JP2000288362A - Cleaning method of filtration membrane - Google Patents
Cleaning method of filtration membraneInfo
- Publication number
- JP2000288362A JP2000288362A JP11100343A JP10034399A JP2000288362A JP 2000288362 A JP2000288362 A JP 2000288362A JP 11100343 A JP11100343 A JP 11100343A JP 10034399 A JP10034399 A JP 10034399A JP 2000288362 A JP2000288362 A JP 2000288362A
- Authority
- JP
- Japan
- Prior art keywords
- gas
- water
- dissolved
- filtration membrane
- fine particles
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Landscapes
- Separation Using Semi-Permeable Membranes (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、ろ過膜の洗浄方法
に関する。さらに詳しくは、本発明は、ろ過膜に付着し
た微粒子を効率よく除去することができるろ過膜の洗浄
方法に関する。[0001] The present invention relates to a method for cleaning a filtration membrane. More specifically, the present invention relates to a method for cleaning a filtration membrane capable of efficiently removing fine particles attached to the filtration membrane.
【0002】[0002]
【従来の技術】半導体用シリコン基板、液晶用ガラス基
板、フォトマスク用石英基板などの電子材料表面から、
微粒子、有機物、金属などの不純物を除去することは、
製品の品質や歩留まりを確保する上で極めて重要であ
る。不純物除去のための洗浄工程で使用される洗浄水や
リンス水には、非常に高い純度が要求されている。これ
らの洗浄工程で使用される洗浄水やリンス水中に、微粒
子などの不純物が混入していると、不純物が半導体用シ
リコン基板などに対して二次汚染を招き、欠陥発生の原
因になる。このために、洗浄工程において使用する超純
水は、あらかじめ分析を行って水質を確認し、常時管理
する必要がある。超純水中の微粒子計測方法としては、
レーザー光の散乱を利用したパーティクルモニターによ
るオンライン計測法と、超純水をろ過膜を用いてろ過
し、ろ過膜上に捕捉された微粒子を走査型電子顕微鏡で
計測する直接検鏡法の2種類がある。直接検鏡法の場
合、ろ過膜は、測定の対象となる超純水よりもさらに高
純度の水で、又は、これにアンモニアを加えた水で洗浄
しているが、ろ過膜上にはなおかなりの初期汚染微粒子
が付着しているので、超純水中の微粒子を識別計測する
ためには大量の超純水を通水する必要があり、ろ過水量
と通水時間の両面で非常に無駄が多いのが現状である。
このために、ろ過膜を洗浄して付着している微粒子を効
率よく除去することができるろ過膜の洗浄方法が求めら
れている。2. Description of the Related Art From the surface of electronic materials such as silicon substrates for semiconductors, glass substrates for liquid crystals, and quartz substrates for photomasks,
Removing impurities such as fine particles, organic matter, and metals
It is extremely important to ensure product quality and yield. Very high purity is required for cleaning water and rinsing water used in a cleaning step for removing impurities. If impurities such as fine particles are mixed in the cleaning water or the rinsing water used in these cleaning steps, the impurities cause secondary contamination on a silicon substrate for semiconductors and the like, thereby causing defects. For this reason, ultrapure water used in the washing step needs to be analyzed in advance to check the quality of the water and to be constantly controlled. As a method for measuring particles in ultrapure water,
On-line measurement using a particle monitor that utilizes laser light scattering, and direct microscopy, in which ultrapure water is filtered using a filtration membrane, and fine particles captured on the filtration membrane are measured using a scanning electron microscope. There is. In the case of direct microscopy, the filtration membrane is washed with water of higher purity than the ultrapure water to be measured, or with water added with ammonia, but still remains on the filtration membrane. Since a considerable amount of initial contaminant particles are attached, it is necessary to pass a large amount of ultrapure water in order to identify and measure the particles in ultrapure water, which is extremely wasteful in terms of both the amount of filtered water and the time of water flow. There are many at present.
For this reason, there is a need for a method for cleaning a filtration membrane that can efficiently remove the attached fine particles by cleaning the filtration membrane.
【0003】[0003]
【発明が解決しようとする課題】本発明は、ろ過膜に付
着した微粒子を効率よく除去することができるろ過膜の
洗浄方法を提供することを目的としてなされたものであ
る。SUMMARY OF THE INVENTION An object of the present invention is to provide a method for cleaning a filtration membrane which can efficiently remove fine particles adhering to the filtration membrane.
