是否可以適 用等質疑,這些認知基本上是存在的,但在技術 面若無法妥善克服,疑慮成為採行上之一大阻力 〇 四、現行冷卻水塔循環水採用0處理方法之探討 0用於冷卻水塔之循環水處理已有十餘年歷史,至19 9 5年美國才約3 0 0 - 5 0 0個廠使用。本來之用途目的是著眼 於殺菌、滅藻,以替代化學葯品(包括氯氣等),故傳統設 計使用0處理時,注加方法亦沿習傳統,在冷卻水塔之底 槽,取部份水作為溶解氣體0齐式,再以溶存0水回流冷 卻水塔之底槽,此種方法不僅大幅降低0象功能與作用, 同時亦減少循環水之處理效益,另一方面亦對冷卻水處理 流程作很多限制。 從過去報導中曾經指出,0用於冷卻水塔水處理,固 然有很多成功案例,同時亦有不少失敗之案例,在失敗之 案例中,製造廠或供應商常歸咎於設計上不妥當,及0發 生裝置之品質不佳,事實在經過最近一段時間之產品改良 及技術經驗累積,理應可化解以往所存在之缺失。但很不 幸地,由於傳統應用技術上有其盲點無法突破,以致於實 務上未能廣泛地被運用。即使以目前廠商、供應商、使用 者等所認為是成功之案例,若加以分析評估,仍然可明顯4 ο 2 6 4 Ο V. Description of the invention (9) During the process, problems that may be encountered will come out one after another, such as 0 watts of dissolved water in the exhaust gas _ 0 ring points, reaction associated gases and reaction products, etc. on the equipment and The human body may be corrosive and toxic, and the existing equipment and process conditions are applicable. These cognitions basically exist, but if the technical aspects cannot be properly overcome, doubts become a major resistance to adoption. Ⅳ. Discussion on the current treatment method of circulating water in cooling water towers. 0 The circulating water treatment for cooling water towers has more than ten years of history. It was only used by about 300 to 500 plants in the United States in 195. The original purpose is to focus on sterilization and algae replacement to replace chemicals (including chlorine gas, etc.), so when the traditional design uses 0 treatment, the filling method also follows the tradition. In the bottom tank of the cooling water tower, take part of the water as the Dissolved gas is homogeneous, and then dissolves 0 water back to the bottom tank of the cooling water tower. This method not only greatly reduces the function and effect of 0 images, but also reduces the treatment efficiency of circulating water. On the other hand, it also makes a lot of cooling water treatment processes. limit. From previous reports, it has been pointed out that although 0 is used for cooling water tower water treatment, there are many successful cases, and there are also many failure cases. In the failure cases, the manufacturer or supplier often blame the poor design, and 0 The quality of the occurrence device is not good. The fact that after recent product improvement and technical experience accumulation, it should be able to resolve the existing deficiencies. Unfortunately, due to its blind spots in traditional application technology, which cannot be broken, it has not been widely used in practice. Even if the current cases considered by manufacturers, suppliers, users, etc. are successful, if they are analyzed and evaluated, it will still be obvious.
第12頁 452640 五、發明說明G〇) 地看出,◦棘能僅有極小部被利用,雖然其投資報酬率已 很不錯,嚴格來說很難稱得上達到「成功」位階,亦即尚 有極大之應用空間可待研發。 將冷卻水當做一般循ί衷用水處理,而進行〇處理, 基本上並不妥適,儘管循環流程外貌大抵近似,然而其反 應機制,則有顯著之差別存在,而將〇 3當成化學藥品之替 代劑,更是扼殺0之優點而突顯其短處。兩者之間應如何 配合協調,以便發揮最大功能,就必須從〇社入之方法及 流程重新加以檢討。現行冷卻水塔以0處理之流程,如第 1 圖所示,其資料來源:FEDERAL TECHNOLOGY ALERTS, OZONE TREATMENT FOR COOLING TOWERS。 1 . 0處理法在實務上之限制: 以傳統方法進行冷卻水塔循環水處理,迄今所公認為 之問題與限制,大約有下列幾項: A.循環水流程 C 1 )水溫不可過高,可能的話低於丨0 0下以下。 (2 )循環水p Η值愈低愈好β (3) 有機物或無機物之可與〇衣應物(C0D)含量低 〇 (4) 水中之硬度、S. S.含量低。 (5 )每次循環時間不能太長(1 〇分鐘以内)。 (6) 處理流量不宜太大(1〇〇〇〇加侖下)。 (7) 水塔容量及系統水量不宜過大β (8 )水塔附近空氣品質必須良好清潔。Page 12 452640 V. Description of the invention G) It can be seen that only a small part of the spine energy is used. Although its return on investment is already very good, it is difficult to qualify as the "success" level, that is, There is still a lot of application space to be developed. Treating cooling water as a general purpose water treatment and performing 0 treatment is basically not appropriate. Although the appearance of the circulation process is almost similar, there are significant differences in the reaction mechanism, and 0 3 is regarded as a chemical drug. Substitute agents are even more strangling the advantages of 0 and highlight their weaknesses. How to coordinate and coordinate the two in order to make the most of their functions, we must review the methods and procedures of the company. The current process of cooling water towers treated with 0, as shown in Figure 1, its data source: FEDERAL TECHNOLOGY ALERTS, OZONE TREATMENT FOR COOLING TOWERS. 1.0 The practical limitation of the treatment method: The conventional method of circulating water treatment of cooling water towers, the problems and limitations that have been recognized so far include the following: A. Circulating water flow C 1) The water temperature must not be too high, If possible, it is lower than 丨 0 0 and below. (2) The lower the p Η value of the circulating water, the better β (3) The content of organic or inorganic matter that can be compatible with the product is low. (4) The hardness in water and the content of S. S. are low. (5) The cycle time cannot be too long (less than 10 minutes). (6) The processing flow should not be too large (under 10,000 gallons). (7) The water tower capacity and system water volume should not be too large. Β (8) The air quality near the water tower must be clean.
第丨3頁 452640 五、發明說明(π) Β . 0瘩解與反應 (1 )氣態0痒解於水中,必須有合適之操作條件。 (2) 在溶存0與循環水進行接觸反應前,應保持足 夠之濃度。 (3) 循環水回流熱水至冷卻水塔頂部時,須有足夠 殘留0濃度,才能對冷卻水塔内,進行殺菌、 滅藻、除污等作完全處理。 (4) 須有合適之0添加率(注入率),避免過量與不 足。 (5 ) 0 3自行分解率宜降至最低。 C.其他要求 U )補充水之水質要很乾淨、低溫、低pH值。 (2 )濃度周期要愈大愈好。 (3)對管路、構造物不宜造成腐蝕現象。 (4 )不希望有結垢現象發生。 (5 )對人體之危害性減至最低。 (6 )排放水之水量少、水質改善、不含有害或毒性 物質,減少對環境之衝擊。 (7 )儘可能減少操作維護所需之人力、動力。 (8 )既有流程缺失須先改善,以配合0获用之需要 〇 2 .腐蝕與結垢現象 2. 1腐蝕 在一般觀念中是物質、材料之表面,在某些作用或反Page 丨 3 452640 V. Explanation of the invention (π) Β. 0 瘩 解 和 反应 (1) Gaseous 0 itchy solution in water, there must be appropriate operating conditions. (2) Sufficient concentration should be maintained before the contact between dissolved 0 and circulating water. (3) When circulating water returns to hot water to the top of the cooling water tower, there must be enough residual 0 concentration to complete the treatment of the cooling water tower for sterilization, algae killing and decontamination. (4) There must be a proper 0 addition rate (injection rate) to avoid excessive and insufficient. (5) The self-decomposition rate should be minimized. C. Other requirements U) The quality of the make-up water should be clean, low temperature and low pH. (2) The larger the concentration period, the better. (3) Corrosion should not be caused to pipelines and structures. (4) No scaling is desired. (5) The harm to human body is minimized. (6) The amount of discharged water is small, the water quality is improved, and no harmful or toxic substances are contained, which reduces the impact on the environment. (7) Minimize the manpower and power required for operation and maintenance. (8) The lack of existing processes must be improved to meet the needs of 0. 〇 2. Corrosion and scaling phenomenon 2.1 Corrosion is the surface of matter and materials in general concepts, and in some functions or anti-
第14頁 452640 五'發明說明(12) 應下,逐漸被侵損或劣化之統稱。雖然反應機制有所 差異,但對物質、材料而言,大多為負面效應。(除 一些特別用途以外)。首先就其發生之原因,略分述 如下: (1 )沖蝕:受流力之摩擦作用,而產生之侵蝕,一般 流體或流體化物質均可能產生。例如水力 沖刷、氣流喷射等。 (2)磨蝕:是固體與固體間作緊密之相對運動時,因 摩擦而產生之表面粍損。例如磨刀、砂磨 等均是。 (3 )溶蝕:物體在某些具溶解性或反應性溶液中,接 觸面先受到作用而溶解。例如在酸液、鹹 液或其他溶劑中均會產生。 (4 )鏽蝕:物體表面因受到反應條件而變質、劣化或 脫離,例如各種金屬之生鏽,一般多為氧 化還原作用所造成。 (5) 腐蝕:因微生物在物源、材料上棲居,以該材料 作為食物源或營養基。而造成材料之耗損 或劣化。例如嗜鐵、嗜磷、嗜硫、嗜氮菌 類,以及各種微生物。 (6) 電解:因電子之移動,而使表面離子化分離或集 結。例如電解、電鍍、陰極防蝕或電化學 反應。 請注意一般流程上可能有複數作用共生,所以很Page 14 452640 Description of the Five 'Inventions (12) It should be collectively referred to as being gradually damaged or deteriorated. Although the reaction mechanisms are different, most of them have negative effects on substances and materials. (Except for some special uses). First of all, the reasons for its occurrence are briefly described as follows: (1) Erosion: The erosion caused by the friction of the fluid force may be generated by ordinary fluids or fluidized substances. Such as hydraulic flushing, air jet, etc. (2) Abrasion: It is the surface damage caused by friction when solid and solid are in close relative motion. For example, sharpening, sanding, etc. are all. (3) Dissolution: In certain soluble or reactive solutions, the contact surface is first affected and dissolved. For example, it can be produced in acid, salt or other solvents. (4) Corrosion: The surface of the object is deteriorated, deteriorated or detached due to the reaction conditions. For example, the rust of various metals is generally caused by oxidation reduction. (5) Corrosion: Because microorganisms inhabit material sources and materials, this material is used as a food source or nutrient base. As a result, the material is worn or deteriorated. Examples include ironophilic, phosphorophilic, sulfurophilic, nitrobacteria, and various microorganisms. (6) Electrolysis: The surface is ionized and separated or aggregated due to the movement of electrons. Examples include electrolysis, electroplating, cathodic corrosion prevention, or electrochemical reactions. Please note that there may be multiple interactions in the general process, so it is very
第15頁 4 5 2 6 4 0 方面腐蝕之程度 成之結果。格言 重視以外,時間 常見之除鏽利用 水刀切割、印刷 應均須作時間上 雜質,通稱與人 、包被(coating 造成一些不必要 經常在流程中成 ,主要可分為下 五、發明說明(13) 難明確區分是何種原因 ,係由腐蝕作用能力大 所稱滴水能穿石,故除 因素亦不可忽略。 腐蝕用於正面效用 酸洗、除垢之鹹洗以及 電路板之蝕刻等均是, 之控制,以免過度侵蝕 2. 2結垢 結垢是在固形物上積存 為蓄意添加之保護層不 )、披覆(1 i nn i ng)有所 之麻煩’因而防制結垢 為必要之處理,產生結 列數種: (1 )礦物性固體微粒之 (2 )溶解性固體在某些 (3 )物質與構造物產生 (4 )微生物以構造物為 所形成。 (5) 固體微粒藉由生物 (6) 凡得爾電位(van 積。 (7 )具有膠黏性物質或 所形成,另一 小與時間所形 對腐蝕能力須 者亦有,例如 喷砂、防鏽、 但這些正面效 造成損害。 一層非期待之 同。例如電鑛 差異。結垢常 或除垢程序, 垢之原因很多 附著、累積。 條件下之溶出附著。 反應後結合。 基質(介質)棲居,及殘骸累積 膠泥為膠著劑,產生結層化。 der waals),對粒子之吸引累 溶劑存在而產生結合。P.15 4 5 2 6 4 0 The degree of corrosion is the result. In addition to the motto's emphasis, the time-consuming rust removal using waterjet cutting and printing should be made impurities in time, commonly known as people, coating (some coatings caused by unnecessary unnecessary often in the process, mainly divided into the next five, description of the invention (13) It is difficult to clearly distinguish the reason. The reason is that the dripping water can penetrate the stone because of its great corrosion effect, so the factors can not be ignored. Corrosion is used for positive effect acid pickling, descaling salt washing, and circuit board etching etc. Both are controlled to prevent excessive erosion. 2.2 Fouling Fouling is the accumulation of a protective layer intentionally added on the solids), and the coating (1 i nn i ng) is troublesome, thus preventing fouling For the necessary treatment, there are several types of knots: (1) mineral solid particles (2) soluble solids are produced in certain (3) substances and structures (4) microorganisms are formed by structures. (5) Solid particles are generated by biological (6) van der potential (van product.) (7) It has a sticky substance or is formed, and another small and time-shaped corrosive ability must also be available, such as sandblasting, Anti-rust, but these positive effects cause damage. One layer is not the same as expected. For example, the difference in electricity and minerals. Scale often or descaling procedures, scale causes a lot of adhesion and accumulation. Dissolution and adhesion under conditions. Combination after reaction. Substrate (medium ) Dwelling, and the debris accumulated in the cement as a glue, resulting in stratification. Der waals), the attraction of particles and the existence of a solvent to bind.
