JP2006043670A - Cleaning method using hyperfine bubble - Google Patents
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A20/00—Water conservation; Efficient water supply; Efficient water use
- Y02A20/124—Water desalination
- Y02A20/131—Reverse-osmosis
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- Separation Using Semi-Permeable Membranes (AREA)
Abstract
Description
本発明はRO膜、MF膜、UF膜、イオン交換膜およびイオン交換樹脂等への付着抑制や付着異物の剥離回復操作を必要とする広い分野に有効に適応可能である。 The present invention can be effectively applied to a wide range of fields that require adhesion suppression to RO membranes, MF membranes, UF membranes, ion exchange membranes, ion exchange resins, and the like, and peeling recovery operation of adhered foreign substances.
水処理に適応する分離膜の洗浄方法には化学洗浄と物理洗浄がある。化学洗浄としては塩酸,硝酸、リン酸、次亜塩素酸ソ−ダ−などの無機酸と修酸、クエン酸などの有機酸が使用される。
物理洗浄としては加圧空気を膜面に吹き込むエスクラアビング法と膜の裏側から水を逆さに押し出す水逆洗法、高圧エア−(0.6MPa)で逆洗する空気逆洗法があり、これらは並行して実施される場合が多い。Separation membrane cleaning methods suitable for water treatment include chemical cleaning and physical cleaning. For chemical cleaning, inorganic acids such as hydrochloric acid, nitric acid, phosphoric acid and soda hypochlorite and organic acids such as oxalic acid and citric acid are used.
As physical cleaning, there are an escrabing method in which pressurized air is blown into the membrane surface, a water backwash method in which water is pushed backward from the back side of the membrane, and an air backwash method in which backwashing is performed with high-pressure air (0.6 MPa). These are often performed in parallel.
通常、物理洗浄は20〜60分毎に実施される。また、化学洗浄は1〜3ケ月に実施されるが、使用した薬品が廃液として多量に排出され、その処分が問題となる、化学洗浄、物理洗浄とも分離膜面表面に蓄積した汚染物質をとり除いて膜透過性能を回復維持する目的で実施する訳であるが、付着物が完全に回復しない場合がある。
各々の分離機能を付与させた膜種にて、許容できる付着異物の蓄積度の影響は異なり、供給させる対象液の中に溶存する物質の溶解状態で、接触膜面に与える影響度が異なると同時に、膜の近辺の溶液は、接近する膜保持構造の荷電状況の影響を受けて、膜表面への付着、吸着強度は複雑に変化して、離れ難くなる可能性も十分にある。 The influence of the accumulation degree of adhering foreign matter that can be tolerated differs depending on the membrane type to which each separation function is given, and the influence on the contact membrane surface differs depending on the dissolved state of the substance dissolved in the target liquid to be supplied. At the same time, there is a possibility that the solution in the vicinity of the membrane is affected by the charge state of the approaching membrane holding structure, and the adhesion and adsorption strength to the membrane surface changes in a complex manner and becomes difficult to separate.
この様な付着物を剥離させるために必要とすうエネルギ−は、化学薬品を供給し、付着物を膨潤させるなどの濃度調整をするなどで、物理変化を起こさせことで、付着異物溶解促進させるなどの効果により、膜面および補助構造材質面よりの剥離操作を可能にするのが定法であるとされてきた。
しかし、問題点は剥離目的の付着異物の膨潤性を得られる薬物組成と、分離膜を構成する素材の変質、または表面機能構造の破壊などを配慮すると、効果的な薬剤を適応し難い、更には、分離膜の構成素材との親和性が強く、薬剤の流出洗浄性が悪いなどの配慮事項などが絡み、付着異物の洗浄剥離効果のみの配慮だけではなく、複雑に絡まった問題点も多く、特に、薬品洗浄後の分離膜の内部に浸透した薬剤の流出、置換操作と操作後の作業洗浄液の処分操作が問題に成っている。 However, the problem is that it is difficult to apply an effective drug, considering the drug composition that can swell the adhered foreign material for the purpose of peeling, the alteration of the material constituting the separation membrane, or the destruction of the surface functional structure. Has a strong affinity with the constituent materials of the separation membrane and involves considerations such as poor drug outflow detergency. In particular, the outflow and replacement operation of the drug that has permeated into the separation membrane after the chemical cleaning, and the disposal operation of the working cleaning liquid after the operation are problematic.