【0004】[0004]
【課題を解決するための手段】本発明者らは、上記の課
題を解決すべく鋭意研究を重ねた結果、ろ過膜をガス溶
解水と接触させて洗浄することにより、ろ過膜に付着し
た微粒子を効果的に除去し得ることを見いだし、この知
見に基づいて本発明を完成するに至った。すなわち、本
発明は、(1)ろ過膜を、酸素ガス、水素ガス、炭酸ガ
ス、窒素ガス又は希ガスを溶解したガス溶解水と接触さ
せて洗浄することを特徴とするろ過膜の洗浄方法、を提
供するものである。さらに、本発明の好ましい態様とし
て、(2)ろ過膜が、超純水又は高純度薬液のろ過処理
に用いられるろ過膜である第(1)項記載のろ過膜の洗浄
方法、(3)ろ過膜が、超純水又は高純度薬液中の微粒
子数の直接検鏡法による測定に用いられるろ過膜である
第(1)項記載のろ過膜の洗浄方法、(4)酸素ガス、水
素ガス、窒素ガス又は希ガスを溶解したガス溶解水に、
高純度のアルカリを添加する第(1)項記載のろ過膜の洗
浄方法、(5)ろ過膜とガス溶解水との接触に際して、
ろ過膜又はガス溶解水に超音波を伝達する第(1)項記載
のろ過膜の洗浄方法、及び、(6)ガス溶解水を、キャ
ビテーションジェット流体又はバブルジェット流体とし
てろ過膜に接触させる第(1)項記載のろ過膜の洗浄方
法、を挙げることができる。Means for Solving the Problems The inventors of the present invention have conducted intensive studies to solve the above-mentioned problems, and as a result, by contacting and washing the filtration membrane with gas-dissolved water, the fine particles adhering to the filtration membrane have been obtained. Have been found to be able to be effectively removed, and the present invention has been completed based on this finding. That is, the present invention provides: (1) a method for cleaning a filtration membrane, which comprises contacting the filtration membrane with gas-dissolved water in which oxygen gas, hydrogen gas, carbon dioxide gas, nitrogen gas or rare gas is dissolved, and Is provided. Further, as a preferred embodiment of the present invention, (2) the method for washing a filtration membrane according to (1), wherein the filtration membrane is a filtration membrane used for a filtration treatment of ultrapure water or a high-purity chemical solution; (1) The method for cleaning a filtration membrane according to the above (1), wherein the membrane is a filtration membrane used for measuring the number of fine particles in ultrapure water or a high-purity chemical solution by direct microscopy; (4) oxygen gas, hydrogen gas, In gas dissolved water in which nitrogen gas or rare gas is dissolved,
(1) The method for washing a filtration membrane according to (1), wherein a high-purity alkali is added, (5) upon contact between the filtration membrane and gas-dissolved water,
(1) The method for cleaning a filtration membrane according to the above (1), wherein ultrasonic waves are transmitted to the filtration membrane or the gas-dissolved water, and (6) the method for bringing the gas-dissolved water into contact with the filtration membrane as a cavitation jet fluid or a bubble jet fluid. The washing method of the filtration membrane described in the item 1) can be mentioned.
【0005】[0005]
【発明の実施の形態】本発明のろ過膜の洗浄方法は、ろ
過膜を、酸素ガス、水素ガス、炭酸ガス、窒素ガス又は
希ガスを溶解したガス溶解水と接触させて洗浄するもの
である。本発明方法においては、酸素ガス、水素ガス、
炭酸ガス、窒素ガス又は希ガスの1種のみを溶解したガ
ス溶解水を用いることができ、あるいは、酸素ガス、水
素ガス、炭酸ガス、窒素ガス又は希ガスの2種以上を組
み合わせて溶解したガス溶解水を用いることもできる。
本発明方法により洗浄するろ過膜の材質に特に制限はな
く、例えば、ポリエステル系、ポリカーボネート系、セ
ルロース系、フッ素樹脂系などの有機質のろ過膜や、酸
化アルミニウムなどの無機質のろ過膜などを挙げること
ができる。本発明方法により洗浄するろ過膜の用途に特
に制限はなく、例えば、超純水又は高純度薬液のろ過処
理に用いられる限外ろ過膜や精密ろ過膜、超純水又は高
純度薬液中の微粒子数の直接検鏡法による測定に用いら
れるろ過膜、水中の濁度を測定するためのろ過膜などを
挙げることができる。本発明方法は、これらの中で、微
粒子数測定用のろ過膜の洗浄に特に好適に用いることが
できる。超純水などの微粒子数を直接検鏡法により測定
するためには、測定の対象である超純水などを、ろ過膜
が着脱可能な微粒子捕捉フィルターに通水して、ろ過膜
面上に微粒子を捕捉し、所定量の超純水などを通水した
のち、フィルターからろ過膜を外し、走査型顕微鏡を用
いてろ過膜面上の微粒の数を計測する。通水後のろ過膜
面上の微粒子数から、通水前のろ過膜面上の微粒子数を
差し引くことにより、捕捉された微粒子数を把握するこ
とができる。しかし、通水前のろ過膜面上の微粒子数が
多いと、計測が困難となって誤差が生じやすい。また、
通水前のろ過膜面上の微粒子数より、捕捉された微粒子
数の方を多くしないと、誤差が生じやすいので、測定の
ための通水量を大量にしなければならず、したがって長
時間を要する。本発明方法により洗浄されたろ過膜は、
ろ過膜面上に残存する微粒子数が少ないので、少量の通
水で捕捉された微粒子数を正確に計測することができ、
測定に要する水量を節減し、所要時間を短縮することが
できる。BEST MODE FOR CARRYING OUT THE INVENTION In the method for cleaning a filtration membrane according to the present invention, the filtration membrane is cleaned by bringing it into contact with gas-dissolved water in which oxygen gas, hydrogen gas, carbon dioxide gas, nitrogen gas or a rare gas is dissolved. . In the method of the present invention, oxygen gas, hydrogen gas,
Gas-dissolved water in which only one of carbon dioxide gas, nitrogen gas and rare gas is dissolved can be used, or gas dissolved in combination of two or more of oxygen gas, hydrogen gas, carbon dioxide gas, nitrogen gas and rare gas Dissolved water can also be used.