第16頁 452640 五、發明說明(14) (8 )外加能源(如加熱),而使固體微粒或溶解固體釋 而附著。 針對上述結垢所發生之機制,添加合適之抑制劑 ,是有減少其形成之可能,但在很多狀況下,結垢之 成因並非單獨產生,而是可能多種混合共生。因此抑 制劑亦有其效能之限制,在經一段時期後,仍須以物 理或化學方法進行除垢,同樣地,結垢程度與結垢能 力及經過時間均有關。 2. 3腐蝕與結垢之相互關係 (1)腐蝕與結垢對於固定物而言,表面上看來為相反 作用,結垢可以減少腐蝕,腐蝕可以清除結垢, 在某些狀況是存在的。例如:除鏽用之酸洗,除 垢用之強酸或強鹹。 (2 )生物性之結垢,可能增加腐蝕作用,因其成為良 好介質及營造利於生物生長之環境,但亦加速結 垢内與介質表面間之腐蝕,例如:保持水份、養 份及固著生物膜。 (3 )結垢對物理性侵蝕提供保護作用,但不均勻之結 垢,可能導致局部加速腐餘。 (4 )許多結垢並非全面性被覆,而是具有滲透性,如 此對大多數腐蝕作用不具保護作用。 (5 )腐蝕會傷害材質,同樣地結垢亦有此可能,而結 垢所形成之壁障,更易妨礙原來之作用與效應。 (6 )生物性之腐蝕與結構,必須及早去除,否則會形Page 16 452640 V. Description of the invention (14) (8) External energy (such as heating) causes solid particles or dissolved solids to release and attach. In view of the above-mentioned mechanism of scaling, it is possible to reduce its formation by adding appropriate inhibitors. However, in many cases, the causes of scaling are not generated separately, but may be mixed and coexist. Therefore, the inhibitor also has its effectiveness limitation. After a period of time, it must still be descaled by physical or chemical methods. Similarly, the degree of scaling is related to the ability to scale and the elapsed time. 2.3 Correlation between corrosion and fouling (1) Corrosion and fouling seem to have opposite effects on the surface of fixed objects. Fouling can reduce corrosion and corrosion can remove fouling. In some conditions, it exists. . For example: pickling for rust removal, strong acid or salty for descaling. (2) Biological scaling may increase the corrosion effect, because it becomes a good medium and creates an environment conducive to biological growth, but also accelerates the corrosion in the scale and the surface of the medium, such as maintaining water, nutrients and solids. A biofilm. (3) Fouling provides protection against physical erosion, but uneven scaling may cause local accelerated corrosion. (4) Many scales are not fully covered, but are permeable, so they do not protect most corrosion effects. (5) Corrosion will damage the material, and scaling is also possible. The barrier formed by scaling is more likely to hinder the original function and effect. (6) Biological corrosion and structure must be removed as soon as possible, otherwise it will form
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_______—--------- 五、發明說明(15) 成加乘效應。 3.存在問題 目前以0祚冷卻水塔循環水處理,效果偏低之原因, 雖然報導中0拃為冷卻水塔循環處理應用之M二 ’ ^ >人月£ ,大 多為正面之肯定*但亦有不少案例指出其效益有限 價值不高’推究其成因大抵有下列數項: ^ ’ (1)既有流程條件設備及操作方式’無法適應〇 :所且 之特性,導致0 f力能無法發揮。 ' (2 )現場環境過於惡劣並具有損害性,導致無法1 〇處理設備及順利操作,經常故障。 '叹置 (3 )目前所採行〇痒加之流程方法,存在有許多缺 ,使其用法效能均受到限制^ 夕、失 (4) 設置〇敦備之期前預估考量因素不足,你杂 心 興實際( 或既有)條件狀況差距過大,而在曰後作業 又未能對各種變動給予適當之調整β μ & ’ (5) 設計單位之期前調查,數據取得未能詳實,專# 能力不足’又對日後管理運作、操作、維護欠缺 考量,導致所謂設計不當。 (6) 採購偏重於設備器材,對於技術能力、智慧KNOW HOW之程度,很少列入考量,因而僅重於有形體 物品(H a r d w a r e)之設置,卻難以得到功能技術 (software)之效果。 (7) 施工、監造者本身未具充份專業知識,造成諸多 不妥與缺失,影響正常操作及效能,並常導致故_______—--------- V. Description of the Invention (15) Multiplication effect. 3. Existing problems The current reason is that the 0 祚 cooling water tower circulating water treatment has a low effect. Although 0 拃 is reported in the cooling water tower circulating treatment application, it is mostly positive and positive * but also There are many cases that point out that its limited benefits are not high. The reason for this may be the following: ^ '(1) Existing process conditions, equipment and operating methods' cannot be adapted. Play. '(2) The on-site environment is too harsh and damaging, resulting in inability to handle the equipment and smooth operation, and often fails. 'Sigh (3) There are many shortcomings in the current method adopted. It has a lot of shortcomings, which limits its use efficiency. ^ Xi, Mi (4) Set up. The estimated considerations before the period are insufficient, you are miscellaneous. Xinxing's actual (or existing) conditions are too wide, and the subsequent operations have failed to make appropriate adjustments to various changes β μ & '(5) The pre-period survey of the design unit, the data acquisition was not detailed, special # Insufficient ability, and lack of consideration for future management operations, operations, and maintenance, leading to the so-called improper design. (6) Purchasing focuses on equipment and equipment. The degree of technical ability and wisdom of KNOW HOW is rarely considered. Therefore, it is only focused on the setting of physical items (H a r d w a r e), but it is difficult to obtain the effect of functional technology (software). (7) The construction and supervisors themselves do not have sufficient professional knowledge, causing many defects and defects, affecting normal operation and efficiency, and often causing failures.
第18頁 45264 0 五 、發明說明(16) 障和害及縮減耐用壽命。 (8)運作營柿丄 s视未能確切落實,例行作業流於形 對各種银ί & 八’而 ,η Λ . 變動未能有效地及時因應。 (9 ) 0處理η生 1 f所需之特殊環境及配合設備不足,道μ 功能縫,、, &導致 乂發揮,例如:冷卻水、原料、氣舻 ’及办% 札艘處理 Μ π ,,, 嗎環境等之提供。 (1 0 )對於 g M t 唆操作、維護、管理及作業負荷與難易 ’ 能事前通盤考量,謀求因應對策,導站,^ 、動力、故 寸双人力 4頦广η* 費用成本不合理° 現行以〇作;;問題分析 ,係依據〇ί令卻水塔水處王里’所採^流程與方法 ^ ^ 泯一般循環水,及傳統〇處理觀念了,& 提出旁路分I ^r> ,所 . 夏(side stream by pass)連鲭* ^田 水塔底槽之角〜 A處理冷卻 :倌之通裎。事實上冷卻水塔循環水與— '也、養殖油堂~ β 股游泳 數:其::於^特性更有顯著之影響,以下有藉所由差其異生 數項分析’便容易看出。 再中 (1 )以冷卻水塔之底槽為反應之場所 由底槽所構成分路溶解為〇术’再注入冷卻水塔 之底槽’原來期望在底槽中能充分混合反應,以 對冷卻循環水系統之微生物病灶’進行充分之反 應,但冷卻水塔之底槽容積通常有限,是匯流池 而非貯水池’在循環水大流责(FLOW RATE)下, 水力停留時間極其有限,若以少量之溶存〇水,Page 18 45264 0 V. Description of the invention (16) Obstacles and damages and reduced durable life. (8) The operation camp was not implemented accurately, and the routine operation flowed into shape. For various kinds of silver, and η Λ, the changes could not be effectively responded to in a timely manner. (9) Insufficient special environment and cooperating equipment required for processing η and 1 f, the functional gap of μ, and & leads to the function of 乂, such as: cooling water, raw materials, gas 舻 ', and %% Provide environment. (1 0) For g M t 唆 operation, maintenance, management, and workload and difficulty 'can be comprehensively considered beforehand, and seek for countermeasures, guidance stations, ^, power, old force 4 双人 Wide η * Expense cost is unreasonable ° The current analysis is based on 〇. The problem analysis is based on the procedures and methods adopted by Wang Li's water tower, Wangli '. ^ The general circulating water, and the traditional concept of ○ treatment, & proposed bypass points I ^ r >, So. Xia (side stream by pass) even mackerel * ^ corner of the bottom of the water tower of the water tower ~ A treatment cooling: 倌 之 通 裎. In fact, the circulating water of the cooling water tower and-'Ye, breeding oil hall ~ β-stroke swimming number: its :: Yu ^ characteristics have a more significant impact, the following reasons for the difference of its heterogeneous number of analysis' will be easy to see. (1) The bottom tank of the cooling water tower is used as a place for the reaction. The path formed by the bottom tank is dissolved into 0. 'Refill the bottom tank of the cooling water tower'. It was originally expected that the reaction could be fully mixed in the bottom tank to cool the cooling cycle. The microbial lesions of the water system 'react adequately, but the bottom tank volume of the cooling water tower is usually limited. It is a confluence pool instead of a storage tank.' Dissolved in water,
45 26 4 0 五、發明說明(π) ,是相 欲求能充分混合反應,及足夠之接觸時間 循 當困難。大部份未及在底槽内反應之〇3’便由咬 環水抽水機抽取,經冷卻水管路送入熱交換之 > >卟率備 備中’實際用於冷卻水塔底槽作用反應之 低0 (2 )溶解氣體〇象用水 , 溶解由0發生裝置所用之水,传取自於冷々45 26 4 0 V. The description of the invention (π) is the desire to fully mix the reaction and sufficient contact time to make it difficult. Most of the 03's that did not react in the bottom tank were pumped by the ring water pump and sent to the heat exchange via the cooling water pipeline. ≫ > Porosity rate in preparation 'Actually used for cooling water tower bottom tank reaction Low 0 (2) dissolved gas, like water, dissolves the water used by the 0 generator, passed from the cold head
waft vfrt ilC 之底槽水’事實上底槽中之水質,除水溢略執作 熱交換後回流水以外,(因經過冷卻水塔散”·、有 用),其他水質條件則近似或更為不利’ ( 冷卻水塔之蒸發.作用,pH值、s· S濃度、瑪。就 反應物及污雜物因水塔洗滌、濃縮而增高) 氣體〇萚解度而言是會降低,而自行分解率T, 而加速,另一方面由於溶存〇水回流炱底槽 會 並寄望能散佈而使底槽中全部能接觸反應’ 有高濃度溶存〇残留其中,這些殘留〇谏度亦影 響氣體〇夂溶解度。 (3)氣體0瘙入之方法 在目前所使用0氨體溶解方式,有散氣式 (D if fusor)、流力吸引方式(Venturi)及機械混 合方式(Jet or),其中以散氣方式效果最好,而 且可以達到高濃度,流力吸引方式效果最低,且 因受限於(LIQUID/GAS RATIO)溶解濃度被限於極 低範圍’因而溶存〇 ί農度很低’加上使用冷卻水waft vfrt ilC bottom tank water 'In fact, the quality of the water in the bottom tank, except for the return water after the water overflow is performed as a heat exchange (because it is dispersed through the cooling water tower), and other water quality conditions are similar or more unfavorable '(Evaporation of cooling water tower. Action, pH value, s · S concentration, Ma. As for reactants and contaminants increased by water tower washing and concentration) The degree of decomposition of gas will decrease, and the self-decomposition rate T Acceleration, on the other hand, due to the return of dissolved water, the bottom tank will spread and hope to spread, so that all the bottom tank can contact the reaction. There are high concentrations of dissolution. Residues, these residuals also affect the gas solubility. (3) The method of injecting gas into gas is the currently used method of dissolving ammonia. There are Dif fusor, Venturi and Jet or mechanical mixing methods. The method has the best effect, and it can achieve high concentration, and the fluid suction method has the lowest effect. Because of the limitation (LIQUID / GAS RATIO), the concentration of the solution is limited to a very low range, so the solubility is very low, and the cooling is used. water
第20頁 五、發明說明(18) 塔底槽水為溶液,水質不佳溶解度低,又易因反 應及自行分解而耗用溶存03,故注入底槽之溶存 0濃度通常很低,在最近許多實驗室及實務上証 明,同樣劑量之0高濃度時之效能較低,濃度之 效能數以倍計。故偏低之溶存0棘用降低,由於 受到流程方式之限制,目前0氟體溶入只得採用 流力吸引(Venturi)方式。 (4 ) 0處理之對象標的 在冷卻循環過程中雖為一連續性流程,但依其作 用別大抵可分為,冷卻用水之輸送、設備熱交換 之吸熱、回流熱水之輸送及_冷卻水塔之排熱等四 部份,其中除冷卻水塔為對外界開放以外,其餘 均在封閉系統中流動,因此各種外物界入、生物 滋長等,均以冷卻水塔為病灶。一般化學藥品處 理或導入0處理,亦以冷卻水塔為主要重點,尤 其使用0處理,最主要用途在殺菌、滅藻,目前 0處理方式僅注入底槽,隨後即被輸入系統而回 流熱水中,幾乎不可能有殘留0存在,故除非有 足夠高濃度之溶存0 3,能夠應付流程中反應耗損 及自行分解,否則冷卻水塔自頂部至底槽間,微 生物、病菌、生物膜等最容易滋生之處,並無法 得到0處理之效果,而會繼續掉落成為系統之固 形物負擔,這亦是現0處理冷卻水塔時候,必須 持續作0添加處理之要因。Page 20 V. Description of the invention (18) The bottom tank water is a solution, the water quality is poor, the solubility is low, and it is easy to consume the dissolved 03 due to the reaction and self-decomposition. Therefore, the concentration of the dissolved 0 injected into the bottom tank is usually very low. Many laboratories and practices have proved that the efficacy at the same dose of 0 high concentration is lower, and the efficacy of concentration is several times. Therefore, the use of low-storage 0-spins is reduced. At present, due to the limitation of the process method, the 0-fluoride dissolution can only be achieved by the flow force (Venturi) method. (4) Although the target of 0 treatment is a continuous process during the cooling cycle, it can be divided into: cooling water transportation, equipment heat exchange heat absorption, reflux hot water transportation and cooling water tower. Except for the four parts of heat removal, except that the cooling water tower is open to the outside, the rest are flowing in a closed system. Therefore, the cooling water tower is used as the focus of various foreign objects and biological growth. General chemical treatment or introduction of 0 treatment, also the main focus of cooling water tower, especially the use of 0 treatment, the most important use is in sterilization, algae killing, the current 0 treatment method is only injected into the bottom tank, and then input into the system and return to the hot water It is almost impossible to have residual 0, so unless there is a sufficiently high concentration of dissolved 0 3, which can cope with the reaction loss and self-decomposition in the process, the cooling water tower from the top to the bottom tank, microorganisms, germs, biofilms, etc. are most likely to breed. However, the effect of zero treatment cannot be obtained, and it will continue to fall into the solid burden of the system. This is also the main reason why zero addition treatment must be continued when the current zero treatment of cooling water towers.