そこで、これらの化学薬剤の添加効果の助けに依存する手法が持つ数々の難点を補う為に、より幅広い分離膜に共通に適応できる剥離操作を見つけ出そうとする動きで、分離膜面と付着異物とで形勢される異なる複雑な結合力、を考慮して幅広い分野に共通する引き離し効果を発揮させるためには、非常に狭い間隙に浸透して、より弱い結合で結びついた結合点を引き離すことで、除々小さい範囲の結合点を集中することで、徐徐に崩壊点を拡大し、周辺への影響を回避出来る手法を採用させる事が出来れば、理想的な解決方法と判断される。 Therefore, in order to compensate for the many difficulties of the methods that depend on the help of the addition effect of these chemical agents, the movement to find a separation operation that can be commonly applied to a wider range of separation membranes, In order to exert the separation effect common to a wide range of fields in consideration of the different complex bonding forces formed by, by penetrating into a very narrow gap and separating the bonding points connected by weaker bonds, If a method that can gradually expand the collapse point and avoid the influence on the surroundings by concentrating the coupling points in a small range gradually, it is judged as an ideal solution.
本発明によると湿式系の分離機能膜の表面での本来の分離操作の続行により、異物の付着物の累積により、本来の分離膜機能が持つべき特性が汚染されて性能低下した場合、気体の溶解した溶液の爆裂分散操作により作り出される超微細気泡が発揮する吸着効により、膜面上に付着する汚染物に付着し剥離することで洗浄効果が得られ、その洗浄廃液には薬剤を含まず、廃液処理の必要も無いという利点がある。
そのためには、水に気体を超微細な独立した気泡として連続的に作成し、補給する手法が適応できるならば、この様な超微細な独立気泡の表面には、高密度の荷電子蓄積され、マイナスイオン荷電を帯びてくることが知られており、狭い間隙に浸透し易くなり、特に付着面(ぬれて居ない領域はプラスに荷電していると判断されている)に浸透し、供給する微細気泡の表面が持つ逆帯電(マイナス)量で中和しながら、完全に濡らすこと(マイナス荷電下に変化)での剥離効果を発揮することが期待されている。
具体的には、汚れた領域に微細気泡水を補給すると、初期には汚染領域の端部よりは、微細気泡水は流出せず、気泡が全く含まない液が流出するが、除々成長した、会合した大きく成長した気泡を含む液が流出し、さらに除々に粒子が小さくなり、本来の注入した微細気泡が流出することで、発生していた差圧の減少とが合致した状況が生み出されていることが確認されている。According to the present invention, when the original separation operation on the surface of the wet-type separation function membrane is continued and the characteristics of the original separation membrane function are contaminated due to the accumulation of foreign substances, the performance of the gas is reduced. Due to the adsorption effect exhibited by the ultrafine bubbles created by the explosion dispersion operation of the dissolved solution, a cleaning effect is obtained by adhering to and peeling off contaminants adhering to the membrane surface, and the cleaning waste liquid does not contain chemicals There is an advantage that there is no need for waste liquid treatment.
For this purpose, if a method of continuously creating and replenishing gas in water as ultrafine independent bubbles and applying it can be applied, high-density charge electrons are accumulated on the surface of such ultrafine closed cells. It is known to be negatively charged, and easily penetrates into narrow gaps, and in particular penetrates and adheres to the adhering surface (areas that are not wet are judged to be positively charged). It is expected to exert a peeling effect by completely wetting (changing under negative charge) while neutralizing with the reverse charge (minus) amount of the surface of the fine bubbles.