There is no particular limitation on the material of the filtration membrane to be washed by the method of the present invention, and examples thereof include organic filtration membranes such as polyester-based, polycarbonate-based, cellulose-based, and fluororesin-based membranes, and inorganic filtration membranes such as aluminum oxide. Can be. There is no particular limitation on the use of the filtration membrane to be washed by the method of the present invention. For example, ultrafiltration membranes or microfiltration membranes used for filtration of ultrapure water or high-purity chemicals, fine particles in ultrapure water or high-purity chemicals A filtration membrane used for measuring the number by direct microscopy, a filtration membrane for measuring turbidity in water, and the like can be given. Among them, the method of the present invention can be particularly suitably used for washing a filtration membrane for measuring the number of fine particles. In order to measure the number of particles such as ultrapure water directly by microscopy, ultrapure water to be measured is passed through a particle capture filter with a removable filter, After capturing the fine particles and passing a predetermined amount of ultrapure water or the like, the filter membrane is removed from the filter, and the number of fine particles on the filter membrane surface is measured using a scanning microscope. By subtracting the number of fine particles on the filtration membrane surface before passing water from the number of fine particles on the filtration membrane surface after passing water, the number of captured fine particles can be grasped. However, if the number of fine particles on the surface of the filtration membrane before the passage of water is large, the measurement becomes difficult and an error is likely to occur. Also,
If the number of trapped fine particles is not larger than the number of fine particles on the filtration membrane surface before water passage, an error is likely to occur, so that a large amount of water must be passed for measurement, and it takes a long time. . The filtration membrane washed by the method of the present invention,
Since the number of fine particles remaining on the filtration membrane surface is small, the number of fine particles captured by a small amount of water can be accurately measured,
The amount of water required for measurement can be reduced, and the required time can be reduced.
【0006】本発明方法に用いる酸素ガス、水素ガス、
炭酸ガス、窒素ガス又は希ガスを溶解したガス溶解水
は、これらのガスを超純水に溶解した水であることが好
ましい。超純水は、25℃における電気抵抗率が18M
Ω・cm以上であり、有機体炭素が10μg/リットル以
下であり、微粒子が10,000個/リットル以下であ
ることが好ましい。本発明方法において、酸素ガス、水
素ガス、炭酸ガス、窒素ガス又は希ガスを溶解したガス
溶解水の製造方法に特に制限はなく、例えば、これらの
ガスを水にバブリングして溶解させることもできる。し
かし、これらのガスの溶解効率を高めるためには、あら
かじめ水を脱気して溶存気体の飽和度を低下したのち、
溶解すべきガスを供給して溶解させることが好ましい。
ここに、気体の飽和度とは、水中に溶解している気体の
量を、圧力0.1MPa、温度20℃における気体の溶解量
で除した値である。例えば、水が圧力0.1MPa、温度2
0℃で空気と接して平衡状態にある水は、窒素ガス1
4.9mg/リットルと酸素ガス9.1mg/リットルを溶解
して飽和度1.0倍の状態となっているので、脱気によ
り気体の溶解量を窒素ガス3.0mg/リットル、酸素ガ
ス1.8mg/リットルとした水の飽和度は0.2倍であ
る。飽和度が0.2倍の水は、気体溶解キャパシティー
に飽和度の0.8倍に相当する空きがあるので、飽和度
の0.8倍に相当するガスを容易に溶解することができ
る。例えば、圧力0.1MPa、温度20℃において、水素
ガスの水への溶解量は1.63mg/リットルであるの
で、飽和度0.2倍の水に対して水素ガスを溶解して、
溶存水素ガス濃度1.30mg/リットルの水素ガス溶解
水を容易に製造することができる。圧力0.1MPa、温度
20℃における水への溶解量は、酸素ガス44.3mg/
リットル、炭酸ガス1,710mg/リットル、窒素ガス
19.0mg/リットル、ヘリウム1.56mg/リットル、
ネオン9.36mg/リットル、アルゴン60.8mg/リッ
トル、クリプトン233mg/リットル、キセノン643
mg/リットルであり、それぞれの溶解量に応じた飽和度
のガス溶解水を製造することができる。[0006] Oxygen gas, hydrogen gas used in the method of the present invention,
The gas-dissolved water in which carbon dioxide gas, nitrogen gas or rare gas is dissolved is preferably water in which these gases are dissolved in ultrapure water. Ultrapure water has an electrical resistivity of 18M at 25 ° C.