rA3J2^JLQ_______ 五、發明說明¢19) C 5 ) 0處理之用途 以0作為冷卻水塔循環水之處理,基本上主要用 ,對象為殺死細菌、微生物及生物膜等作用’附 ▼作用對於脫色、脫臭、除垢及降解COD是伴生 效應’而對—般水處理之淨化作用’如降低硬度 、電導度、S.S.等則非其所長,且可能是干擾因 素’即使在一般水處理0所擔任之角色,亦非在 去除s. S、硬度或C0D,這些無論在技術上或經濟 上考量’大多使用其他方法處理,由於0轟統括 性反應’其氧化作用係同時發生,很難分離’故 在通常方式中,只好將其總耗用量視為系統之需 求量’然而若能以〇象特性,其溶存濃度隨時間 自^于分解而遞減,隨操作因素而改變分解速率, 對不同用途之對象物,所須之濃度及接觸時間之 差異’以及在循環流程中最適場所之選擇等,便 可使0得到合理之高利用率。 (6 )流程參數監控與0象注入率 #部水塔一般並非要求使用高度淨水之水質,而 在實務運作中除非作業時段以外,仍有日夜溫度 差、睛雨氣溫差、季節性變化、外物界入、生物 滋長及蒸發濃縮等現象,導致循環水中各種成份 ’如PH值、水溫、礦物質、固形溶解物、硬度、 生物殘骹、結垢集結物等等經常在變動,而當每 一 CYCLE 之 BLOWN DOWN、MAKE-UP水操作時,又rA3J2 ^ JLQ _______ V. Description of the invention ¢ 19) C 5) 0 Use of treatment 0 is used to treat circulating water in cooling water towers. It is mainly used for the purpose of killing bacteria, microorganisms and biofilms. 'Apply ▼ the role of decolorization , Deodorization, descaling and degradation of COD are associated effects, and the purification effect of ordinary water treatment, such as reducing hardness, conductivity, SS, etc. are not their strengths, and may be interfering factors, even in general water treatment. The role they play is not in removing s, S, hardness, or COD. These are technically or economically considered. 'Most of them are processed by other methods. Due to the zero-inclusive reaction, its oxidation occurs simultaneously and is difficult to separate.' Therefore, in the usual way, its total consumption can only be regarded as the system's demand. However, if it can be characterized by zero, its dissolved concentration will decrease with time due to decomposition, and the decomposition rate will change with operating factors. The use of the object, the required concentration and the difference in contact time 'and the choice of the most suitable place in the circulation process can make 0 a reasonable high utilization rate. (6) Process parameter monitoring and 0 Xiang injection rate # The water tower generally does not require the use of highly purified water, and in actual operation, there are still day and night temperature differences, rain temperature differences, seasonal changes, and The phenomenon of physical invasion, biological growth, and evaporation and concentration cause various components of circulating water such as PH value, water temperature, minerals, solid dissolved matter, hardness, biological residues, scale accumulations, etc., often change, and when Each BLOWN DOWN, MAKE-UP water operation of CYCLE, and
第22頁 452640 五、發明說明(20) 會引起大幅變動,這是一般循環水系統所沒有之 現象。以量測循環水中各種參數,作為注入0 # 之監視與控制,例如有些採用量ORP、pH、Tempe rature、Conductivity、殘留溶存0岸,作為控 制0砗入量之控制,實務上很難實現,這是沿襲 傳統觀念所產生之結果,同時對0 3影響極為重要 之「時間」因素,卻常被忽略,導致0 主入率常 出現過與不及之問題,迄今尚無適當之因應方法 ,然而由於循環流程有均化作用,溶存0有時效 性,故應有可簡化其操作控制之方法。 (7 )殺菌、滅藻作用 0孫解於水後形成氫氧自由基,氧化還原電位大 幅上升,殺菌、滅藻能力亦提高,在0 #理上對 於殺菌,無論其反應機制為破壞細胞膜或抑制基 因生長,均以「不活性化」一言蔽之,一般以不 活性化程度到達9 9. 9 %時,視同完全殺菌,對於 生物之不活性化,因生物對象、類別、體型而有 所不同,一般以濃度X時間(CT值)作為依據,在 濃度X時間中,其濃度是由具有「不活化性」之 低限濃度,至完全殺菌之上限為範圍,濃度太低 不具殺菌能力,濃度過高亦不可能加速殺菌,此 與一般消毒劑隨劑量而變化有所差異。 由冷卻水塔實際運作中得知,在常態下若溶存0 3 濃度在0. 1 mg/1時,經過3小時才能達到80%之殺Page 22 452640 V. Description of the invention (20) will cause great changes, which is a phenomenon not found in general circulating water systems. Measure various parameters of circulating water as the monitoring and control of injection 0 #. For example, some use ORP, pH, Tempe rature, Conductivity, residual dissolved 0 shore, as a control to control the amount of 0, it is difficult to achieve in practice. This is the result of following the traditional concept, and the "time" factor that has a very important impact on 0 3 is often ignored, which causes the problem of 0 main entry rate to appear and fail. So far, there is no appropriate response method. However, Because the circulation process has a homogenizing effect, and the dissolved 0 has a time-effectiveness, there should be a method that can simplify its operation control. (7) Bactericidal and algae killing effect. After the sun dissolves in water, it forms hydroxide radicals, the oxidation-reduction potential rises greatly, and the bactericidal and algae killing ability also improves. 0 # For sterilization, no matter the reaction mechanism is to destroy the cell membrane or The inhibition of gene growth is covered by the word "inactivation". Generally, when the degree of inactivation reaches 99.9%, it is regarded as complete sterilization. For inactivation of living organisms, it depends on biological objects, categories, and body types. The difference is generally based on the concentration X time (CT value). In the concentration X time, the concentration is from the lower limit concentration with "inactivation" to the upper limit of complete sterilization. The concentration is too low to be sterilized. It is impossible to accelerate the sterilization if the concentration is too high, which is different from the general disinfectant with the dosage. It is learned from the actual operation of the cooling water tower that under normal conditions, if the dissolved 0 3 concentration is 0.1 mg / 1, it will reach 80% killing after 3 hours.
第23頁 ^45 26 4 0 五、發明說明(21) 菌效果,依CT值推論 CT1: 0.4mg/l X 3min = 1.2mg/l-minl00% CT2: O.ling/1 x 180min = 1 8mg / 1-m i n 8 0% 由此可見在溶存0濃度為0 . 1 m g / 1時,係在有效 濃度下限邊緣,故效果不大,時間延長,而若提 高溶存0濃度為0. 4mg/ 1時,則殺菌效果明顯上 升,據實驗室所試驗之結果,以大腸菌為例,有 效濃度下限溶存0谍度約0 . 4mg/ I,上限約為 0. 5 2mg/l,而一般飲用水殺菌時,為0濃度約 0. 3-0. 5mg/ 1之間,接觸時間約6分,實際上濃度 愈高則時間可以縮短到以秒計,請注意在這裡所 謂之時間,係指接觸時間,而非水力停留時間。 由以上分析得知,若溶存0濃度過低則效果有限 ,而若溶存0濃度可以1 0 0 %不活化性化,此後再 注入0济無菌可殺,形成溶存0濃度維持於平衡 定值,面臨難以決定之問題。 (8 )腐蝕作用 0為一種強氧化劑,對某些材質會產生氧化性之 腐蝕作用,此為存在之事實,因此在通常觀念中 ,接觸0鉀份必須考慮使用耐0之材質,但一般 所謂腐蝕程度,是以腐蝕之能力與接觸時間有關 ,低濃度之腐蝕劑在長時間接觸,或高濃度腐蝕 劑在短時間接觸,所產生之腐蝕程度是有限的, 例如常見使用高濃度之強酸、強鹼,作為材料之Page 23 ^ 45 26 4 0 V. Description of the invention (21) Bacterial effect, inferred from CT value CT1: 0.4mg / l X 3min = 1.2mg / l-minl00% CT2: O.ling / 1 x 180min = 1 8mg / 1-min 8 0% It can be seen that when the dissolved 0 concentration is 0.1 mg / 1, it is at the edge of the lower limit of the effective concentration, so the effect is not large and the time is prolonged, and if the dissolved 0 concentration is increased to 0.4 mg / 1 At the time, the bactericidal effect was significantly increased. According to the results of laboratory tests, taking coliform as an example, the lower limit of the effective concentration is 0. 0mg / I, the upper limit is about 0.5 2mg / l, and the general drinking water is bactericidal. When the concentration is 0, the concentration is about 0.3 to 0.5 mg / 1, and the contact time is about 6 minutes. In fact, the higher the concentration, the shorter the time can be shortened to seconds. Please note that the so-called time here refers to the contact time. , Not hydraulic retention time. From the above analysis, it is known that if the concentration of dissolved 0 is too low, the effect is limited, and if the concentration of dissolved 0 can be 100% inactivated, and then injected into the aseptic to kill, forming the dissolved 0 concentration to maintain the equilibrium value, Facing difficult decisions. (8) Corrosion effect 0 is a strong oxidant, which will produce oxidative corrosion effect on some materials. This is a fact of existence. Therefore, in the general concept, 0-resistant materials must be considered when contacting 0 potassium, but generally so-called The degree of corrosion is related to the ability to corrode with the contact time. The low-concentration corrosive agent is exposed for a long time, or the high-concentration corrosive agent is exposed for a short time. The degree of corrosion is limited. For example, high concentrations of strong acids and alkalis are commonly used. As a material
第24頁 452640 五、發明說明(22) 除鏽除垢之用,便是腐蝕作用在短時間接觸所產 生之正面效果。冷卻水塔之循環流程中,基於因 應不同作用與效能,而有不同材質之選擇,例如 冷卻水塔、熱交換器、管路抽水機等,由於冷卻 水塔在作交換時,其滴落之水滴具有很高之曝氣 溶氧效果,因此在設計冷卻水塔系統時,溶氧之 氧化力通常已被考量在内,具有高度氧化力之化 學劑,可能會超出材質忍受範圍,而被排除使用 ,氣氣尚如此,何況是臭氧之氧化力較氣氣更強 ,因此採用0處理時,對材質之腐蝕問題,受到 關注是可以被理解。 許多冷卻水塔循環水使用0處理後,顯示其腐蝕 程度與一般用化學藥品差異不大,且有刷洗結垢 之正面作用,而被認為0在冷卻水塔系統處理, 不致產生腐蝕之觀念並非正確。事實上是因殘留 溶0濃度很低,僅足於移除表面結垢物之故。 由於0在冷卻水塔循環水之環境下,高度之反應 能力及自行分解特性,使得溶0濃度,在極短之 時間内使驟降,尤其經過熱交換器升溫,自行分 解便加速(每上升1 0°C約增加一倍),因此0毐 業廠商便指出,循環之流程不宜超過1 0分鐘,而 欲有留有殘留溶存0濃度,則其前段流程之濃度 便須大幅提高,如此則不僅注入使需求0聶大幅 增加,且對前段之流程,亦會造成較嚴重之腐蝕Page 24 452640 V. Description of the invention (22) The purpose of rust and scale removal is the positive effect of corrosion in short-term contact. In the circulation process of the cooling water tower, based on different functions and efficiency, there are different materials to choose from, such as cooling water towers, heat exchangers, pipeline pumps, etc., because the cooling water towers are exchanged, the dripping water drops have a high The effect of aeration and dissolved oxygen, so when designing cooling water tower systems, the oxidizing power of dissolved oxygen has usually been taken into account. Chemical agents with a high degree of oxidizing power may exceed the material tolerance range, and are excluded from use. In this way, not to mention that the oxidizing power of ozone is stronger than that of air, so when using 0 treatment, the problem of corrosion of materials can be understood. Many circulating cooling water tower cooling water treatments show no significant difference in corrosion degree compared with common chemicals and have the positive effect of scrubbing and scaling. It is considered that the treatment of cooling water tower systems does not cause corrosion. The fact is that the residual dissolved O concentration is very low, which is only enough to remove the surface scale. Due to the high reactivity and self-decomposition characteristics of 0 in the environment of circulating water in the cooling water tower, the concentration of dissolved 0 will drop sharply in a very short period of time, especially after heating up by the heat exchanger, the self-decomposition will accelerate (for every 1 0 ° C approximately doubled), so the 0 manufacturers pointed out that the circulation process should not exceed 10 minutes, and if there is a residual dissolved 0 concentration, the concentration of the previous process must be greatly increased, so not only The injection has greatly increased the demand, and it will also cause severe corrosion to the previous process.
第25頁 452640 五、發明說明(23) ,這是目前採用方法中,為何有材質選擇以及流 程周期時間之限制。 從0<特性及腐蝕程度而言,「時間」成為一重 要運作關鍵,因此若能在流程中,擇取相對之需 求溶存0濃度,並配合流程時間、注入位置及接 觸時間,則可得到合理之防制腐蝕,及減少0濡 求量。 (9 )除垢作用 0本身並非抑制劑(丨11}1以&1:〇1')亦非除垢劑,在 許多長期使用之報告中,卻指出使用0處理冷卻 水塔循環水後,結垢現象明顯減少,而且有些案 例更進一步指出,材料表面有如重新刷洗過一般 乾淨,因此常將其認為0處理重要效益之一,其 實並非通案皆如此。 0具有強大之殺滅微生物能力,因而若表面結垢 ,係以生物膜膠泥為膠著劑時,則因生物膜被殺 死、膠泥被氧化,喪失其附著性,自然會由表面 脫離。一些結垢物質,因被氧化形成可溶性之氧 化物,而可分解結垢,另外有些物質,則因0夂 腐姓而消耗,如鐵、猛等水垢,因此0式對於除 垢,是其主要反應之延伸作用,間接所得之效果 ,但須注意者是,除垢與腐蝕有很密切之關連, 良好之除垢效果往往會伴生腐蝕,尤其為維持一 定濃度以上之溶存0聘,前段流程中溶存0濃度Page 25 452640 V. Description of the invention (23) This is the reason why there are restrictions on material selection and process cycle time in current methods. In terms of 0 < characteristics and degree of corrosion, "time" has become an important operational key, so if you can choose the relative demand to dissolve 0 concentration in the process, and cooperate with the process time, injection location and contact time, you can get a reasonable Prevents corrosion and reduces the amount required. (9) The descaling effect 0 itself is not an inhibitor (丨 11} 1 to & 1: 〇1 ') nor a descaling agent. In many long-term reports, it is pointed out that after using 0 to treat the circulating water of the cooling water tower, The scaling phenomenon is significantly reduced, and some cases further point out that the surface of the material is as clean as re-brushing, so it is often regarded as one of the important benefits of 0 treatment, but it is not always the case. 0 has a strong ability to kill microorganisms. Therefore, if the surface is scaled and the biofilm cement is used as the adhesive, the biofilm will be killed and the cement will be oxidized, losing its adhesion, and will naturally detach from the surface. Some scale materials can be decomposed due to oxidation to form soluble oxides, and some materials are consumed by 0%, such as iron, fierce, and other scales. Therefore, formula 0 is the main factor for descaling. The extension effect of the reaction, the effect obtained indirectly, but it must be noted that descaling is closely related to corrosion, and good descaling effects are often accompanied by corrosion, especially to maintain the solubility above a certain concentration. In the previous process, Dissolved 0 concentration
第26頁 452640 五、發明說明(24) 須很高,如此則對前段流程中之材料’將面腐 蝕之考驗,如何作適當之拿握是技術上一大困難Page 26 452640 V. The description of the invention (24) must be very high. In this case, the test of the material in the previous process will corrode the surface. How to hold it properly is a technical difficulty.
Q 在此再次提示〇表除垢機制’在高濃度時反應性 提高,且所需時間很短,故若以0具有自行分解 之特性加以活用’減少腐蝕及減少0濡求量之期 待,便可實現。 C1 0 )人體安全 # 〇具有很強殺滅生物能力,雖然不是毒藥’但仍 然是具有危害之毒性物質,一向被使用者所關切 ,一般以8小時連續曝露之空氣中之劑量作為安 全指標,在0據度〇.2ppmVol時不會有感覺’ 〇濃 度超過0.2ppmVol至0.5ppm Vol時’可以嗅出剌 激味,但尚屬無害領域,而在0濃度超過0. 5 PPm Vol至30 ppm Vo 1時,是暫時性之有害影響’若〇3 濃度超過30ppmVol至400ppmVol,才會產生永久 性之傷害。至於致死性之0濃度,則在4 0 0 ppm V〇l以上,請注意這些濃度均是在空氣之〇含量 ’從排出源經由空氣擴散及稀釋作用,以及人員 距離發生源之距離而言,實際上可能吸入之劑量 ,遠低於此值,以接觸時間而言,當人員能嗅出 〇刺激味而無害之領域,i分鐘以e^ 30 0ppmVol 10分鐘以内為50ppmVo卜實際上較家庭瓦斯更為 安全。Q here again reminds me that the table descaling mechanism 'reaction increases at high concentrations, and the time required is very short, so if it is used with the property of self-decomposition of 0', it is expected to reduce corrosion and reduce the amount required. Can achieve. C1 0) human safety # 〇 has a strong biocidal ability, although it is not a poison, but it is still a harmful toxic substance, which has always been concerned by users. Generally, the dose in the air exposed for 8 hours is used as a safety indicator. At 0 degrees 0.2 ppmVol, there will be no feeling. '〇 When the concentration exceeds 0.2ppmVol to 0.5ppmVol', it can smell irritating, but it is still harmless, and at 0 concentration exceeding 0.5 PPm Vol to 30 ppm. For Vo 1, it is a temporary harmful effect. 'If the concentration of 〇3 exceeds 30ppmVol to 400ppmVol, permanent damage will occur. As for the lethal concentration of 0, it is above 400 ppm V0l. Please note that these concentrations are based on the content of 0% of air from the source of diffusion and dilution through the air, and the distance of personnel from the source, The actual inhalable dose is much lower than this value. In terms of contact time, when people can smell 0 irritating and harmless areas, i minutes are e ^ 30 0ppmVol within 10 minutes is 50ppm Vo is actually more than family gas More secure.