Specifically, when replenishing the fine bubble water to the dirty area, initially the fine bubble water does not flow out from the end of the contaminated area, but the liquid containing no bubbles flows out, but gradually grows. The liquid containing the large bubbles that have grown together flows out, and the particles gradually become smaller, and the original injected fine bubbles flow out, creating a situation that matches the reduction in the differential pressure that was generated. It has been confirmed that
従って、供給微細気泡の含まれる濃度が高い程、汚染された領域の回復は速いが、その汚染度に応じては、薄い濃度の気泡水を、長時間供給することで、同様な効果があることも確認されていることより、付帯させる設備の増大化、運転に係わる消費電力の増大を避けるためにも、時間を掛けた中和作業でも同様な効果が認められている。 Accordingly, the higher the concentration of the supplied fine bubbles, the faster the recovery of the contaminated area is. However, depending on the degree of contamination, the same effect can be obtained by supplying a low concentration of bubble water for a long time. In order to avoid an increase in incidental facilities and an increase in power consumption related to the operation, the same effect has been recognized in the neutralization work taking time.
この様な超微細気泡粒子を多濃度に、連続的に発生させる方法には、数々(超音波振動同調法、高圧衝撃衝突法、爆裂分散法等)の手法が考察されるが、どの様な手法を用いても、その系に存在する気泡粒子径が、より小さな粒子径領域を占める率が高くなる程、微細な間隙にまで浸透する効果を向上するとが想定される。
更に、狭い空間に浸透した気泡の表面荷電の中和による気泡の会合、膨張破裂することで、固体面よりの剥離する力を生み出させる洗浄効果を生み出す。
他の剥離効果を生み出す手法に、外部よりの超音波の供給による気泡の破壊強度の調整などの可能性を組み合わせて剥離効果を補強させる手法などを付加す可能もある。Many methods (such as ultrasonic vibration tuning method, high-pressure impact collision method, explosion dispersion method) are considered as methods for continuously generating such ultrafine bubble particles at a high concentration. Even if the method is used, it is assumed that the bubble particle diameter existing in the system increases the ratio of occupying a smaller particle diameter region, so that the effect of penetrating into a fine gap is improved.
Furthermore, the bubble is associated with the surface by neutralizing the surface charge of the bubble that has penetrated into the narrow space, and the bubble is expanded and ruptured, thereby producing a cleaning effect that generates a peeling force from the solid surface.
It is also possible to add a technique for reinforcing the peeling effect by combining the possibility of adjusting the bubble breaking strength by supplying an ultrasonic wave from the outside to a technique for generating another peeling effect.
更に、この作業を水温を上昇させた温水環境下でも、気泡粒子の維持を制御出来れば、付着物の表面粘度を低下させて吸着力を低下させるとか、剥離をおこさせ易い環境下で の作業条件を選ぶことで操作効果を高めることも、重要な選択条件と言える。 Furthermore, if the maintenance of the bubble particles can be controlled even in a hot water environment where the water temperature is increased, the work can be performed in an environment where the surface viscosity of the deposits is reduced to reduce the adsorption power or the peeling is likely to occur. Increasing the operation effect by selecting conditions is also an important selection condition.
次に、実施例により本発明をさらに詳細に説明する。
原水を供給する高圧ポンプ〜例えば多段タ−ビンポンプを採用し、最も好ましくは、1.2Mpaち放出する能力を持ったポンプに連結した配管中に,金属板を交互に溶接させた衝撃剪断機能を保持した剪断器を設置し、この剪断器の前に溶解させるべき気体を圧入させて圧入水と気体とを同時に供給し、剪断器内で相互に接触させこの混合水を配管の端部に接合した圧力タンクに連結し、気泡混合液としてある時間を滞留し、経過後の完全なる飽和溶解水と過剰な気体成分とに分離させ、気体の過剰成分を連続的に付帯間の工作物を介して系外に排出させること考慮し、常に一定した加圧状態を維持して安定した発生気泡径の維持がなされる好ましい運転条件を維持させる配慮がなされる。Next, the present invention will be described in more detail with reference to examples.
A high-pressure pump that supplies raw water, for example, a multi-stage turbine pump, most preferably has an impact shearing function in which metal plates are alternately welded in a pipe connected to a pump capable of discharging 1.2 Mpa. Install a held shearer, press the gas to be dissolved before this shearer, supply the water and gas at the same time, contact each other in the shearer, and join this mixed water to the end of the pipe It is connected to the pressure tank, stays for a certain time as a bubble mixture, and is separated into completely saturated dissolved water and excess gas components after the passage, and the excess gas components are continuously passed through the work between the incidentals. Therefore, consideration is given to maintaining preferable operating conditions in which a constant pressurized state is always maintained and a stable bubble diameter is maintained.