Ω · cm or more, organic carbon is preferably 10 μg / liter or less, and fine particles are preferably 10,000 particles / liter or less. In the method of the present invention, the method for producing gas-dissolved water in which oxygen gas, hydrogen gas, carbon dioxide gas, nitrogen gas or a rare gas is dissolved is not particularly limited. For example, these gases can be dissolved by bubbling water. . However, in order to increase the dissolving efficiency of these gases, water must be degassed in advance to reduce the saturation of dissolved gases,
Preferably, the gas to be dissolved is supplied to dissolve.
Here, the gas saturation is a value obtained by dividing the amount of gas dissolved in water by the amount of gas dissolved at a pressure of 0.1 MPa and a temperature of 20 ° C. For example, water has a pressure of 0.1 MPa and a temperature of 2
Water in equilibrium with air at 0 ° C.
Since 4.9 mg / liter and 9.1 mg / liter of oxygen gas are dissolved and the saturation is 1.0 times, the amount of dissolved gas is reduced by degassing to 3.0 mg / liter of nitrogen gas and 1% of oxygen gas. The saturation of water at 0.8 mg / liter is 0.2 times. Water having a saturation degree of 0.2 times has a space corresponding to 0.8 times the saturation degree in the gas dissolution capacity, so that a gas corresponding to 0.8 times the saturation degree can be easily dissolved. . For example, at a pressure of 0.1 MPa and a temperature of 20 ° C., the amount of hydrogen gas dissolved in water is 1.63 mg / liter, so hydrogen gas is dissolved in water having a saturation degree of 0.2 times.
Hydrogen gas dissolved water having a dissolved hydrogen gas concentration of 1.30 mg / liter can be easily produced. The amount dissolved in water at a pressure of 0.1 MPa and a temperature of 20 ° C. was 44.3 mg of oxygen gas /
Liter, carbon dioxide gas 1,710mg / l, nitrogen gas 19.0mg / l, helium 1.56mg / l,
Neon 9.36 mg / L, Argon 60.8 mg / L, Krypton 233 mg / L, Xenon 643
mg / liter, and gas-dissolved water having a degree of saturation corresponding to each dissolved amount can be produced.
【0007】ガス溶解水を製造するに際して、水の脱気
方法に特に制限はなく、例えば、真空脱気、減圧膜脱気
などによることができる。また、脱気した水にガスを溶
解させる方法に特に制限はなく、例えば、バブリング、
エゼクター、気体透過膜モジュールを用いる溶解などに
よることができる。これらの中で、気体透過膜モジュー
ルを多段に用いて溶存気体の除去及びガスの溶解を行う
ことが好ましい。例えば、気体透過膜モジュールを2段
に設け、前段の気体透過膜モジュールを用いて全溶存気
体を対象とする減圧膜脱気を行い、後段の気体透過膜モ
ジュールを用いて酸素ガス、水素ガス、炭酸ガス、窒素
ガス又は希ガスを溶解することができる。気体透過膜モ
ジュールを2段に設けて、全溶存気体を対象とする減圧
膜脱気とガスの溶解を2段に行うことにより、ガスを無
駄に放出することなく、ほぼ定量的に水に溶解すること
ができる。本発明方法においては、酸素ガス、水素ガ
ス、窒素ガス又は希ガスを溶解したガス溶解水に、高純
度のアルカリを添加することができる。ガス溶解水にア
ルカリを添加して、pHを8以上、より好ましくはpH9〜
10に調整することにより、ろ過膜面上の微粒子の除去
効果と再付着防止効果を高めることができる。添加する
高純度のアルカリに特に制限はなく、例えば、アンモニ
ア、水酸化ナトリウム、水酸化カリウム、水酸化テトラ
メチルアンモニウム(TMAH)などを挙げることがで
きる。これらの中で、高純度アンモニア水を好適に使用
することができる。本発明方法において、ろ過膜を、酸
素ガス、水素ガス、炭酸ガス、窒素ガス又は希ガスを溶
解したガス溶解水を用いて洗浄する方法に特に制限はな
く、例えば、ろ過膜を挟持具で吊るし、ガス溶解水を満
たした洗浄槽に浸漬してバッチ式処理を行うことがで
き、あるいは、ろ過膜をローダー上に載せ、ガス溶解水
をろ過膜に注いで処理する枚葉式洗浄を行うこともでき
る。洗浄槽中のガス溶解水は流動状態とすることが好ま
しく、ガス溶解水を連続的に供給し、溢流させつつ洗浄
することが好ましい。洗浄槽は、2段以上に設けること
ができ、アルカリを添加したガス溶解水を用いた場合に
は、最後の洗浄槽には超純水を満たし、リンスすること
が好ましい。枚葉式洗浄においても、アルカリを添加し
たガス溶解水を用いた場合には、洗浄後にリンス工程を
設けることが好ましい。本発明方法においては、ろ過膜
をガス溶解水を用いて洗浄する際に、ろ過膜又はガス溶
解水に超音波を伝達することができる。超音波を伝達す
ることにより、ろ過膜面上の微粒子の除去効果を高める
ことができる。伝達する超音波の周波数に特に制限はな
いが、10kHz〜3MHzであることが好ましい。ろ過膜又
はガス溶解水に超音波を伝達する方法に特に制限はな
く、例えば、超音波洗浄器の洗浄槽にガス溶解水を満た
してろ過膜を浸漬することができ、あるいは、超音波発
振装置つきのノズルを用いて、ろ過膜にガス溶解水を噴