第27頁 452640 五、發明說明(25) 而在美國及日本,對在空氣中0濃度之限制為 0 . 1 p p m以下,有超量時便加以分解,或停止0發 生裝置,目前採行冷卻水塔0處理為連續注入, 容許濃度較低,而因添加量亦小故無問題,但即 使注入高濃度0 3,只要接觸時間短或人員距離發 生源較遠,亦無安全上之顧慮。 0本身不具爆發性,與可然性氣體混合之爆發濃 度,範圍在2 0 - 1 0 0 w t %,實際是4 8 w t %以上,但無 論任何數值,均超過目前0發生裝置所及最大極 限濃度以上,故尚無此顧慮。 【發明目的與概述】 本發明的目的,係在提供一種低成本、高利用率之冷 卻水塔循環水之臭氧處理系統。 為達到以上的目的,本發明改變傳統冷卻水塔之副系 統,利用一補充水加入中和劑,預先將臭氧氣體溶解成為 高濃度臭氧水,該高濃度臭氧水係由該冷卻水塔之頂部注 入以進行消毒殺菌及滅藻,於臭氧進行冷卻水塔處理期間 ,將回流水旁流隔離作為該砂濾槽所需之逆洗水。 由於〇是唯一具有自行分解之特性,溶解於水中之〇3 自行分解更快,加上pH值、溫度、時間,均對自行分解作 用影響很大,故即使反應流程與傳統方式相同,但其操作 方法則有差異,否則會造成高比例之自行分解損失,因此 目前各種0 A應用工法皆有專利存在。因為不同工法對0 3 之效能利用率,可能相差數以千百倍計,本工法以目前冷 _ 111 ill 111 第28頁 452640 五、發明說明(26) 卻循環水系統之〇處理為對象,預估對成本尚昂貴之〇 :f, 其效能可較傳統0處理法高出數十倍。 【圖式簡單說明】 對於熟習本技藝之人士而言,從以下所作的詳細敘述配合 伴隨的圖式,本發明將能夠更清楚地被暸解,其各種目的 及優點將會變得更明顯。 圖號說明: 10 冷卻水塔 12 冷卻水塔之底槽 14 砂濾槽 16 抽水機 18 製程設備 20 溶解槽 22 臭氧分解裝置 【詳細說明】 傳統冷卻循環水系統如第2圖所示,主系統冷卻循環 水由冷卻水塔1 0對大氣作熱交換後,以底槽1 2匯集,再經 過砂濾槽1 4去除固體物後,由加壓抽水機1 6送入製程之設 備(熱交換器)1 8中,作為冷卻用水,經過設備熱交換之 升溫,回流水則由冷卻水塔1 0頂部進入,為促進空氣對流 以利冷卻水塔中之熱交換,通常設置有風扇(圖中未示) 抽氣。 副系統中,利用補充水補充因蒸發損失、排放損失及 洗砂排水損失之水量。注入中和劑,以對應因蒸發而使冷 卻循環水中pH上升,通常為酸劑。消毒劑則用於殺菌滅藻 ,以維持水質衛生安全,並抑制微生物滋生造成發臭,對 流路造成妨礙阻塞作用。排放水係藉排放口(圖中未示)排Page 27 452640 V. Description of the invention (25) In the United States and Japan, the limit of 0 concentration in the air is less than 0.1 ppm. When there is an excess, it is decomposed, or the 0 generator is stopped. Currently, cooling is used. The treatment of water tower 0 is continuous injection, and the allowable concentration is low, and there is no problem because the addition amount is small. However, even if the high concentration of 0 3 is injected, as long as the contact time is short or the personnel is far away from the source, there are no safety concerns. 0 itself is not explosive, and the explosive concentration mixed with the probable gas ranges from 20 to 100 wt%, which is actually more than 48 wt%, but no matter what the value is, it exceeds the maximum limit of the current 0 generating device. Above the concentration, there is no such concern. [Objective and Summary of the Invention] The object of the present invention is to provide an ozone treatment system for circulating water in a cooling water tower with a low cost and high utilization rate. In order to achieve the above object, the present invention changes the auxiliary system of the conventional cooling water tower, and uses a supplementary water to add a neutralizing agent to dissolve ozone gas into high-concentration ozone water. The high-concentration ozone water is injected from the top of the cooling water tower to Disinfection, sterilization and algae elimination are performed. During the ozone cooling water tower treatment, the reflux water is bypassed as a backwash water required for the sand filter tank. As 〇 is the only one with the characteristics of self-decomposition, 〇3 dissolved in water decomposes faster, and the pH, temperature, and time all have a great influence on the self-decomposition. The operation method is different, otherwise it will cause a high proportion of self-decomposition loss, so currently there are patents for various 0 A application methods. Because the efficiency utilization rate of 0 3 by different construction methods may differ by thousands of times, this construction method is based on the current cold _ 111 ill 111 page 28 452640 V. Description of the invention (26) However, the treatment of circulating water system 0 is the object. It is estimated that the cost of 0: f is still expensive, and its efficiency can be dozens of times higher than that of the traditional 0 processing method. [Brief description of the drawings] For those skilled in the art, the present invention will be more clearly understood from the detailed descriptions and accompanying drawings made below, and its various purposes and advantages will become more apparent. Description of drawing number: 10 Cooling water tower 12 Bottom tank of cooling water tower 14 Sand filter tank 16 Water pump 18 Process equipment 20 Dissolving tank 22 Ozone decomposition device [Detailed description] The traditional cooling circulating water system is shown in Figure 2. The main system cooling circulating water The cooling water tower 10 exchanges heat with the atmosphere, collects it in the bottom tank 12, and then passes through the sand filter tank 14 to remove the solids, and then sends it to the process equipment (heat exchanger) 18 by the pressure pump 16. As the cooling water, the temperature rises through the heat exchange of the equipment, and the return water enters from the top of the cooling water tower 10. In order to promote air convection to facilitate the heat exchange in the cooling water tower, a fan (not shown) is usually provided to extract air. In the secondary system, supplemental water is used to replenish the amount of water lost due to evaporation loss, discharge loss, and sand washing and drainage loss. A neutralizing agent is injected to increase the pH of the cooled circulating water due to evaporation, and is usually an acid agent. Disinfectants are used to sterilize and algae to maintain water quality and safety, and to suppress odors caused by microbial growth and obstruct the flow path. Drainage water is discharged through a drain (not shown)
第29頁 45^640 五、發明說明(27) 出,一般為避免電導度過高形成壁垢,妨礙流路及熱交換 作用,故在上限時,排放部份水量,而以補充水稀釋。最 後,洗砂所排出廢水(洗砂廢水)由砂濾槽1 4中排出,砂 濾槽1 4藉砂床之逆洗用之壓力水管(圖中未示)注入逆洗 水,砂床在過濾某一週期後,因水頭損失過大時,便進行 反沖洗。 基於許多原因之考量,過去經常採用之消毒劑-氣氣 已漸被停止採行,其他替代性消毒劑尚無合適者,最近採 用以0處理冷卻循環水者日益增加,但0 3會自行分解,無 殘留累積性及成本仍高是為主要阻力。在使用以0為消毒 劑時,因0缺少殘存性,故為對主要微生物產生源.做消毒 、殺菌、滅藻時,注入口必須在冷卻水塔之頂部,回流水 進口處才具實效,由於回流水溫度、pH均較高,1不純反 應物含量多,因而使臭氧需用量增加,成為目前最大困難 。而利用冷卻水塔底槽注入方式及問題,前已說明,在此 不另贅述。 本發明則如第3圖所示,請與第2圖比較之。其主系 統之流程仍然維持不變。副系統流程則將補充水、中和劑 、氣體0冼導入溶解槽2 0溶解成為高濃度0冰,之後再由 冷卻水塔1 0頂部注入,進行消毒殺菌及滅藻,而高濃度0 3 水之注入方式,係依冷卻循環系統中,處理場所之需求, 作區段分別,以回分式依序注入適當量。另一不同之點係 利用回流水作為砂濾槽1 4之逆洗水,於0揲行冷卻水塔處 理期間,將循環之回流水旁流隔離,改流入砂濾槽1 4而作Page 29 45 ^ 640 5. Description of the invention (27) It is generally stated that in order to avoid excessive electric conductivity to form wall scale, hinder the flow path and heat exchange effect, at the upper limit, a part of the water is discharged and diluted with supplemental water. Finally, the waste water from the sand washing (sand washing waste water) is discharged from the sand filter tank 14, and the sand filter tank 14 is filled with backwash water through the pressure water pipe (not shown) for the backwash of the sand bed. After a certain period of filtration, when the head loss is too large, a backwash is performed. Due to the consideration of many reasons, the disinfectant-gas often used in the past has been gradually stopped. Other alternative disinfectants are not yet suitable. Recently, the number of people who use 0 to treat cooling circulating water is increasing, but 0 3 will decompose on its own. The main obstacles are the absence of residual accumulation and the high cost. When using 0 as a disinfectant, 0 is lacking, so it is a source of major microorganisms. When disinfecting, sterilizing, and algae killing, the injection port must be on the top of the cooling water tower, and the return water inlet is effective. The running water temperature and pH are both high, and the content of impure reactants is high, which increases the amount of ozone required, which has become the biggest difficulty at present. The method and problems of using the cooling water tower bottom tank injection have been described previously, and will not be repeated here. The present invention is shown in Fig. 3, please compare it with Fig. 2. The processes of its main system remain unchanged. In the secondary system process, supplementary water, neutralizer, and gas are introduced into the dissolution tank 20 to dissolve into high-concentration 0 ice, and then injected from the top of the cooling water tower 10 to sterilize and sterilize and kill algae. High-concentration 0 3 water The injection method is based on the requirements of the processing site in the cooling cycle system, divided into sections, and the appropriate amount is injected sequentially in a return-type manner. Another different point is the use of reflux water as the backwash water of the sand filter tank 14. During the processing of the cooling water tower, the circulating return water is isolated by side flow, and it flows into the sand filter tank 14 instead.
第30頁 452640 五、發明說明(28) 為其之逆洗水,故排放廢水中兼具BLOW DOWN及洗砂廢水 ,使得使用水量及排水量降低。而溶存臭氧之分解裝置2 2 ,在一些特殊場合,為保護製程設備1 8避免受到0腐蝕時 設置。另,砂濾槽1 4尚可利用冷卻水塔之底槽鋪砂粒而形 成。 現,詳列本發明0處理及砂床洗淨程序,以使能更加 了解本發明之半離線回分式臭氧水處理法。首先假設系統 附有風扇抽氣。 1.處理及洗淨預備 (1)酸液注入,0發生設備起動。 (2 )溶解槽2 0開始進行0氣體之溶解,濃度上升。 2 .處理及洗淨開始 (1 )冷卻水塔1 0進流,由回流水切換為0處理水, 而回流水經由BY-PASS管路或其他單元之冷卻 水塔分擔。 (2 )開啟補充水進入0槔解槽後,製成0水流入冷 水塔1 0。 (3 )冷卻水塔風扇停止。 3 . 0處理停止 (1)關閉OZONE發生機。 (2 )補充水繼續流動。 (3 )風扇啟用。 4.逆洗開始 Π)補充水停止,排水開啟,反沖水(逆洗水)開Page 30 452640 V. Description of the invention (28) It is the backwash water, so the discharged wastewater has both BLOW DOWN and sand washing wastewater, which reduces the amount of water used and drainage. The ozone-decomposing device 2 2 is provided in some special occasions to protect the process equipment 18 from 0 corrosion. In addition, the sand filter tank 14 can be formed by laying sand particles in the bottom tank of the cooling water tower. Now, the zero-treatment and sand-bed cleaning procedures of the present invention are listed in detail to enable a better understanding of the semi-offline return-type ozone water treatment method of the present invention. First assume that the system is equipped with a fan exhaust. 1. Preparation for treatment and cleaning (1) Acid injection, 0 equipment startup. (2) The dissolution tank 20 starts to dissolve 0 gas, and the concentration increases. 2. Start of treatment and cleaning (1) The cooling water tower 10 flows in, and the return water is switched to 0 treatment water, and the return water is shared by the cooling water tower of the BY-PASS pipeline or other units. (2) After the supplementary water is turned on and enters the 0 槔 solution tank, 0 water is made to flow into the cold water tower 10. (3) The cooling tower fan stops. 3.0 Processing Stop (1) Turn off the OZONE generator. (2) Make-up water continues to flow. (3) The fan is enabled. 4. Start of backwash Π) Makeup water is stopped, drainage is turned on, and backwash water (backwash water) is turned on
第31頁 w ^ 6 4 Ο 五、發明說明(29) 啟。 (2 ) Β Υ - P A S S切回,進流切換至回流水。 5.洗淨完成 閉關反沖洗進流,排水出流。 6 .生物膜開始成長 洗淨後生物膜從頭開始,進行微生處理時段至到下 一週期。 若僅由系統流程表面來看,很難理解其功能特性之存 在,但若對0轟用之特質則可適用於許多功能之需求,尤 其是對於增加溶解度、反應效能及抑制自行分解,降低消 耗0邊:等方面助益很大,因而與運作上關係十分密切,以 下分別作說明。 1.高濃度0水製作 對冷卻循環水系統之病灶一冷卻水塔1 0作0處理時, 必須能使0與冷卻水塔1 0中附著物及底部匯流槽1 2之滋生 物充分接觸,才能具有效能,因冷卻水塔10内為自由落體 之非連續流,因此進流含0炙水,必須循原來流路注入, 亦即在回流水之出口,即是冷卻水塔之進口。彳艮不幸地, 回流水出口是冷卻循環系統中,對0接觸反應條件最為不 利之處,因而效果很低,成為使用0不經濟之重要原因。 對溶解氣相0在水中,不利條件為P Η值高、溫度高、 耗用0對象物含量高,無足夠之水深供0氨泡接觸行程, 無足夠之時間形成氫氧自由基。pH值高、溫度高會促進〇3 之自行分解,無足夠水深及溶解時間,則氣泡内0粳排出P. 31 w ^ 6 4 〇 V. Description of the invention (29) Kai. (2) Β Υ-P A S S is switched back and the inflow is switched to reflux water. 5. Washing is completed. Close the backwash, and drain the outflow. 6. The biofilm begins to grow. After washing, the biofilm starts from the beginning and undergoes a micro-biotreatment period to the next cycle. If only from the surface of the system process, it is difficult to understand the existence of its functional characteristics, but if it is used for the characteristics of zero bombardment, it can be applied to the needs of many functions, especially for increasing solubility, reaction efficiency, inhibiting self-decomposition, and reducing consumption. Side 0: It is very helpful in other aspects, so it has a close relationship with the operation, which will be explained separately below. 1. When high concentration 0 water is used to treat the lesion of the cooling circulating water system, the cooling water tower 10, and 0, the 0 must be able to make full contact with the attachments in the cooling water tower 10 and the nourishing organisms at the bottom manifold 12 to have Efficiency, because the cooling water tower 10 is a non-continuous flow of free fall, so the inflow contains zero hot water, which must be injected through the original flow path, that is, the outlet of the return water is the inlet of the cooling water tower. It is unfortunate that the return water outlet is the most unfavorable place in the cooling circulation system for the reaction conditions of 0 contact, so the effect is very low, and it becomes an important reason for the uneconomical use of 0. Disadvantages for dissolving gas phase 0 in water are high PΗ value, high temperature, high content of consumed 0 objects, insufficient water depth for 0 ammonia bubble contact stroke, and insufficient time to form hydroxyl radicals. High pH and high temperature will promote the self-decomposition of 〇3. If there is not enough water depth and dissolution time, 0 will be discharged in the bubble.