一般に的に水に飽和させるための空気量は、液の温度、維持する加圧条件に伴い変化するが、体積比で判断すれば、大まかな水体積1:0.07〜0.11圧入気体体積比を目安に供給すれば、水温の変化があれども、ほぼ一定した過飽和度状態より生まれる微細な気泡成分重量濃度が180〜220ppm前後の気泡水濃度を供給することとなる。
この様に圧入水の圧力は、好ましくは0.6Mpa以上を保ち、更に好ましくは1Mpa前後を保ち、最も好ましくは1.2Mpa以上を保ち、更にこれらの圧力水に押し込める気体圧は少なくとも約1Mpa以上の高い圧力を維持した圧力タンクよりの安定した気体が注入されることが期待されている。
この圧力タンクの端部に接合した排出排出管には、吐出口の断面積と弁座と弁体で構成される特殊構造弁を採用することで、吐出口より弁座より吐出された圧力水はほぼ同一面積の弁座より瞬間に内部の高圧部より、外部の低圧部に吐出されることで、溶解していた気体成分は、圧力差のに応じて、溶解気体成分の爆裂沸騰を起こし、微細な気泡に成長して分散する。Generally, the amount of air to saturate with water varies with the temperature of the liquid and the pressurizing conditions to be maintained, but if judged by volume ratio, a rough water volume of 1: 0.07 to 0.11 intruded gas. If the volume ratio is supplied as a guide, even if there is a change in the water temperature, a bubble water concentration with a fine bubble component weight concentration of approximately 180 to 220 ppm produced from a substantially constant supersaturation state will be supplied.
Thus, the pressure of the injected water is preferably kept at 0.6 Mpa or more, more preferably around 1 Mpa, most preferably kept at 1.2 Mpa or more, and the gas pressure pushed into these pressure waters is at least about 1 Mpa or more. It is expected that a stable gas from a pressure tank that maintains a high pressure will be injected.
The discharge / discharge pipe joined to the end of this pressure tank employs a specially structured valve consisting of the cross-sectional area of the discharge port, the valve seat and the valve body, so that the pressure water discharged from the valve seat through the discharge port Is discharged from the internal high-pressure part to the external low-pressure part instantaneously from the valve seat of almost the same area, causing the dissolved gas component to explode and boil according to the pressure difference. , Grow into fine bubbles and disperse.
これらの操作で得られる気泡水中の気泡粒子径は、吐出操作時の押し込みポンプ圧力維持能力(タンク内圧と吐出爆裂弁の出口後の圧(外圧)との圧力差が大きい程、爆裂状況が噴出環境を決定する。
洗浄操作系の途中の工程では、洗浄対象の分離膜を経由することにより、入口での気泡径は膜面の狭い間隙を通過する過程にて、気泡同志の会合により成長させられるが次に設置された加圧調整の絞りバルブを経由することで、キャビテ−ション現象での気泡の破断により微細な粒子径に細分される可能性も生じる。The bubble particle size in the bubble water obtained by these operations is such that the greater the pressure difference between the indentation pump pressure during discharge operation (the pressure inside the tank and the pressure after the discharge explosion valve outlet (external pressure)), the more the explosion occurs. Determine the environment.
In the process in the middle of the cleaning operation system, the bubble diameter at the inlet is grown by the association of bubbles in the process of passing through the narrow gap on the membrane surface through the separation membrane to be cleaned. By passing through the pressure-adjusted throttle valve, there is a possibility that the fine particle size is subdivided due to the breakage of bubbles in the cavitation phenomenon.