射することもできる。In producing gas-dissolved water, there is no particular limitation on the method of degassing water. For example, vacuum degassing, degassing under reduced pressure, and the like can be used. There is no particular limitation on the method of dissolving the gas in degassed water, for example, bubbling,
Dissolution using an ejector or a gas-permeable membrane module can be performed. Among them, it is preferable to use a gas permeable membrane module in multiple stages to remove dissolved gas and dissolve gas. For example, a gas permeable membrane module is provided in two stages, decompression membrane degassing for all dissolved gases is performed using the gas permeable membrane module in the previous stage, and oxygen gas, hydrogen gas, Carbon dioxide gas, nitrogen gas or rare gas can be dissolved. By installing gas permeable membrane modules in two stages and performing decompression membrane degassing and gas dissolution for all dissolved gases in two stages, gas can be almost quantitatively dissolved without wasteful release. can do. In the method of the present invention, high-purity alkali can be added to gas-dissolved water in which oxygen gas, hydrogen gas, nitrogen gas, or rare gas is dissolved. An alkali is added to the gas-dissolved water to adjust the pH to 8 or more, more preferably 9 to
By adjusting to 10, the effect of removing fine particles on the filtration membrane surface and the effect of preventing re-adhesion can be enhanced. The high-purity alkali to be added is not particularly limited, and examples thereof include ammonia, sodium hydroxide, potassium hydroxide, and tetramethylammonium hydroxide (TMAH). Among these, high-purity aqueous ammonia can be suitably used. In the method of the present invention, there is no particular limitation on the method for cleaning the filtration membrane using gaseous water in which oxygen gas, hydrogen gas, carbon dioxide gas, nitrogen gas or a rare gas is dissolved, and, for example, the filtration membrane is hung by a clamp. Batch treatment can be performed by immersing in a washing tank filled with gas-dissolved water, or single-wafer cleaning in which a filter membrane is placed on a loader and gas-dissolved water is poured into the filter membrane for treatment. Can also. It is preferable that the gas-dissolved water in the cleaning tank be in a fluidized state, and it is preferable that the gas-dissolved water be continuously supplied and washed while overflowing. The washing tank can be provided in two or more stages. When gas-dissolved water to which alkali is added is used, it is preferable that the last washing tank be filled with ultrapure water and rinsed. Also in single wafer cleaning, when using gas-dissolved water to which alkali is added, it is preferable to provide a rinsing step after cleaning. In the method of the present invention, ultrasonic waves can be transmitted to the filter membrane or the gas-dissolved water when the filter membrane is washed with the gas-dissolved water. By transmitting the ultrasonic waves, the effect of removing the fine particles on the filtration membrane surface can be enhanced. The frequency of the transmitted ultrasonic wave is not particularly limited, but is preferably 10 kHz to 3 MHz. There is no particular limitation on the method of transmitting ultrasonic waves to the filtration membrane or the gas-dissolved water. For example, a cleaning tank of an ultrasonic cleaner can be filled with gas-dissolved water and the filtration membrane can be immersed, or an ultrasonic oscillator Gas-dissolved water can also be sprayed on the filtration membrane using a nozzle with a gas nozzle.