第32頁 • 45 26 4 0 五、發明說明(30) 液表散溢無法充分利用,這些因素在回流水中均為系統内 之上限高點。 在注入點無法變更下,探討改變回流水之屬行是否可 行,答案是否定的,因需付出更高之代價。 本發明係採用冷卻循環系統不可或缺之補充水(MAKE U P W A T E R),作為製造高濃度之0水,除因補充水較低溫 及潔淨之外,另外依循系統之需要,將中和用之酸劑,在 0水處理期間集中使用以降低pH值。 由於高濃度0冰處理時間短、流量低,因此營造各種 有利0瘙解及氫氧自由基之產生等條件,便容易實現。 含高比例氫氧自由基之高濃度0水,是以一接觸溶解 槽,導入補充水、酸劑及0氨體,在足夠深度及停留時間 下,進行接觸溶解,並與水反應,形成高氧化還原電位之 氫氧自由基,旋即注入冷卻水塔中處理。 因高濃度0拃處理時,亦以滴落之自由落體方式進行 接觸反應,因此可使用水理上低限之流量,一般而言約為 循環水流量1 5 %至2 0 %之間,由於處理用之補充水僅約1 0分 鐘,對於每日所需補充水總量而言,比例甚低,故水量上 可以接受。 中和冷卻循環水鹼性化所需之酸劑,可以估算或實証 得知,因冷卻水為循環系統,故中和劑可以集中注入系統 ,若僅以小量之補充水為對象,則中和酸劑將使其pH值降 低很多,這並不須另外增加系統之負擔,且,只是將中和 用酸劑先行導入補充水中加以利用,並未消耗,基本上亦Page 32 • 45 26 4 0 V. Description of the invention (30) The liquid surface overflow cannot be fully utilized. These factors are the upper limit of the system in the return water. Under the condition that the injection point cannot be changed, explore whether it is feasible to change the ownership of the return water. The answer is no, because a higher price is required. The invention adopts make-up water, which is indispensable for the cooling circulation system, as a high-concentration 0-water, in addition to the low temperature and cleanness of the make-up water, and in accordance with the needs of the system, the acidifier used for neutralization It is used intensively to reduce pH during 0 water treatment. Because the high-concentration 0-ice processing time is short and the flow rate is low, it is easy to create a variety of conditions that are favorable for the dissolution and the generation of hydroxyl radicals. The high-concentration 0-water containing a high proportion of hydroxyl radicals is introduced into a contact dissolution tank, and supplemental water, an acid agent, and 0-ammonia are introduced. The contact is dissolved at a sufficient depth and residence time, and reacts with water to form a high concentration. The redox potential of the hydrogen and oxygen radicals is immediately injected into a cooling water tower for processing. Because the high-concentration 0 拃 treatment, the contact reaction is also carried out in the form of a free-falling drop. Therefore, the lower flow limit of the water can be used. Generally speaking, it is about 15% to 20% of the circulating water flow. The supplementary water used for treatment is only about 10 minutes. For the total amount of daily supplementary water required, the proportion is very low, so the amount of water is acceptable. The acidifying agent required to neutralize the cooling cycle water can be estimated or empirically obtained. Because the cooling water is a circulating system, the neutralizing agent can be injected into the system centrally. If only a small amount of supplementary water is used as the object, the neutralizing agent is neutralized. And acid will reduce its pH value a lot, which does not need to increase the burden on the system, and only the neutralizing acid is first introduced into the make-up water for use, it is not consumed, basically
第33頁 452640 五、發明說明(31) 無問題。 氣相0在水中以氣泡型式上升,而在上浮過程與水接 觸而溶解及反應,在使用一般散氣裝置下,效率之水深約 在4 - 5 Μ之間,因此溶解槽可以配合設置,而在接觸溶解 過程所需時間,大抵在1 - 3 Μ I Ν之間,由於使用之溶解水 流量不大,槽容積需求有限,配合必要之水深,便可設計 筒型之溶解槽,或以機械離心力溶入法,以提升0水濃度 〇 由以上分析、製作含高比例氫氧自由基之高濃度0冰 ,只要將既有設施導入溶解槽2 0,先行與0氟體反應,再 調配操作方法,便可簡易形成,但高濃度0水不僅反應速 率加快,需要量亦減少,尤其因流量之減低,使設備管路 容量均減少,在技術上及經濟上均具高度之可行性= 2 .高濃度0水注入方法 冷卻循環水流程中,冷卻水塔1 0之散熱單元屬於開放 空間,許多污雜物質、微生物均由此處進入系統中,而冷 卻水塔1 0之環境又特別適合阻害物之滋生,例如細菌、藻 類、生物膜之生長及沈積物,附著物等之壓密巨積化,形 成醫學上所稱之病灶,因此進行缺乏殘留性之0處理時, 自當以冷卻水塔1 0為主要對象,亦即0夂注入,須在冷卻 水塔1 0上游或其内部,由於在冷卻水塔1 0中之液體流路, 因散熱之需要,將流體散化為顆粒狀,以自由落體方式掉 落,為非連續流體,因此在冷卻水塔1 0中注入氣相之0 3, 很難有良好之接觸反應,大部份可能隨對流空氣強制排出Page 33 452640 V. Description of the invention (31) No problem. The gas phase 0 rises in the form of bubbles in water, and dissolves and reacts with water in contact with the water during the upward floating process. The efficiency of the water depth is about 4-5 μm when using a general air dispersing device. The time required for the contact dissolution process is between 1 and 3 Μ Ν. Because the flow of dissolved water is not large, the volume of the tank needs to be limited. With the necessary water depth, a cylindrical dissolution tank can be designed, or mechanically The centrifugal dissolution method is used to increase the concentration of 0 water. From the above analysis, a high concentration of 0 ice containing a high proportion of hydroxyl radicals is produced. As long as the existing facilities are introduced into the dissolution tank 20, the reaction with 0 fluoride is performed first, and then the deployment operation is performed. The method can be easily formed, but the high-concentration 0-water not only accelerates the reaction rate, but also reduces the demand, especially because the flow rate is reduced, the equipment pipeline capacity is reduced, which is highly feasible technically and economically = 2 In the high-concentration 0-water injection method, in the cooling circulating water process, the cooling unit of the cooling water tower 10 is an open space, and many pollutants and microorganisms enter the system from here. The environment is particularly suitable for the growth of obstacles, such as the growth of bacteria, algae, biofilms, and the accumulation of sediments, attachments, etc., to form medically known lesions. Therefore, when the zero treatment is lacking, Since the cooling water tower 10 is the main object, that is, 0 夂 injection, it must be upstream of or inside the cooling water tower 10. Due to the liquid flow path in the cooling water tower 10, due to the need for heat dissipation, the fluid is dispersed into It is granular and falls as a free-fall body. It is a discontinuous fluid. Therefore, 0 3 of the gas phase is injected into the cooling water tower 10, and it is difficult to have a good contact reaction. Most of them may be forced out with convection air.
第34頁 4 5 2 b' 4 Ο 五、發明說明(32) 在冷卻水塔1 0底部之匯流 聪力低,而且位於下游’無 應處理’效果不佳不宣採行 ,唯有在塔上方之回流水處 流程,可以在流程中尋找合 回流水之出口處,緊鄰 其流量大而距離短,水力停 口即使有分水渠道,水深亦 水中之時間、行程均很短, 加上回流水之水溫、pH值 應,卻助長〇 3自行分解速率 成分,亦會牦用部份之溶存 底槽1 2深度有限,溶解〇 > 法對上位之冷卻水塔1〇進^ ’是故在冷卻水塔1 0之0痒入 ’此與一般使用非0處理法之 適之注入點並不相同。 於冷卻水塔1 0上方之進流口, 留時間通常以秒計,回流水出 十分有限’使得〇氣泡停留於 氣體0轉成溶解〇之比率偏低 均高’不利於〇氩體之溶解反 ’另外’回流水中所含之各種 〇3,以致於降低冷卻水塔10中 失及0扣失’亦不因回流水參數變動而受到影響。 〇處理水之0後度’這種沿習至今之氣相注入方法,實際 上是不適用於像冷卻水塔1 〇 ’非連續流之處理流程。 〇水注入法是完全摒棄上述氣體注入流程之方式,而 是以前置設備’預先將氣相0轉化成流體化之溶存〇水, 再以相同之水理注入冷卻水塔中運作,因而其接觸反應 所及’與原來循環水相同’使冷卻水塔1 〇中得以高濃度0 3 水進行處理’且不會有氣相主入回流水所具有之各種缺 以〇水注入冷卻水塔1 0中,除與附著物進行接觸反應 以外,其他損失很少,因而能維持一定以上之高漢度〇3, 充分發揮其殺菌、滅薄、促進生物膜、附著物之脫落作用Page 34 4 5 2 b '4 〇 V. Description of the invention (32) The confluence at the bottom of the cooling water tower 10 is low, and it is located in the downstream' no response '. In the return water flow process, you can find the exit of the combined return water in the process, which is close to its large flow and short distance. Even if the hydraulic stop has a water diversion channel, the water depth and time in the water are very short, plus the return water. The water temperature and pH value should promote the cleavage rate component of 〇3, and some of the dissolved bottom tank 12 will also be used to a limited depth. The method of dissolving 〇 > into the upper cooling water tower 10 ^ 'is why Cooling tower 1 0 0 0 ticks' This is not the same as the normal injection point of non-zero treatment. At the inlet above the cooling water tower 10, the retention time is usually measured in seconds, and the return water is very limited, so that the percentage of air bubbles staying in the gas 0 to dissolve is low and high, which is not conducive to the dissolution of argon. 'Additionally' various kinds of O3 contained in the return water, so as to reduce the loss in the cooling water tower 10 and zero buckle loss' are not affected by changes in the return water parameters. The 0-degree after-treatment water treatment method, which is a conventional gas-phase injection method, is actually not applicable to the treatment flow of a discontinuous flow such as a cooling water tower 1 0 '. 〇 Water injection method is to completely abandon the above-mentioned gas injection process. Instead, the gas phase 0 is converted into fluidized dissolved water in advance by the pre-equipment, and then injected into the cooling water tower with the same water treatment to operate, so its contact reaction The same 'same as the original circulating water' enables the high concentration of 0 3 water in the cooling water tower 10 to be treated 'and there will be no shortage of gas phase into the return water. The water is injected into the cooling water tower 10, except for Except for the contact reaction with attachments, other losses are small, so it can maintain a high degree of certainty above a certain level. It can fully exert its sterilization, thinning, and promote the shedding of biofilms and attachments.
45^640 五、發明說明(33) 3 ·冷卻水塔匯流底槽之0處理 由冷卻水塔1 0内掉落之水滴,在冷卻水塔1 0底部通常 設有匯流之底槽1 2,以便抽水機1 6抽取加壓,再送入製程 中進行冷卻,因匯流底槽1 2,由非連續性水體轉換成連續 性流體,故其水理與一般連續性流體相同。 經過冷卻水塔1 0滴落之水,是各種物質集合之場所, 因而冷卻水塔1 0之底槽1 2,常成為微生物、細菌、藻類滋 生之温床,亦是冷卻循環系統必須處理之另一重點,由於 在塔1 0内非連續流接觸反應,所消耗之0不大,(時間短 、殺菌、滅藻耗用0邊:小),故尚有相當高濃度之0水存在 ,以此0水作為槽底物連續流體之接觸反應,並在流力之 作用下而攪拌均化,如此可使底槽1 2得到良好之0處理效 果。 底槽1 2為連續流體且停留時間長,因此可能進行各種 反應機制,使得流出水0濃度降低,另外,在複數並聯運 作之冷卻水塔10,當單塔進行0水處理時,其出流水因與 他塔混合而稀釋,或與其他成分反應後,可以降低其0濃 度,基本上至抽水機1 6或送入製程中之冷卻水,其含0濃 度已低,且因後續反應及自行分解,使0濃度更為降低。 4 .依區段分注0冰· 在冷卻水塔10循環流程中,有需要以0處理之場所及 適合0反應之區段,而且在一辛大型冷卻循環水系統中, 常包含有複數之設備,例如冷卻水塔、冷凍機、冷凝器及 熱交換器等,由於0 3會自行分解及反應耗用,高濃度之溶45 ^ 640 V. Description of the invention (33) 3 · 0 of the cooling water tower's confluence bottom tank handles the water drops falling from the cooling water tower 10, and the bottom of the cooling water tower 10 is usually equipped with a confluence bottom tank 12 to facilitate the pump 1 6 Extraction and pressure, and then sent to the process for cooling, because the confluence bottom tank 12 is converted from a discontinuous water body to a continuous fluid, so its hydraulics is the same as that of a general continuous fluid. The water dripping through the cooling water tower 10 is a place where various substances gather. Therefore, the bottom tank 12 of the cooling water tower 10 often becomes a breeding ground for microorganisms, bacteria, and algae. It is also another focus of the cooling circulation system. Because of the discontinuous flow contact reaction in the tower 10, the consumption of 0 is not large (short time, sterilization, algae consumption 0 side: small), so there is still a relatively high concentration of 0 water, so 0 Water is used as a continuous fluid contact reaction of the bottom of the tank, and is stirred and homogenized under the action of the flow force, so that the bottom tank 12 can obtain a good 0 treatment effect. The bottom tank 12 is a continuous fluid and has a long residence time. Therefore, various reaction mechanisms may be performed to reduce the concentration of effluent water 0. In addition, in a plurality of cooling water towers 10 operating in parallel, when a single tower is treated with 0 water, the effluent water is caused by After mixing with other towers and diluting or reacting with other ingredients, it can reduce its 0 concentration, basically until the pump 16 or the cooling water sent to the process, which has a low concentration of 0, and due to subsequent reactions and self-decomposition, Reduce the 0 concentration even more. 4. Dispensing 0 ice by section · In the cooling water tower 10 cycle flow, there are places that need to be treated with 0 and sections suitable for 0 reaction, and a large cooling circulating water system often contains multiple equipment , Such as cooling water towers, freezers, condensers and heat exchangers, etc., because 0 3 will decompose and react on its own, high concentration of solvent
第36頁 45264〇 1----- 五、發明說明(34) 子〇扃造成腐蝕損害’及加速分解,而且系統中每 成 一 _ -W 一 、、'/U t -Ιψ —場所 二品丰又’所需要ο處理之用途與程度不同,因而傳 樂量取殘留0痛度,是不適當且無多大意義。傳、洗加 以需要0處理之場所,所需求之〇處理濃度為標的, 配合該區間之操作條件,作分別注入〇產’則可以得到較 ,之效果與經濟,亦藉由〇狀速自行分解之效應,避免過 量殘留0表累積’而對系統造成損害,為使〇處理有效, 不致過量造成腐蝕,及經濟成本上考量,以回分方式定值 注入0 3’便可在有多處設備之系統中,則可採用順序運作 〇處理’以減少〇發生裝置之容量。 以上述依場所、區段作〇水回分注處理時,便可解決 循環流程時間過長’或多數水塔、熱交換器之多目的使用 ,以及容量過大(10,000 gal)之問題。 以下以一實施例說明如後: (1)各場所之0徉入量: 冷卻水塔循環系統中,各參考點之溶存〇值須 視水質調整,較佳實施例之溶存0值範圍如下 表所示: 各料點 溶存〇5值 底檐臭乾水ii入處 0^ppm-1.5ppm 槽猶各 O.G25ppmO25ppm 斜勒由木口 0.075ρρπΗ). 15ppm 熱交換器進流口 0.04ppmO_08ppm 辦邮回济叙散減 0.010ppnK).04ppmP.36 45264〇1 ----- V. Description of the invention (34) 扃 〇 扃 Causes corrosion damage 'and accelerated decomposition, and each component in the system _ -W Ⅰ,' / U t -Ιψ — two products in the place Feng You's needs are different in the use and degree of treatment, so it is inappropriate and meaningless to take the residual pain level with the amount of music. Passing and washing places that require 0 treatments, the required 0 treatment concentration is the standard, and according to the operating conditions of the interval, the injection of 0 production can be compared, the effect is economical, and it is also self-decomposed by the 0 speed Effect, to avoid excessive residual accumulation of 0 meters, and cause damage to the system. In order to make the 0 treatment effective, not to cause excessive corrosion, and economic cost considerations, the value of 0 3 'can be set in a retrospective way to set the value in multiple devices. In the system, you can use sequential operations and processing to reduce the capacity of the generating device. With the above-mentioned 0-water re-dispensing treatment according to the location and sector, the problems of excessively long circulation flow time, multi-purpose use of most water towers and heat exchangers, and excessive capacity (10,000 gal) can be solved. The following is an example to explain the following: (1) The amount of 0 in each place: In the cooling water tower circulation system, the zero value of each reference point must be adjusted according to the water quality. The range of the zero value of the preferred embodiment is as follows: Show: Dissolve at each material point. 05 value, bottom eaves, smelly dry water ii. 0 ^ ppm-1.5ppm. Slots are O.G25ppmO25ppm, slanted by wooden port 0.075ρρπΗ). 15ppm heat exchanger inlet 0.04ppmO_08ppm (Scatter reduction 0.010ppnK) .04ppm