更に、弁座と弁の接合面積が狭い程、接触時間が短い程、吐出水の速度が速く、飛散気泡が作る粒子径は小さな方向に移行すると想定されている。
しかし、最も重要な気泡径は、初段での分離気泡膜の間隙に進入する時の口径が小さい程、分離膜構造物の断面積方向に掛かる負荷圧が小さく、構造物の機械的な変形が少なく、通液抵抗の変化が少なく内部の狭い空間に滞留する気泡を追い出し親水化を促進する。Furthermore, it is assumed that the smaller the contact area between the valve seat and the valve and the shorter the contact time, the faster the discharged water speed and the smaller the particle size created by the scattered bubbles.
However, the most important bubble diameter is that the smaller the diameter when entering the gap of the separation bubble membrane in the first stage, the smaller the load pressure applied in the cross-sectional area direction of the separation membrane structure, and the mechanical deformation of the structure Less, changes in resistance to fluid flow are small, and air bubbles staying in the narrow space inside are expelled to promote hydrophilicity.
従って、通液系で微細気泡を発生させるための手法は、爆裂法で生成される気泡だけでなく、圧力配管を経る毎に変形する気泡径が大きく変形しても、この気泡の働きはその強度に変化することで、処理対象の分離膜構造の内部に存在する価値は認められていると判断されている。
また、これらの吐出弁は出来るだけ目的とする剥離洗浄操作する対象分離膜が格納されている容器が持つ炒る口に最も近い場所に設置させることが重要ないみを持つ。
吐出気泡水を、細い配管にて遠方にまで、引き延ばす操作を行うと、配管内で気泡同志が会合し、大きな気泡に成長し易いくなり、表面のマイナスイオンの荷電密度が低下して、本来の期待する特殊な荷電中和効果機能を失うこととなる。Therefore, the method for generating fine bubbles in the liquid flow system is not only the bubbles generated by the explosion method, but even if the bubble diameter deformed every time passing through the pressure pipe is greatly deformed, the function of these bubbles is It is judged that the value existing in the separation membrane structure to be processed is recognized by changing the strength.
In addition, it is not important to install these discharge valves as close as possible to the roasting mouth of the container in which the target separation membrane to be subjected to the separation cleaning operation is stored as much as possible.
If the operation of extending the discharged bubble water to a distance with a thin pipe is carried out, the bubbles will be associated with each other in the pipe, making it easier to grow into large bubbles, reducing the charge density of negative ions on the surface, It loses the special charge neutralization effect function expected of.
この問題点を回避させるためには、圧力を維持してきた吐出弁の元口までの配管距離を延ばし、対象膜の洗浄操作に際しては、格納容器に出来るだけ近い所に装填し、対象膜の洗浄操作に際しては、格納容器に出来るだけ近い所に吐出気泡水が直ちに洗浄対象の分離膜に速く接触出来る事を配慮すべく装填できると言える。
川水の前後の塩分濃度の工業用水の適応にも十分に共通された操作状況が得られる。In order to avoid this problem, the piping distance to the original port of the discharge valve that has maintained the pressure is increased, and when the target film is cleaned, it is loaded as close to the containment vessel as possible to clean the target film. In operation, it can be said that the discharged bubble water can be loaded as close as possible to the containment vessel so that it can immediately contact the separation membrane to be cleaned quickly.
Operational conditions that are sufficiently common to adaptation of industrial water with salinity before and after river water can be obtained.
脱塩操作の前処理として構造物の細間隙への入異物の流入による障害を回避するための防衛策として、数々の手法を適応してきたが、砂濾過では粗大粒子の流入は避けられず,より阻止精度を向上させる目的でMF膜などが適応され、粗大粒子は阻止さ避けられれたが微細なバクテリヤ成分(0.05〜0.5ミクロン)は通過して、より細かい分離径を持つ膜面に蓄積し、繁殖増大して問題点を増大した事象が数々現れ、これら微物の付着エネルギ−は大きく、化学薬品による変質では余計に取れ難くなる傾向にある。
この様なバクテリヤ質のタンパク質の汚染物に剥離条件は、強いアルカリ性が要求されるが、効果のある濃度、温度条件では、対象の分離膜を構成する素材おも侵してしまい、洗浄操作で本来の分離機能も失うと言う弊害を伴うことも、覚悟せざるを得ない可能性があることが、確認されている。A number of methods have been applied as defensive measures to avoid obstacles due to the inflow of foreign objects into the narrow gaps of structures as a pretreatment for desalination operations, but inflow of coarse particles is inevitable in sand filtration. For the purpose of improving the accuracy of inhibition, MF membranes are applied, and coarse particles are avoided and avoided, but fine bacterial components (0.05 to 0.5 microns) pass through and have a finer separation diameter. Many events that accumulate on the surface and increase the number of problems appear due to increased reproduction, the adhesion energy of these fines is large, and it tends to be difficult to remove by alteration by chemicals.