【0008】本発明方法においては、ガス溶解水を、ジ
ェット流体として挟持具で保持したろ過膜に噴射するこ
とができる。ジェット流体の形態に特に制限はなく、例
えば、バブルジェット流体、キャビテーションジェット
流体などを挙げることができる。図1は、バブルジェッ
ト流体用のノズルの断面図及びノズル出口形状を示す平
面図である。バブルジェット流体用ノズルには、送水管
1にガス溶解水が高圧で送られ、送気管2に気体が高圧
で送られ、ノズル3の中でガス溶解水と気体が混合す
る。ガス溶解水と気体の混合により、気体が有している
エネルギーがガス溶解水に移行するとともに、ガス溶解
水が微細な水流となり、ノズル出口4から高エネルギー
の水流としてろ過膜に噴射される。ノズルに送水するガ
ス溶解水の圧力は、2〜10kg/cm2であることが好ま
しく、4〜7kg/cm2であることがより好ましい。ノズ
ルに送気する気体の圧力は、2〜10kg/cm2であるこ
とが好ましく、3〜6kg/cm2であることがより好まし
い。図2は、キャビテーションジェット流体用のノズル
の断面図及びノズル出口形状を示す平面図である。キャ
ビテーションジェット流体用ノズルは、高圧水送水管5
と低圧水送水管6を有し、いずれの送水管にもガス溶解
水が送水される。ノズル出口において、高圧水はノズル
中央の小面積の開口部7より噴射され、低圧水はその周
辺を囲む同心円状の大面積の開口部8より噴射される。
高圧水と低圧水の流速比は、5:1〜20:1であるこ
とが好ましく、8:1〜15:1であることがより好ま
しい。高圧水と低圧水の流速に差を設けることにより、
高圧水と低圧水の流れの界面において渦流が発生し、外
気を巻き込んで気相からなるキャビティが成長する。成
長したキャビティが破壊することにより、衝撃波が発生
し、衝撃波を伴った水流としてろ過膜に噴射される。高
圧水の圧力は、5〜100kg/cm2であることが好まし
く、20〜80kg/cm2であることがより好ましい。低
圧水の水圧は、0.5〜5kg/cm2であることが好まし
く、1〜4kg/cm2であることがより好ましい。本発明
のろ過膜の洗浄方法によれば、ろ過膜の洗浄に、酸素ガ
ス、水素ガス、炭酸ガス、窒素ガス又は希ガスを溶解し
たガス溶解水を用いることにより、従来の洗浄法に比べ
て、ろ過膜面上に残存する微粒子数を10分の1ないし
100分の1に減少することができ、これによって、ろ
過膜を超純水中の微粒子数の直接検鏡法による識別計数
に用いる場合、少ない通水量で、短時間で正確な測定値
を得ることができる。In the method of the present invention, the gas-dissolved water can be jetted as a jet fluid to the filtration membrane held by the holding tool. The form of the jet fluid is not particularly limited, and examples thereof include a bubble jet fluid and a cavitation jet fluid. FIG. 1 is a sectional view of a nozzle for a bubble jet fluid and a plan view showing a nozzle outlet shape. To the nozzle for the bubble jet fluid, gas-dissolved water is sent to the water supply pipe 1 at high pressure, gas is sent to the air supply pipe 2 at high pressure, and the gas-dissolved water and gas are mixed in the nozzle 3. The energy of the gas is transferred to the gas-dissolved water by the mixing of the gas-dissolved water and the gas, and the gas-dissolved water is turned into a fine water stream, which is jetted from the nozzle outlet 4 as a high-energy water stream to the filtration membrane. The pressure of the gas dissolved water to water in the nozzle is preferably 2 to 10 kg / cm 2, more preferably 4~7kg / cm 2. The pressure of the gas air to the nozzle is preferably 2 to 10 kg / cm 2, more preferably 3~6kg / cm 2. FIG. 2 is a sectional view of a nozzle for a cavitation jet fluid and a plan view showing a nozzle outlet shape. The nozzle for cavitation jet fluid is a high pressure water pipe 5
And a low-pressure water supply pipe 6, and gas-dissolved water is supplied to each of the water supply pipes. At the nozzle outlet, high-pressure water is sprayed from a small-area opening 7 in the center of the nozzle, and low-pressure water is sprayed from a concentric large-area opening 8 surrounding the periphery.