第37頁 五、發明說明(35) 依據與中國鋼鐵公司,華邦電子公司之技術研 討’認為苔蘚、藻類形成至可見程度約3-5天 ’故若每天能於回流水進入冷卻水塔之塔頂處 時’以進程短時間之高濃度〇飧灑,則可在初 期將累積之水垢及藻類孢子去除當可化解這種 瓶頸’ ~般以5〜10pp m濃度之0水進行約一循 環週期之注入,則可使全系統積垢現象降低。 由於短時間之腐蝕性,不會對管路材質造成累 積性之傷害,因此即使〇择入有短時間過量的 情形’亦不致會較長期效應所導致之腐蝕性為 嚴重,何況0馮自行分解無殘留累積性,因此 在此以0作為處理方法更為適合。 (2 )冷卻水量: 使用0處理冷卻水塔之水量是指系統水量而言 ,依現有旁流方法注入〇 3,在系統水量為2 0 0 0 0 加侖時每天約需7 K G之〇 r如果改使用離線批 次注入法’則每天一次以四倍〇痒入量,約持 續10-30分鐘,則可達成去除水垢殺藻之需求 。相對地,平常以80%連續注入,則需〇邊為: 70Kgx 80% = 5. 6kg...... (ι ) 7kgx 400%x l/24x 1/2= 0.6kg...... (2) 每天耗用0邊=(1) + (2) = 6. 2kg<7.0kg〔較目前 旁流法節省0供給量〕 其他有關冷卻水量’是依系統需求條件而定,Page 37 V. Description of the invention (35) According to the technical discussion with China Iron and Steel Corporation and Winbond Electronics Corporation, 'think that moss and algae have formed to a visible level for about 3-5 days'. Therefore, if the return water can enter the cooling tower every day, At the top, 'spray at a high concentration for a short period of time, then the accumulated scale and algae spores can be removed in the early stage when this bottleneck can be resolved. ~ Generally, a 0 ~ 5 ppm concentration of 0 water is used for about a cycle. The injection can reduce the fouling phenomenon of the whole system. Due to the short-term corrosiveness, it will not cause cumulative damage to the pipeline material. Therefore, even if a short-term excess is selected, it will not cause serious corrosiveness caused by long-term effects, let alone 0 Feng's own decomposition There is no residual accumulation, so it is more suitable to use 0 as the treatment method. (2) Cooling water volume: The water volume of the cooling water tower treated with 0 refers to the system water volume, which is injected by using the existing bypass method. When the system water volume is 20000 gallons, it will take about 7 kg per day. The offline batch injection method is used to quadruple the amount of itching once a day for about 10-30 minutes, and the demand for removing scale and algae can be achieved. In contrast, continuous injection at 80% usually requires 0 edges: 70Kgx 80% = 5. 6kg ... (ι) 7kgx 400% xl / 24x 1/2 = 0.6kg ... (2) Consumption of 0 sides per day = (1) + (2) = 6. 2kg < 7.0kg [saving 0 supply compared with the current bypass method] Other related cooling water 'is based on system demand conditions,
第38頁 4 5 2 6 4 Ο 五、發明說明(36) 例如循環周期,熱交換率、溫度差等依據環境 場合而有所不同β (3 )逆洗水量: 因冷卻循環水為閉路系統,其污質在系統内呈 現累積’利用Blow down及補充水以降低系統 内固體物與電導度濃度,故Blow down水量足 依系統内電導度為指標,即濃度周期。一般而 言’閉路系統較開路系統中過濾槽所需逆洗週 期為長亦即破穿洩漏時間長’目前係利用B 1 〇w down之水作為逆洗砂濾槽之用,因而並不致於 需要額外之逆洗耗水。作者本身在國内外自來 水淨水場,污度水處理廠’有許多過濾槽之經 驗’逆洗用水依過濾方式(上向流或下向流〕 濾材’洗淨方式〔水洗 '空洗或兼用〕而有出 入,並非定值,在逆洗過程中,以5〜丨〇倍於過 渡流直之逆洗水量行之,但本方法居然足以排 放水之二次利用,故不必考慮渡層之水損失情 況’而以Blow down之水全量作為渡槽之逆洗 用水量。 (4 )各場所之溫度: 冷卻水使用’經過熱交換吸熱增溫為最高值, 可反應於回流水出口處’會因循環流量、熱交 換器之溫度及傳導熱量而改變,在〇處理系統 中最好低於Π 5°F經冷卻水塔’冷卻後之水溫Page 38 4 5 2 6 4 〇 V. Description of the invention (36) For example, the cycle period, heat exchange rate, temperature difference, etc. vary depending on the environmental situation β (3) Backwash water volume: Because the cooling circulating water is a closed circuit system, The pollutants in the system are cumulative. Blow down and supplemental water are used to reduce the concentration of solids and conductivity in the system. Therefore, the amount of Blow down water is based on the conductivity in the system as an indicator, that is, the concentration cycle. Generally speaking, 'the closed-loop system requires a longer backwash cycle than the open-circuit filter tank, that is, it takes longer to break through and leak.' Currently, B 1 0w down water is used as a backwash sand filter tank, so it does not cause Requires additional backwash water. The author himself has domestic and foreign tap water purification plants, and the sewage water treatment plants have "experience with many filtration tanks". The backwash water is filtered according to the filtering method (upward flow or downward flow). The filter material is "washing method." There are discrepancies, which are not fixed values. During the backwash process, the amount of backwash water is 5 to 丨 0 times that of the transitional flow. However, this method is enough to discharge the secondary use of water, so it is not necessary to consider the water in the crossing. Loss situation ', and the total amount of Blow down water is used as the backwash water for the aqueduct. (4) Temperatures in various places: The cooling water use' heat absorption and temperature increase through heat exchange to the highest value, which can be reflected at the return water outlet 'will cause Circulating flow rate, heat exchanger temperature and heat conduction change, it is best to be lower than Π 5 ° F in the treatment system.
第39頁 4 5 2 64 0 五、發明說明U7) 與氣溫及冷卻水塔效率有關,一般以大氣溫度 為下限,對0雨言,水溫冷卻能力均有關,經 驗上顯示每增加一冷卻噸則須提高0痒入率的 1 ppm ° 系統中因機械散熱而使抽水機出口溫度略升, 氣體散出吸收熱量而使水溫略降,但影響有限 常略而不計,因此,冷卻系統中以冷卻水塔進 流與出流,以及熱交換器入口與出口水溫作為 較明顯分界,而此兩者則在系統設計時已被推 估,在實際操作時須作修正,並非每一系統均 為定值,亦非每一時段均相同。 5 . 0武生物膜濾、床 冷卻循環系統中,在冷卻水塔1 0處為開放空間,難免 有外物介入,其中有機物與微生物結合而滋生,產生生化 反應,對於水質淨化而言具有正面意義,但生物膜及藻類 殘骸所產生之巨積固形物,卻常成為冷卻系統流路之阻害 物,影響正常運作而成為頭痛之問題。 由於冷卻循環水並非完全封閉系統,外物介入集結或 微生物、藻類殘骸,必須加以移除,因而通常在冷卻循環 水系統中,設有過濾之設備,但過濾之設備僅適用篩留粒 徑較大之固形物,對微小及溶解物質功能很低,又因冷卻 循環水不適用加藥絮凝,通常對水質淨化作用有限。 當循環水因蒸發水份而使成分濃度上升,或外來物質 累積,導致水質劣化達到某一限度時,必須作排放,另以Page 39 4 5 2 64 0 V. Description of the invention U7) It is related to air temperature and cooling tower efficiency. Generally, the atmospheric temperature is the lower limit. For 0 rain words, the water temperature cooling capacity is related. Experience shows that for each additional cooling ton 1 ppm must be increased by 0 ticks ° In the system, the temperature of the outlet of the pump is slightly increased due to mechanical heat dissipation, and the temperature of the water is slightly reduced due to the heat released by the gas, but the impact is limited and often ignored. Therefore, the cooling system uses The inflow and outflow of the water tower, and the water temperature at the inlet and outlet of the heat exchanger are the more obvious boundaries. These two have been estimated in the system design and must be corrected in actual operation. Not every system is fixed. The value is not the same every time. In 5.0 biological membrane filtration and bed cooling circulation system, there is an open space at 10 of the cooling water tower, and foreign objects are inevitably involved. Organic matter and microorganisms are combined to breed and produce a biochemical reaction, which has positive significance for water purification. However, the massive solids produced by biofilms and algae debris often become obstacles to the cooling system flow path, affecting normal operation and becoming a headache. Because the cooling circulating water is not a completely closed system, foreign objects involved in the build-up or the debris of microorganisms and algae must be removed. Therefore, in the cooling circulating water system, filtering equipment is usually provided, but the filtering equipment is only suitable for screening. Large solids have low functions for small and dissolved substances, and are not suitable for medicinal flocculation due to cooling circulating water, which usually has limited purification effect on water quality. When the circulating water causes the component concentration to rise due to the evaporation of water, or the accumulation of foreign substances causes the water quality to reach a certain limit, it must be discharged.
第40頁 452640 五 '發明說明(38) 潔淨水入替補充因而會增加耗水量。 由上述分析得知,如果能在冷卻循環水系統中產生生 化作用,則對水質淨化有相當助益,但主要關鍵在於不能 使微生物、藻類過度成長,以及殘骸必須移除至系統外, 才能實現。 在傳統所使用之消毒劑,若欲在短時間内殺菌、滅藻 ,必須使用較高之劑量,但因冷卻循環之週期短(數分鐘 至十數分鐘),殘餘消毒劑仍然會回到微生物作用之發生 源,抑制微生物滋生,而無法收到生物處理之效果,但若 消毒劑量不足,則無法完全消滅菌藻,可能形成巨積體, 而對冷卻循環系統之流程造成危害,很難兩全其美。 利用臭氧作消毒、殺菌、滅藻是有其效用,但成本居 高,本工法除以〇拃為消毒、殺菌、滅藻之功能以外,另 就0 A自行分解特性,加以利而構成生物處理之機制。 其方法係以塔底之匯流池1 2或集水渠,鋪砂粒而成濾 床,或緊接冷卻水塔之後進行砂濾單元1 4,則以砂粒為生 物膜之介質,形成生物濾床。微生物在介質砂粒表面成長 ,自然產生淨化作用,在經過一段時間後,生物膜成長到 某一厚度時,便以0對微生物殺滅及對生物膜氧化,破壞 其膠泥,強制其脫離介質表面,再利用清水逆洗將生物膜 及砂床篩留物移除排出,0處理停止後,生物膜作用重新 開始成長,如此週而復始,生物淨化作用便可實現。 由於0殺菌、滅藻及氧化力極強,高濃度ο β可縮減 其反應時間,因此採用高濃度0樵行短時間之殺菌,可能Page 40 452640 V. Description of the invention (38) The replacement of clean water will increase water consumption. According to the above analysis, if it can produce biochemical effects in the cooling and circulating water system, it will be quite helpful for water purification, but the main key is that it cannot make microorganisms and algae grow excessively, and the debris must be removed outside the system to achieve. . In traditional disinfectants, if you want to sterilize and kill algae in a short time, you must use a higher dose, but because of the short cycle of the cooling cycle (several minutes to ten minutes), the residual disinfectant will still return to the microorganisms. The source of the effect can inhibit the growth of microorganisms, and cannot receive the effect of biological treatment. However, if the disinfection dose is insufficient, the algae cannot be completely disinfected, and macroliths may be formed, which will harm the process of the cooling circulation system and it is difficult to achieve the best of both worlds. . The use of ozone for disinfection, sterilization, and algae killing has its effectiveness, but the cost is high. In addition to 〇 拃 for disinfection, sterilization, and algae killing, this method also has 0 A self-decomposition characteristics, which is beneficial for biological treatment. The mechanism. The method is to use sand pools 12 or water collecting channels at the bottom of the tower to spread sand grains to form a filter bed, or to directly carry out the sand filtration unit 14 after the cooling water tower, and then use the sand grains as a biofilm medium to form a biological filter bed. Microorganisms grow on the surface of medium sand and naturally produce a purification effect. After a period of time, when the biofilm grows to a certain thickness, it kills the microorganisms and oxidizes the biofilm with 0, destroys its cement, and forces it to detach from the surface of the medium. The biofilm and sand bed sieve are removed and discharged by backwashing with clean water. After the 0 treatment is stopped, the biofilm action starts to grow again, so in this cycle, the biological purification effect can be achieved. Because 0 sterilization, algae killing and oxidizing power are very strong, high concentration ο β can reduce its reaction time, so using high concentration 0 樵 for short time sterilization, it is possible
第41頁 462640 五、發明說明(39) 有高濃度之殘餘〇疯出,但在水量稀釋,反應物再耗用1 長時間之自行分解,及製程高溫之分解,則回流水中大抵 無殘餘0 3。 一般生物膜之脫落,係因生物膜增厚以後,由内部厭 氧菌之分解,而使生物膜、膠泥附著力減低,再因重力或 流力促其剝離脫落,但如此必須經過厭氧消化過程,時間 長、體積大,且不易掌握,利用0處理之目的,在於使生 物活性消滅,且對膠泥作氧化分解,使其附著力在短時間 内強制下降而脫離,無須依賴生物膜成長之狀況,因而不 致形成過大體積之脫落殘骸。 一般生物膜之成長,在數曰内尚未達到為害程度,藻 類亦如此,故若以數日為一週期,進行0處理及砂層洗淨 ,然後重新開始,則不致形成對系統之障礙,而在這段期 間,生物之淨化作用便可利用。 6.分解殘餘溶存臭氧,保護設備免於腐蝕 臭氧為強氧化物,會因反應而消失,自行分解而消失 ,因氫氧自由基快速連鎖反應而消失,另外亦可因熱解、 觸媒反應、活性碳吸附或紫外線破壞而被強制消失,基於 這種特性,在對一些為避免0腐蝕之流程設備,便可使用 臭氧分解裝置2 2等方法來加以化解,亦即在必要時,可 藉由這些措施,使溶存0濃度大幅降低至安全值,這是其 他化學藥品難以實現之特別用途β 再者,對本發明之技術更進一步說明。Page 41 462640 V. Description of the invention (39) There is a high concentration of residues. 0 Crazy, but after dilution in water, the reactants take another long time to decompose on their own, and in the process of high temperature decomposition, there is almost no residue in the reflux water. 3. Generally, the biofilm is shed, because the biofilm is thickened, it is decomposed by the internal anaerobic bacteria, which reduces the adhesion of the biofilm and the cement, and then it is peeled off by gravity or fluid force, but it must go through the anaerobic digestion process. The time is long, the volume is large, and it is not easy to grasp. The purpose of using 0 treatment is to destroy the biological activity, and to oxidize and decompose the cement, so that its adhesion is forcibly reduced and detached in a short time, without relying on the growth of the biofilm. Therefore, no excessively large volume of falling debris is formed. In general, the growth of biofilms has not reached a harmful level within a few days, and so is algae. Therefore, if a period of several days is used for 0 treatment and sand layer cleaning, and then restarted, it will not form an obstacle to the system. During this period, the biological purification effect can be used. 6. Decompose the residual dissolved ozone, protect the equipment from corrosion. Ozone is a strong oxide, which will disappear due to the reaction, self-decomposition and disappear, disappear due to the rapid chain reaction of hydroxyl radicals, and it can also be caused by pyrolysis and catalyst reaction. , Activated carbon adsorption or UV destruction and forced disappearance. Based on this characteristic, for some process equipment to avoid zero corrosion, you can use the ozone decomposition device 22 and other methods to resolve, that is, when necessary, you can borrow Due to these measures, the dissolved 0 concentration is greatly reduced to a safe value, which is a special application that is difficult to achieve by other chemicals. Furthermore, the technology of the present invention is further explained.