Peeling conditions for such bacterial protein contaminants are required to have strong alkalinity. However, under effective concentration and temperature conditions, the material constituting the target separation membrane will also be affected, and the cleaning operation will inherently It has been confirmed that there is a possibility that it may be necessary to be prepared to have the harmful effect of losing its separation function.
通常、逆浸透膜装置は長時間運転していると膜モジュ−ルの汚染により逆浸透膜装置の圧力損失が上昇する傾向があり、定期的に薬品洗浄を行って上昇した圧力損失の回復を図る必要があり、分離膜を用いた代表的なシステムを▲図1▼にしめす。
この薬品洗浄は膜モジュ−ルを汚染した付着物を化学薬品で溶解除去することを期待するものであるが、付着異物が各種の化学薬品で溶解しない場合がある。
▲図2▼に微細気泡によるRO膜ユニット洗浄時の配管経路を示す。
▲図3▼にRO膜装填した逆浸透操作時の機器配列図を示す。Normally, when the reverse osmosis membrane device is operated for a long time, the pressure loss of the reverse osmosis membrane device tends to increase due to the contamination of the membrane module. A typical system using a separation membrane is shown in FIG.
This chemical cleaning is expected to dissolve and remove deposits contaminating the membrane module with chemicals, but the adhered foreign substances may not dissolve with various chemicals.
Fig. 2 shows the piping path when the RO membrane unit is cleaned with fine bubbles.
FIG. 3 shows a device arrangement diagram during the reverse osmosis operation loaded with the RO membrane.
実施例1
河川水の一次砂濾過を用い、第二段目にカ−ト−リイジを保安濾過器として粗大粒子物を遮蔽、低圧操作逆浸膜透析操作による脱塩水の製造プロセスに適応させた。
この6ケ月経過後の操作時の操作差圧が、膜メ−カ−が提示する内部構造物の破損を誘発する危険変形圧力0.08Mpa/1エレメントに到達し、4本入りベッセルでは、0.34Mpa に迄増大したので通液操作を停止して、微細気泡水を用いた分離膜面に蓄積した付着異物による障害物の剥離流出操作を開始した。Example 1
The primary sand filtration of river water was used. In the second stage, the cartridge was used as a safety filter to shield coarse particles, and this was adapted to the desalted water production process by low pressure operation reverse dialysis membrane dialysis.
The differential pressure during the operation after the elapse of 6 months reaches a critical deformation pressure of 0.08 Mpa / 1 element that induces damage to the internal structure presented by the membrane manufacturer. Since the pressure increased to .34 Mpa, the liquid flow operation was stopped, and an operation of peeling and flowing out obstacles due to adhered foreign matter accumulated on the separation membrane surface using fine bubble water was started.
適応した洗浄対象の逆浸透膜脱塩設備は低圧操作型8インチエレメント×4エレメン/ベッセルのユニットの運転で、操作圧は0.8Mpaであり、透過生産水回収率は75%前後であり、供給河川濾過水量は5,800l/h,透過脱塩水量は4,000l/hr,ブライン水量は1,800l/hr(30l/min)の割り振りで運転されていたが、エレメント内での差圧の増大に伴い透過水量が低下して3,400l/hr(15%down)、差圧が0.34Mpaに増大した。 The reverse osmosis membrane desalination equipment to be washed is a low-
このことは、膜面に汚染異物の蓄積により、表面荷電による塩分蓄積量の除効果の低下による低圧膜特性が打ち消されたと言える。
従って、蓄積異物の付着は、機能膜の表面の荷電方向と荷電量により引きつけられてきた結果と判断すれば、微細気泡の表面に蓄えられた逆荷電量で中和剥離がなされるもと想定される。
微細気泡の発生装置は、多段タ−ビンポンプ1.5KW、到達圧力0.85Mpa発生水量58l/min前後であり、微細気泡の発生のための圧力空気は1.0Mpa×6.2L/minが供給されて、両者が衝撃混合して、吐出爆裂弁(30A)より噴出し、8インチエレメントの吐き出し弁の近くに設置した枝別れ配管より流入供給された。This can be said that the accumulation of contaminants on the membrane surface has counteracted the low-pressure membrane characteristics due to the decrease in the removal effect of the accumulated salt content due to surface charge.