The flow ratio of high-pressure water to low-pressure water is preferably 5: 1 to 20: 1, more preferably 8: 1 to 15: 1. By providing a difference in the flow rate of high-pressure water and low-pressure water,
A vortex is generated at the interface between the flow of high-pressure water and low-pressure water, and entrains outside air to grow a cavity composed of a gas phase. When the grown cavity is destroyed, a shock wave is generated and is jetted to the filtration membrane as a water flow accompanied by the shock wave. The pressure of the high pressure water is preferably 5 to 100 kg / cm 2, more preferably 20~80kg / cm 2. Pressure of low-pressure water is preferably 0.5 to 5 kg / cm 2, more preferably 1~4kg / cm 2. According to the filtration membrane cleaning method of the present invention, compared to the conventional cleaning method, by using gas dissolved water in which oxygen gas, hydrogen gas, carbon dioxide gas, nitrogen gas or a rare gas is dissolved, for cleaning the filtration membrane. The number of fine particles remaining on the surface of the filtration membrane can be reduced to 1/10 to 1/100, whereby the filtration membrane can be used for discrimination and counting of the number of fine particles in ultrapure water by direct microscopy. In this case, accurate measurement values can be obtained in a short time with a small amount of water flow.
【0009】[0009]
【実施例】以下に、実施例を挙げて本発明をさらに詳細
に説明するが、本発明はこれらの実施例によりなんら限
定されるものではない。なお、実施例及び比較例におい
て、付着微粒子数は、直接検鏡法により測定したろ過膜
1枚当たりの直径0.05μm以上の微粒子数である。 実施例1 溶存水素ガス濃度1.2mg/リットルの水素ガス溶解超
純水を洗浄水として用いて、孔径0.05μm、直径2
5mmのポリカーボネート製微粒子捕捉用ろ過膜[ニュー
クリポア社]を洗浄した。挟持具を用いてろ過膜を吊る
し、洗浄水を満たした容積1,000mlの洗浄槽に浸漬
し、洗浄水を300ml/分注ぎ込み、溢流させながら3
0分間洗浄した。ろ過膜に付着した微粒子数は洗浄前が
9.54×107個、洗浄後が1.33×107個であり、
微粒子除去率は86.1%であった。 実施例2 洗浄槽として超音波洗浄器[プレテック社製、ファイン
ソニックPT−08M、周波数750±100kHz]を
用い、実施例1と同じろ過膜を、溶存水素ガス濃度1.
2mg/リットルの水素ガス溶解超純水を洗浄水として用
いて洗浄した。挟持具を用いてろ過膜を吊るし、洗浄水
を満たした超音波洗浄器に浸漬し、洗浄水を300ml/
分注ぎ込み、溢流させながら30分間洗浄した。ろ過膜
に付着した微粒子数は洗浄前が9.36×107個、洗浄
後が6.29×106個であり、微粒子除去率は93.3
%であった。 実施例3 洗浄槽として超音波洗浄器[プレテック社製、ファイン
ソニックPT−08M、周波数750±100kHz]を
用い、実施例1と同じろ過膜を、水素ガス1.2mg/リ
ットルとアンモニア1mg/リットルを溶解した超純水を
洗浄水として用いて洗浄した。挟持具を用いてろ過膜を
吊るし、洗浄水を満たした超音波洗浄器に浸漬し、洗浄
水を300ml/分注ぎ込み、溢流させながら20分間洗
浄し、次いで、超純水を満たした超音波洗浄器に移し、
超純水を300ml/分注ぎ込み、溢流させながら10分
間リンスした。ろ過膜に付着した微粒子数は洗浄前が
9.53×107個、洗浄後が4.55×105個であり、
微粒子除去率は99.5%であった。 実施例4 洗浄水として、溶存酸素ガス濃度35mg/リットルの酸
素ガス溶解超純水を用いた以外は、実施例1と同様にし
て、ろ過膜の洗浄を行った。ろ過膜に付着した微粒子数
は洗浄前が9.48×107個、洗浄後が2.23×107
個であり、微粒子除去率は76.5%であった。 実施例5 洗浄水として、溶存酸素ガス濃度35mg/リットルの酸
素ガス溶解超純水を用いた以外は、実施例2と同様にし
て、ろ過膜の洗浄を行った。ろ過膜に付着した微粒子数
は洗浄前が9.18×107個、洗浄後が7.30×106
個であり、微粒子除去率は92.0%であった。 実施例6 酸素ガス35mg/リットルとアンモニア1mg/リットル
を溶解した超純水を洗浄水として用いた以外は、実施例
3と同様にして、ろ過膜の洗浄を行った。ろ過膜に付着
した微粒子数は洗浄前が9.55×107個、洗浄後が
5.69×105個であり、微粒子除去率は99.4%で
あった。 実施例7 洗浄水として、溶存アルゴン濃度30mg/リットルのア
ルゴン溶解超純水を用いた以外は、実施例1と同様にし
て、ろ過膜の洗浄を行った。ろ過膜に付着した微粒子数
は洗浄前が8.74×107個、洗浄後が4.25×107
個であり、微粒子除去率は51.4%であった。 実施例8 洗浄水として、溶存アルゴン濃度30mg/リットルのア
ルゴン溶解超純水を用いた以外は、実施例2と同様にし
て、ろ過膜の洗浄を行った。ろ過膜に付着した微粒子数
は洗浄前が9.56×107個、洗浄後が1.51×107
個であり、微粒子除去率は84.2%であった。 実施例9 アルゴン35mg/リットルとアンモニア1mg/リットル