1 .臭氧水中之pH 452640 五、發明說明(40) 臭氧之溶解速度及飽和溶解率,以低P丨丨值較佳,氫氣 自由基亦在酸性溶液中較易存在’相反地0 3自行分解率’ 隨pH值上升而以對數增加’因而在0森體進行溶解及水解 ,反應時其pH最好能低下’由於冷卻水之pH值在高溫下’ 酸性成分易形成氣體溢出’因而偏向高plHt,經過一段時 間必須加以中和。 利用補充水調整其ΡΗ值下降’因其水量僅約循環系統 之5%- 1 0%,且水質淨化、降低1)11值所須添加酸性劑量較少 ,且在注入循環流程後’可與原來循環水混合中和,不必 作連續性之注入調整’故具有可行性。 通常中和所須之酸驗量=pH濃度X流ϊ。 對循環水中和所需酸鹼之流量: (ρ Η = 8時)4倍X Q c (Q c :冷卻水循環流量) 對補充水降低PW需酸流量: (p Η = 5時)8倍X Q m (Q πι:補充水流量) 因Qc約為Qm之1 0-20倍,故即使降低補充水中PH值至5 時,所需使用酸量仍低於中和循環冷卻水pH所需之酸量’ 基本上仍屬可行。 臭氧水在低pH值時,溶解率、飽和濃度及結合成為氫 氧自由基之比例均提高,相反地〇 3自行分解率則降低’高 濃度、高效能之0水便可在短時間形成。 2 .臭氧水中之水溫 水溫對溶解0 3、飽和0濃度及氫氧自由基之形成’隨 溫度上升而低減,相反地0A自行分解率’則隨溫度上升1. pH 452640 in ozone water V. Description of the invention (40) The dissolution rate and saturation dissolution rate of ozone are better with a low P 丨 丨 value, and hydrogen radicals are also more likely to exist in acidic solutions. Conversely, 0 3 self-decomposes The rate 'logarithmically increases with the rise of pH value', so the solution is dissolved and hydrolyzed at 0 celsius, and its pH should preferably be low during the reaction. 'Because the pH value of the cooling water is at high temperature,' the acidic components are prone to form gas overflows', so it is high plHt, which must be neutralized over time. Use make-up water to adjust its pH value drop 'because its water volume is only about 5%-10% of the circulation system, and water purification, reducing 1) 11 value, less acid doses must be added, and after injection into the circulation process' can be linked with It turns out that the circulating water is mixed and neutralized, and there is no need to make continuous injection adjustments, so it is feasible. Usually the acid test required for neutralization = pH concentration X flow. For circulating water and the required acid-base flow rate: (when ρ Η = 8) 4 times XQ c (Q c: cooling water circulation flow rate) For make-up water to reduce PW acid flow: (p Η = 5) 8 times XQ m (Q πι: make-up water flow) Because Qc is about 10-20 times of Qm, even when the pH value of make-up water is reduced to 5, the amount of acid required is still lower than the amount of acid required to neutralize the pH of the circulating cooling water 'Basically still feasible. At low pH, the ozone water has a higher dissolution rate, saturation concentration, and the proportion of oxygen radicals that are combined. On the contrary, the 03 self-decomposition rate decreases, and high-concentration, high-efficiency 0 water can be formed in a short time. 2. Water temperature in ozone water Water temperature has a dissolution 0 3, saturation 0 concentration and the formation of hydrogen and oxygen radicals ’decreases with increasing temperature, on the contrary, 0A self-decomposition rate’ increases with temperature
第43頁 452640 五、發明說明(41) 而加快,根據實証約每升高溫度1 0°C,自行分解率便增加 一倍,冷卻循環之回流水,其溫度通常在5 0°C - 7 0°C間, 對0兩言是極為不利,一般補充水之水溫約在1 5°C至2 5°C ,準此,在補充水中之0瘩存效果,與在循環回流水中之 0擦存效果相比,亦數以倍計,由於回流循環水之流量大 ,冷卻不易,所付出代價高,通常不作加以冷卻之考慮, 但若以M A K E - ϋ P補充水之水量而言,僅及循環水量之5 % -1 0 %,即使為降低溫度,所付出之能源亦相對降低。 3 . 0水中之反應物質 在進行0瘩解及水反應時,除自行分解以外,尚有因 反應而需耗用0蘆,這些反應對象物,隨成分、濃度而有 不同之變動,很難掌握,以用途目的而言,冷卻循環水之 0處理,主要對象為殺菌、滅藻,必須維持某一濃度以上 之劑量才具效果,且可縮減其接觸時間至秒計,由於回流 水中所含反應物較多,會耗用部份0 3,而使注入0產必須 包括此反應耗用量部份而提高,本法0水係以潔淨之補充 水為溶解對象,水中所含反應成分低,耗用0蘧十分有限 ,且大抵安定,因此能以必要之濃度直接處理,因0象殺 菌、滅藻功能最快,耗量最少,故在維持高濃度下便能迅 速完成。 4. 0冰沖淋消毒水量 為維持冷卻水塔中之水理分佈,而取得0與反應物質 之充分接觸,因此作為殺菌、滅藻之0水流量,不宜低於 循環冷卻之流量,就一般而言,補充水流量約為1 5%-20%P.43 452640 V. Explanation of the invention (41) It is accelerated. According to the empirical evidence, the self-decomposition rate doubles for every 10 ° C increase in temperature. The temperature of the reflux water in the cooling cycle is usually 50 ° C-7 Between 0 ° C, it is extremely detrimental to 0. Generally, the temperature of the supplementary water is about 15 ° C to 25 ° C. Therefore, the effect of 0 in the supplementary water and 0 in the circulating reflux water Compared with the wiping effect, it is also several times. Because the flow of returning circulating water is large, cooling is not easy, and the cost is high, it is usually not considered as cooling. However, in terms of the amount of make-up water, only And the amount of circulating water is 5% -10%, even if the temperature is reduced, the energy cost is relatively reduced. 3.0 When reacting substances in water are decomposed and reacted with water, in addition to self-decomposition, there is still a need to consume 0 reeds due to the reaction. These reaction objects vary in composition and concentration, which is difficult. Master, for the purpose of use, the zero treatment of cooling circulating water is mainly for sterilization and algae killing. It must maintain a dose of a certain concentration or higher to have an effect, and it can reduce its contact time to seconds. Due to the reaction contained in the reflux water, There are more materials, which will consume part of the 3, and the injection of 0 must include the reaction consumption part to increase. The water of this method uses clean supplemental water as the dissolution object, and the water contains low reaction components. Consumption of 0 蘧 is very limited, and it is stable, so it can be processed directly at the necessary concentration. Because 0 elephant has the fastest sterilization and algae killing functions and the least consumption, it can be quickly completed under high concentration. 4. The amount of 0 ice shower disinfection water is to maintain the hydraulic distribution in the cooling water tower, and to obtain the full contact between 0 and the reacting substances. Therefore, the 0 water flow rate for sterilization and algae killing should not be lower than the circulating cooling flow rate. In other words, the make-up water flow is about 1 5% -20%
第44頁 d526 d 0 五、發明說明(42) ,但若集中於1 Ο - 2 0分鐘内,則其流量可達經常冷卻循環 水流量以上,故就水理而言亦屬可行。 5 . 0表腐触性 0為強氧化劑,自然具有高度之腐蝕性,在乾燥氣體 中,0夂腐蝕性有限,但若與水分結合便會成為高腐蝕性 ,而在水溶液中其腐蝕性更強,因此在接觸0氣體或0水 溶液之物料,其材質一般以不銹鋼或塑膠、木材等耐蝕性 材質為宜。 0具有自行分解之特性,因此若能假以時間,則0周 自行分解為0 2,而使其腐蝕能力減低,因而在一流程中, 〇 3會隨時間_而遞減其濃度,一般而言在脫離子之中性純水 ,常溫常壓力下其半衰期(半減期)約為3 Ο Μ I Ν,當pH值為8 時,則半減期縮短為四分之一,溫度升高到4 5°C時,亦縮 短為四分之一,準此流程條件,則0炙半減期僅約在數十 秒到數分鐘以内,殘存0濃度大幅下降,其腐蝕能力亦隨 之降低。 以上所探討者均為在純水中,無反應狀況所產生之自 行分解效,在實際處理流程中,則有許多雜質成分會消耗 0 3,從耗用低、時間短之殺菌、滅藻、脫臭、脫色及與氧 化物形成競爭,氧化分解至耗用量大、時間長之COD,均 可能耗用許多溶存0 3,或其所轉化之氫氧自由基,因此殘 存0濃度是隨流程之反應而銳減,腐蝕能力亦相對減少。 腐蝕程度與腐蝕性及接觸時間有關,若時間短則其腐 蝕效應有限,即使具有高腐蝕性溶液,若僅在短時間内使Page 44 d526 d 0 V. Description of the invention (42), but if it is concentrated within 10-20 minutes, the flow rate can reach above the regular cooling circulating water flow rate, so it is also feasible in terms of hydraulics. 5.0 Table 0 Corrosiveness 0 is a strong oxidant and naturally has a high degree of corrosiveness. In dry gas, 0 夂 is limited to be corrosive, but it will become highly corrosive if combined with moisture, and it is more corrosive in aqueous solution. Strong, so in contact with 0 gas or 0 water solution materials, the material is generally stainless steel or plastic, wood and other corrosion-resistant materials are suitable. 0 has the characteristics of self-decomposition, so if time can be assumed, 0 weeks will decompose to 0 2 by itself, which will reduce its corrosion ability. Therefore, in a process, 〇3 will decrease its concentration with time _, generally speaking In deionized neutral pure water, its half-life (half-life) is about 3 OM I N under normal temperature and pressure. When the pH value is 8, the half-life is shortened to one quarter and the temperature rises to 4 5 At ° C, it is also shortened to a quarter. Under this process condition, the zero-burning half-life is only about tens of seconds to several minutes, and the residual 0 concentration is greatly reduced, and its corrosion ability is also reduced. Those discussed above are all self-decomposing effects in pure water without reaction. In the actual processing process, many impurities will consume 0.3. From low consumption, short time sterilization, algae elimination, Deodorization, decolorization, and competition with oxide formation, oxidative decomposition to COD with large consumption and long time, can consume many dissolved 0 3, or its converted hydroxyl radicals, so the residual 0 concentration is with the process The response decreases sharply, and the corrosion capacity is relatively reduced. The degree of corrosion is related to the corrosiveness and contact time. If the time is short, its corrosion effect is limited. Even if it has a highly corrosive solution, if it is used only for a short time,
第45頁 4 5 2 6 ^-0 五、發明說明(43) 用,不僅對接液材料(WET PART)不太有影響,且可能對於 表面附著物,如水垢、鐵垢具有袪除之作用,例如一般常 使用鹽酸、硫酸、苛性鹼等高腐蝕性液體,作為表面洗淨 或管路沖洗之用,故若能掌握時間,則不僅非有害物質, 反而更有助於附著物之接除。 6 . 0 A毒性 0具有毒害性,但由於0是過渡性存在之氣體,並非 如一般毒性藥劑般有累積濃度之現象,且以抑制細胞中 D N A,造成不活化性為主要機制,故在未達到不活化性濃 度以前,即使時間再長亦無殺菌作用,而在達到不活化性 最高濃度以上時,即使再提升其濃度或延續其時間,其實 亦無發揮之空間,因此在學理上所謂濃度時間值,實際乃 是在開始具有不活化性抑制作用之濃度開始,至不活性最 高濃度時之區間適用而已,通〇 ☆毒性與下列因素有關: (1) 0 A濃度。 (2 ) 0與對象生物持續接觸時間。 (3)生物所能承受之CT值。 由於0是被應用於殺菌、消毒、滅藻等用途,因而會 被聯想其對人類之毒害性,此種觀念與實際上有很大出入 ,因為對人體而言CT值在50 0 0x 6 = 30, 0 0 0 PPM—秒以内為 無害域,CT值在48, 0 00 PPM—秒- 6 0, 0 0 0 PPM—秒時為暫 時性毒害,若水中溶存0濃度在0. 12 mg/1,pH =7. 2時, VIRUS 1型不活化率99. 9%,所需時間約2分,換算CT值為 144 PPM—秒,相距非常大,而且目前產業界所產生之03Page 45 4 5 2 6 ^ -0 V. Description of the invention (43) Not only has little effect on the wetted material (WET PART), but also has the effect of removing surface attachments such as scale and iron scale. For example, highly corrosive liquids such as hydrochloric acid, sulfuric acid, and caustic are often used for surface cleaning or pipeline washing. Therefore, if time can be grasped, it will not only be non-harmful substances, but will also be helpful for removing attachments. 6. 0 A toxicity 0 is toxic, but because 0 is a transient gas, it does not have the phenomenon of cumulative concentration like ordinary toxic agents, and the main mechanism is to inhibit DNA in cells and cause inactivation. Before reaching the inactive concentration, there is no bactericidal effect even if the time is longer, and when it reaches the highest inactive concentration, even if the concentration is increased or continued, there is no room to play. Therefore, the so-called concentration is theoretically called The time value actually starts at the concentration that has the inactivation inhibitory effect, and the interval to the highest concentration of inactivity is applicable. The toxicity is related to the following factors: (1) 0 A concentration. (2) 0 continuous contact time with the target organism. (3) The CT value that the organism can withstand. Because 0 is used for sterilization, disinfection, algae killing, etc., it will be associated with its toxicity to humans. This concept is very different from the actual one, because the CT value of the human body is 50 0 0x 6 = 30, 0 0 0 PPM—seconds are harmless, CT value is 48, 0 00 PPM—seconds— 6 0, 0 0 0 PPM—seconds are temporary poisoning, if dissolved in water at a concentration of 0. 12 mg / 1, pH = 7.2, VIRUS Type 1 inactivation rate is 99.9%, the time required is about 2 minutes, the converted CT value is 144 PPM-seconds, and the distance is very large.