Therefore, if it is judged that the adhesion of the accumulated foreign matter is a result of being attracted by the charge direction and the charge amount on the surface of the functional film, it is assumed that neutralization peeling is performed with the reverse charge amount stored on the surface of the fine bubbles. Is done.
The device for generating fine bubbles is a multi-stage turbine pump of 1.5 kW, an ultimate pressure of 0.85 Mpa of generated water amount of around 58 l / min, and the pressure air for generating fine bubbles is supplied at 1.0 Mpa × 6.2 L / min Then, both of them were impact-mixed, ejected from the discharge explosion valve (30A), and supplied and supplied from a branch pipe installed near the discharge valve of the 8-inch element.
供給開始の爆裂弁より押し込み液量は56l/minであり、8インチエレメントの断面流速としては0.17cm/minと低速な供給速度である(脱塩操作時0.12〜0.19cm/min)あるが、十分なる通液条件に近い送液速度での供給で約60min後には、送液抵抗が、0.0032Mpa/エレメントに迄で低下しており、4本全体では0.004Mpaまでに低下した。 The amount of liquid pushed in from the explosion start valve is 56 l / min, and the cross-sectional flow rate of the 8-inch element is 0.17 cm / min, which is a low supply rate (0.12-0.19 cm / min during the desalting operation). However, after about 60 minutes of feeding at a feeding speed close to a sufficient feeding condition, the feeding resistance drops to 0.0032 Mpa / element, and the total of the four pieces reaches 0.004 Mpa. Declined.
このことは、エレメントの洗浄操作が、薬品操作でなければ、付着物の剥離操作が出来ないのではなく、異物は荷電方向に異なる面に選択吸着されて、付着していると判断されるので、逆荷電の気泡水を供給することで、問題点の回避が可能となることが説明される。 This means that if the cleaning operation of the element is not a chemical operation, it is not possible to perform the peeling operation of the adhered matter, and it is judged that the foreign matter is selectively adsorbed and adhered to different surfaces in the charge direction. It is explained that the problem can be avoided by supplying the bubble water with the reverse charge.
上記のエレメントの汚れは、有機物汚染でのバクテリヤ汚染が中心であり、化学洗浄はタンパク質の変質収縮が先行して、逆に付着力が強まるなど効果的ではないが、敢えて、化学薬品で洗浄操作を試みようとあすると、先ず酸の1規定の硫酸液を1Lを薄めて流動させたが差圧は低下せず、1規定の可成曹達を供給しても低下しない。
更にこれらの薬品の供給後に、清浄水を100倍量を通液したが、洗浄水の示すpHは高く、膜面に付着したアルカリ成分の残留量が大きく、更に多大の洗浄水が必要なことを示していた。The contamination of the above elements is mainly due to bacterial contamination due to organic contamination, and chemical cleaning is not effective, such as protein denaturation and shrinkage, and on the contrary, the adhesion force is strengthened, but dare to clean with chemicals At first, 1 L sulfuric acid solution of acid was diluted and flowed by 1 L, but the differential pressure did not decrease, and it did not decrease even when 1 N sodium hydroxide was supplied.
Furthermore, after supplying these chemicals, 100 times the amount of clean water was passed, but the pH indicated by the wash water was high, the residual amount of alkali components adhering to the membrane surface was large, and a greater amount of wash water was required. Was showing.