第46頁 A526^l〇 五、發明說明(44) 濃度,高值約在5 0,0 0 0 - 1 0 0 , 0 0 0 PPM之間經過空氣稀釋後 ,大抵不會超過1,000PPM (VOL/VOL),亦即在一般情況下 ,立即有所警覺而遠離,且因其會自行分解及反應,濃度 不大,至於注入流程中之使用濃度,通常在最高在數十 PP Μ以下,且立即溶解與反應,排放之0濃度幾乎低於 1 PPM,而當有0發生洩漏或排放濃度過高時,只要切斷電 源或調整發生量,則立即可化解,因此實際上並無毒害性 存在之事例,環境中之0濃度監測值為1 . Ο PPM,可以作 警示及控制之用,在過去因有0毐害性之質疑,便設置排 放0氨體分解裝置,如加熱分解、觸媒分解或活性炭吸附 等,但大多未曾使用過,因為即使環境中0濃度偏高,只 要假於時間任其散失及自行分解,亦可全數消除。 7. 0發生量 0發生量係依作流程處理時所需要0婢量,包括用於 有效反應量及無效損失量。 在一般連續性流體中,流程處理所需0通常以注入率 稱之,亦即相對於流量,在使用以冷卻循環回流水注入0 : 之傳統工法中,雖然不是以處理水質為對象,但為保持足 夠濃度,因此仍以注入率計算,而回流水則僅成為稀釋作 用,換言之若欲維持相同之水中0濃度,則發生0氨體量 與流量成正比,此乃是為何冷卻循環水為閉鎖性流路,在 進行0處理時,須要大容量之0發生量之重要原因,依本 工法前述0 #進行消毒作用所須之流量而言,其流量僅為 冷卻循環水之0 . 2 - 0 . 5之間,亦即0發生量可以降低至0 . 2A526 ^ l0 on page 46 V. Description of the invention (44) Concentration, the high value is about 50, 0 0-1 0 0, 0 0 0 After dilution with air, it will probably not exceed 1,000 PPM ( VOL / VOL), that is, in general, immediately alert and stay away, and because it will decompose and react on its own, the concentration is not large. As for the concentration used in the injection process, it is usually below a few tens of PP Μ, And immediately dissolve and react, the zero concentration of emissions is almost less than 1 PPM, and when there is zero leakage or the concentration of emissions is too high, as long as the power is cut off or the amount is adjusted, it can be resolved immediately, so it is actually not toxic Existing examples, the monitoring value of 0 concentration in the environment is 1. 0 PPM, which can be used for warning and control. In the past, due to the question of harmfulness, a 0 ammonia emission decomposition device was set up, such as thermal decomposition, contact Media decomposition or activated carbon adsorption, but most of them have never been used, because even if the 0 concentration in the environment is high, as long as it is allowed to dissipate and decompose by itself, it can be completely eliminated. 7. Occurrence of 0 Occurrence of 0 is the amount of 0% required for processing according to the process, including the amount of effective reaction and the amount of invalid loss. In general continuous fluids, the 0 required for process processing is usually referred to as the injection rate, that is, relative to the flow rate. In the traditional method of injecting 0: with cooling circulating reflux water, although it is not intended to treat water quality, it is Maintain a sufficient concentration, so it is still calculated based on the injection rate, and the return water only serves as a dilution effect. In other words, if the 0 concentration in the same water is to be maintained, the amount of 0 ammonia is proportional to the flow rate. This is why the cooling circulating water is blocked. For the sex flow path, when the 0 treatment is carried out, an important reason for the large volume of 0 generation is required. According to the flow required for disinfection in the aforementioned 0 # of this construction method, the flow is only 0.2 to 0 of the cooling circulating water. Between 5, that is, the amount of 0 can be reduced to 0.2
第47頁 d5264〇 五、發明說明(45) -0 . 5之間。 另一方面,由於高濃度0水注入法之溶解率、氫氧自 由基產生率提高,而自行分解及反應耗減量均降低,其利 用率與回流水注入方式相較,數以倍計,因此所需〇氣體 量更為低減,此乃本工法之特色。 8. 0水之流量 在冷卻水塔中之液體為非連續性流體,其滴落速度是 受重力及空氣阻力之作用與壓力,冷卻水塔之水平斷面之 關係,不適用匣限之連續性流體,換言之在水塔内流量與 水滴粒徑、間隔有關係,而冷卻水塔内所需處理者,並非 氣體空間,而是附著於構造物上之污雜物,或以構造物為 介質之生物膜為對象,因此只要0 #滴能與塔内固定物踫 撞接觸,便可產生浸潤之功能,與冷卻水與大氣接觸進行 熱交換者有別,故用於沖淋附著於構造物之0冰流量需求 不大,(只要滴流間隔時間不過長即可,與水滴粒徑影響 不大),因而0水之流量大約在冷卻循環水1 0 - 3 0 %即可。 池底之懸浮、棲居微生物、細菌、藻類等,因匯流後 轉型為連續流體,其停留時間受到流量影響,在相同體積 中,降低流量可延長停留時間,使接觸反應更為完全。 综上所述,本發明,係依據冷卻循環水系統中,冷卻 水塔中之水理特性,補充水、中和劑、排放水及砂滤槽等 ,有別目前在冷卻水塔底槽所作,分流連續式0痒入處理 方式(continue on-line 0 3 injection method),構成一 種適合0處理之流程系統。 Λ 6 2 6 4- Ο 五、發明說明(46) 本發明具有下列之特點與效益: 1 .冷卻水塔内部之0處理更為徹底。 (1 )配合冷卻水塔内滴落及匯流水理應用,0處理 用水量少。 (2 )高濃度0水,含高比例氫氧自由基,效能強、 反應快速完成,耗用量少。 〔3 )處理時間短,影響正常運作低。 2. 氣相0轉化溶存0 #比率高。 (1 )低pH值、低水溫,促進溶解率,減低自行分解 率。 (2 )補充水反應物少,耗損0 J:少。 (3 )適當水深及停留時間之溶解槽,增進接觸溶解 反應效果。 3. 生物處理功能發揮,淨化水質。 (1 )結合砂濾設備,介質生物膜之產生,提升高度 淨化能力。 (2 )強制性殺滅菌藻,氧化剝落生物膜,抑止巨積 塊體出現,化解生物機制之困擾。 (3 )逆洗砂床併用移除殘骸。 (4 )周期性歸零安全可靠。 4. 對設備腐蝕作用少,具有表面除銹垢功能出現。 (1 )冷卻水塔處理後,〇濃度便迅速降低,對冷卻 設備之腐蝕作用降低。 (2 )處理時間在十數分鐘以内,非連續性,僅及表Page 47 d5264〇 5. Description of the invention (45)-0.5. On the other hand, because the high-concentration 0-water injection method improves the dissolution rate and the generation rate of hydroxyl radicals, the self-decomposition and reaction consumption are reduced. Compared with the reflux water injection method, the utilization rate is several times, so The amount of gas required is even lower, which is a feature of this construction method. 8. The flow rate of water The liquid in the cooling water tower is a discontinuous fluid. Its dropping speed is affected by the effect of gravity and air resistance and pressure, and the relationship between the horizontal section of the cooling tower. In other words, the flow in the water tower has a relationship with the particle size and spacing of the water droplets. The processor in the cooling water tower is not a gas space, but a dirt or debris attached to the structure, or a biofilm with the structure as the medium. Object, so long as the 0 #drop can collide with the fixed object in the tower, it can produce the function of infiltration. It is different from the heat exchange between the cooling water and the atmosphere, so it is used to shower the ice flow attached to the structure. The demand is small (as long as the drip interval is not too long, and it has little effect on the particle size of the water droplets), so the flow of 0 water can be about 10-30% of the cooling circulating water. The suspension, inhabiting microorganisms, bacteria, algae, etc. at the bottom of the pond are converted into continuous fluids after confluence, and their residence time is affected by the flow rate. In the same volume, reducing the flow rate can extend the residence time and make the contact reaction more complete. In summary, the present invention is based on the hydrological characteristics of the cooling water tower in the cooling circulating water system, supplementary water, neutralizer, drainage water and sand filter tank, etc. The continuous on-line 0 3 injection method constitutes a process system suitable for 0 processing. Λ 6 2 6 4- 〇 5. Description of the invention (46) The invention has the following features and benefits: 1. The 0 treatment inside the cooling water tower is more thorough. (1) Cooperating with dripping and converging hydraulic application in cooling water tower, the water consumption of 0 treatment is small. (2) High-concentration 0-water, containing a high proportion of hydroxyl radicals, strong performance, rapid reaction completion, and low consumption. [3] The processing time is short and the influence on normal operation is low. 2. Gas phase 0 conversion and dissolved 0 # ratio is high. (1) Low pH and low water temperature, promote dissolution rate and reduce self-decomposition rate. (2) There are few reactants in the make-up water, and the loss is 0 J: less. (3) Dissolution tank with proper water depth and residence time to improve the effect of contact dissolution reaction. 3. Biological treatment function is exerted to purify water quality. (1) Combined with sand filtration equipment, the production of media biofilms improves the high purification capacity. (2) Mandatory sterilization of algae, oxidative peeling of biofilm, inhibiting the appearance of macroblocks, and dissolving the problems of biological mechanisms. (3) Backwash the sand bed and use it to remove the debris. (4) Periodic return to zero is safe and reliable. 4. It has less corrosion effect on the equipment, and has the function of surface rust removal. (1) After the cooling water tower is processed, the concentration of 0 is rapidly reduced, and the corrosion effect on the cooling equipment is reduced. (2) The processing time is less than ten minutes.
第49頁 d 5 2 B 4 Ο 五、發明說明(47) 面,不致侵蝕結構物裡部。 (3 )長時間運作所累積之水垢、銹垢等表面附著, 可以利用短時間0處理而清除。 5.充分利用資源,不必另設或增加,尚可節約用水。 (1)以補充水作為0瘩解用水,以中和用酸劑降低 ρ Η值。 (2 )利用B L 0 W D 0 W Ν之水,作為砂濾床逆洗及移除 污雜物之用。 (3)使用生物膜淨化作用改善水質,減少劣質水排 放量。 6 . 0离求容量小,初期投資節省。 (1) 提高氣相0瘩解率,提能轉化效率。 (2 )以含高比例氫氧自由基之高濃度0處理,效能 高、時間短、耗用量少。 (3 )處理用水量低減,所須注入量減少。 7 . 0處理期間短,運轉費低。 (Ο高濃度0處理所需時間極有限。 (2 )周期性批次處理,每周期僅作一次短時間處理 〇 (3)配合生物膜處理周期,周期時間長,實作操作 時間比例小。 8.處理時段具選擇性,操作方便尚可節省能源。 (1 )周期中處理選定,以配合製程作業上之需求。 (2) 夜間溫度低,利於0濃度維持,冷卻用水需求Page 49 d 5 2 B 4 〇 5. Description of the invention (47) surface, will not erode the inside of the structure. (3) Surface deposits such as scale and rust accumulated during long-term operation can be removed with a short time of 0 treatment. 5. Make full use of resources, no need to set up or increase, still save water. (1) Use make-up water as 0 dehydration water, and reduce ρ Η value with neutralizing acid. (2) Use B L 0 W D 0 W Ν water for backwashing of sand filter bed and removal of dirt. (3) Use biofilm purification to improve water quality and reduce inferior water discharge. 6.0 small capacity, small initial investment savings. (1) Increase the gas phase 0 decomposition rate and increase the energy conversion efficiency. (2) Treated with a high concentration of 0 containing a high proportion of hydroxyl radicals, with high efficiency, short time, and low consumption. (3) The amount of treatment water is reduced and the required injection volume is reduced. 7.0 The processing period is short and the running cost is low. (0 high concentration 0 processing time is extremely limited. (2) Periodic batch processing, only one short time treatment per cycle. 0) (3) In combination with the biofilm processing cycle, the cycle time is long and the actual operating time proportion is small. 8. Selective processing time, convenient operation and energy saving. (1) The processing selection in the cycle to meet the needs of the process operation. (2) Low night temperature, which is beneficial for maintaining 0 concentration and cooling water requirements.
第50頁 4526^0 五、發明說明(48) 減少。 (3 )利用離峰時間運作,節省電力成本。 9.毒害性降低。 (1 ) 0轉換溶存0此例高、排放率少。 (2 )在低溫、低ρ Η值中運作,外戌量小。 (3 )充分反應,殘餘溶存0 #少。 (4 ) 0 #生量小、總量小、易散化。 (5 )運作時間短,危害性有限。 1 0 .控制操作簡便,自動化容易。 (1) 不受流量、水質、水溫、pH值變化影響。(獨 立處理系統運作而調整注入率) (2) 各種參數均可採用設定量操作,不必作變數調 整。 (3) 可以利用定時、連動等簡易控制達到自動化。 11.設置費低。 (1)需要0產生裝置容量減小。 (2 )配合設施,僅溶解槽及管路。 (3 )改裝部份不多且容易,既設與新設均適合應用 ΰ 1 2 .運作費用節省。 (1)大多為原來必備之設施,不會增加操作費。 (2 ) 0祠量少、時間短、動力費少。 (3 )節省水資源之消耗。 (4) 簡易可速成自動化,節省操作人力。P.50 4526 ^ 0 V. Description of the invention (48) Reduced. (3) Use off-peak time operation to save electricity costs. 9. Reduced toxicity. (1) 0 conversion and storage 0 This example is high and the emission rate is small. (2) Operation at low temperature and low ρ Η value, and small external 戌 amount. (3) Fully reacted with less residual 0 #. (4) 0 # The amount of production is small, the total amount is small, and it is easy to disperse. (5) Short operating time and limited hazards. 10. Control operation is simple and easy to automate. (1) Not affected by changes in flow, water quality, water temperature, and pH. (Injection rate is adjusted by independent processing system operation) (2) Various parameters can be operated with set amount, and no adjustment of variables is required. (3) Simple controls such as timing and linkage can be used to achieve automation. 11. Low setup fee. (1) It is necessary to reduce the capacity of the generating device. (2) Cooperate with facilities to dissolve tanks and pipes only. (3) There are not many modification parts and it is easy. Both existing and new installations are suitable for application. Ϋ́ 1 2. Operation cost savings. (1) Most of them are originally necessary facilities and will not increase operating costs. (2) 0 temples are small in amount, short in time, and low in power costs. (3) Save water consumption. (4) Simple and quick automation, saving manpower.
第51頁 五、發明說明(49) 1 3 .習知技術之應用,容易實行。 (1 ) 0在水中之溶解技術。 (2) 0撒菌、滅藻、脫色、脫臭、氧化,統括反應 處理。 (3 )冷卻水塔佈水接觸。 (4 )介質生物膜,生成淨化處理。 (5 )砂濾之逆洗技術。 以上實施例的敘述係為解說及描述本發明的目的而表 達,其無意道盡或限制本發明為被敘述的明確形式;並且 ,基於以上的教導或從本發明的實施例而學習,顯然地許 多修改或變化是可能的。該實施例的選擇係為最清楚地解 釋本發明的原理及其實際應用,俾使本技藝之其他人士對 合適的特定使用意圖以各種實施例及以各種修改最有效地 利用本發明。本發明的技術思想企圖由下列的申請專利範 圍及其均等來決定。Page 51 V. Description of the invention (49) 1 3. The application of conventional technology is easy to implement. (1) Dissolution technology in water. (2) 0 Spread bacteria, kill algae, decolorize, deodorize, and oxidize, and integrate reaction treatment. (3) The cooling water tower is in contact with water. (4) a medium biofilm to generate a purification process. (5) Backwashing technology of sand filtration. The descriptions of the above embodiments are expressed for the purpose of explaining and describing the present invention, and they are not intended to limit or limit the present invention to the definite forms described; and, based on the above teachings or learning from the embodiments of the present invention, obviously Many modifications or changes are possible. This embodiment was chosen to most clearly explain the principles of the invention and its practical application, so that others skilled in the art may use the invention most effectively in various embodiments and with various modifications for the appropriate specific use intent. The technical idea of the present invention is determined by the following patent application scopes and their equivalence.
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Cited By (3)
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TWI386616B (en) * | 2006-11-03 | 2013-02-21 | Nalco Co | Improved method for chemistry control in cooling systems |
TWI422531B (en) * | 2011-05-02 | 2014-01-11 | ||
CN109205761A (en) * | 2017-06-30 | 2019-01-15 | 上海轻工业研究所有限公司 | The recirculating cooling water system and ozone the controlling of injecting quantity device and method of ozone treatment |
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Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
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TWI386616B (en) * | 2006-11-03 | 2013-02-21 | Nalco Co | Improved method for chemistry control in cooling systems |
TWI422531B (en) * | 2011-05-02 | 2014-01-11 | ||
CN109205761A (en) * | 2017-06-30 | 2019-01-15 | 上海轻工业研究所有限公司 | The recirculating cooling water system and ozone the controlling of injecting quantity device and method of ozone treatment |
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