1:原水 2:移送ポンプ 3:前段前濾過設備 4,濾過水貯槽
5:高圧ポンプ 6:脱塩膜分離ユニット 7:脱塩水槽
8:微細気泡発生装置 9:高圧移送ポンプ 10:コンプレッ−
11:加温/循環槽 12:爆裂分離弁1: Raw water 2: Transfer pump 3: Pre-stage filtration equipment 4, Filtrated water storage tank 5: High pressure pump 6: Desalination membrane separation unit 7: Desalination water tank 8: Fine bubble generator 9: High pressure transfer pump 10: Compressor
11: Heating / circulation tank 12: Explosion separation valve
Claims (7)
但し、この副水流と主水流との混合比は時間経過に伴い変更が可能であり、更に適合分離膜種によっては、副水流の注入操作を作動停止時間を間欠的に選択することで、主送液配管の操作圧力の変化とも組み合わせた管理操作を組み合わせ、適応分離膜面の振動作用などを加えることで、剥離機能が向上させることを特徴とするる洗浄方法。Pressurized sewage that enables generation of fine bubbles in which gas is dissolved is connected to the branched sub piping facility through a special valve to the main piping facility of the supply liquid of the main operation for separation operation. The liquid volume ratio of the mixture of the two at the connecting portion is intended to allow both liquids to be mixed uniformly while changing the ratio of the auxiliary water flow rate including air bubbles from 1: 0.1 to 20. Select the optimal mixing promotion equipment, and supply the mixed liquid in which the injected bubbles are uniformly dispersed in the pipe to improve the surface cleaning effect of the separation membrane to be treated. Is obtained.
However, the mixing ratio of this side stream and the main stream can be changed over time.Further, depending on the type of separation membrane used, the operation for stopping the injection of the side stream can be selected intermittently. A cleaning method characterized in that the separation function is improved by combining a management operation combined with a change in the operation pressure of the liquid supply piping and adding a vibration action of the adaptive separation membrane surface.
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| JP2012206025A (en) * | 2011-03-30 | 2012-10-25 | Panasonic Corp | Device for producing ballast water, and method for operating the same |
| US9333464B1 (en) | 2014-10-22 | 2016-05-10 | Koch Membrane Systems, Inc. | Membrane module system with bundle enclosures and pulsed aeration and method of operation |
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| CN108101157A (en) * | 2018-02-06 | 2018-06-01 | 大唐国际发电股份有限公司北京高井热电厂 | A kind of reverse osmosis chemicals dosing plant and system |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| JP2012206025A (en) * | 2011-03-30 | 2012-10-25 | Panasonic Corp | Device for producing ballast water, and method for operating the same |
| US9333464B1 (en) | 2014-10-22 | 2016-05-10 | Koch Membrane Systems, Inc. | Membrane module system with bundle enclosures and pulsed aeration and method of operation |
| US9956530B2 (en) | 2014-10-22 | 2018-05-01 | Koch Membrane Systems, Inc. | Membrane module system with bundle enclosures and pulsed aeration and method of operation |
| US10702831B2 (en) | 2014-10-22 | 2020-07-07 | Koch Separation Solutions, Inc. | Membrane module system with bundle enclosures and pulsed aeration and method of operation |
| USD779632S1 (en) | 2015-08-10 | 2017-02-21 | Koch Membrane Systems, Inc. | Bundle body |
| USD779631S1 (en) | 2015-08-10 | 2017-02-21 | Koch Membrane Systems, Inc. | Gasification device |
| CN108101157A (en) * | 2018-02-06 | 2018-06-01 | 大唐国际发电股份有限公司北京高井热电厂 | A kind of reverse osmosis chemicals dosing plant and system |
| CN109704524A (en) * | 2019-03-05 | 2019-05-03 | 苏州方舟环保科技有限公司 | A kind of micro-nano bubble emulsification liquid processing device |
| CN114940527A (en) * | 2022-02-28 | 2022-08-26 | 成都理工大学 | A pressure-adjustable hydraulic cavitation groundwater circulation well system |
| US11912595B2 (en) | 2022-02-28 | 2024-02-27 | Chengdu University Of Technology | Groundwater circulation well system with pressure-adjustable hydrodynamic cavitation |
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