を溶解した超純水を洗浄水として用いた以外は、実施例
3と同様にして、ろ過膜の洗浄を行った。ろ過膜に付着
した微粒子数は洗浄前が9.59×107個、洗浄後が
1.61×106個であり、微粒子除去率は98.3%で
あった。 比較例1 洗浄水として、超純水を用いた以外は、実施例1と同様
にして、ろ過膜の洗浄を行った。ろ過膜に付着した微粒
子数は洗浄前が9.78×107個、洗浄後が6.81×
107個であり、微粒子除去率は30.4%であった。 比較例2 洗浄水として、超純水を用いた以外は、実施例2と同様
にして、ろ過膜の洗浄を行った。ろ過膜に付着した微粒
子数は洗浄前が8.98×107個、洗浄後が2.53×
107個であり、微粒子除去率は71.8%であった。 比較例3 アンモニア1mg/リットルを溶解した超純水を洗浄水と
して用い、実施例1と同様にして、ろ過膜を20分間洗
浄したのち、さらに超純水を用いて10分間リンスし
た。ろ過膜に付着した微粒子数は洗浄前が9.63×1
07個、洗浄後が5.72×107個であり、微粒子除去
率は40.6%であった。 比較例4 アンモニア1mg/リットルを溶解した超純水を洗浄水と
して用いた以外は、実施例3と同様にして、ろ過膜の洗
浄を行った。ろ過膜に付着した微粒子数は洗浄前が9.
21×107個、洗浄後が1.11×107個であり、微
粒子除去率は87.9%であった。実施例1〜9及び比
較例1〜4の結果を、第1表に示す。EXAMPLES The present invention will be described in more detail with reference to the following Examples, which should not be construed as limiting the present invention. In the examples and comparative examples, the number of attached fine particles is the number of fine particles having a diameter of 0.05 μm or more per one filtration membrane measured by a direct microscopic method. Example 1 Ultrapure water containing dissolved hydrogen gas having a concentration of 1.2 mg / l was used as washing water, and the pore diameter was 0.05 μm and the diameter was 2 μm.
A 5 mm polycarbonate fine particle trapping filtration membrane [New Cripore] was washed. The filter membrane is hung using a clamp, immersed in a 1,000 ml washing tank filled with washing water, and 300 ml / pour of washing water is added.
Washed for 0 minutes. The number of microparticles attached to the filtration membrane was 9.54 × 10 7 before washing, and 1.33 × 10 7 after washing,
The fine particle removal rate was 86.1%. Example 2 The same filtration membrane as that of Example 1 was used by using an ultrasonic cleaner [FINESONIC PT-08M, frequency: 750 ± 100 kHz] as a cleaning tank.
Washing was performed using 2 mg / liter of hydrogen gas-dissolved ultrapure water as washing water. The filtration membrane is hung using a holding tool, immersed in an ultrasonic cleaner filled with cleaning water, and the cleaning water is supplied at 300 ml /
The mixture was poured and washed for 30 minutes while overflowing. The number of fine particles adhering to the filtration membrane was 9.36 × 10 7 before washing, 6.29 × 10 6 after washing, and the particle removal rate was 93.3.
%Met. Example 3 The same filtration membrane as in Example 1 was prepared by using an ultrasonic cleaner [Pretech PT-08M, frequency: 750 ± 100 kHz] as a cleaning tank. Was washed using ultrapure water in which was dissolved as washing water. The filtration membrane is hung using a clamp, immersed in an ultrasonic cleaner filled with washing water, poured with 300 ml / min of washing water, washed for 20 minutes while overflowing, and then ultrasonically filled with ultrapure water. Transfer to the washer,
Ultrapure water was poured at 300 ml / min and rinsed for 10 minutes while overflowing. The number of fine particles attached to the filtration membrane was 9.53 × 10 7 before washing, and 4.55 × 10 5 after washing.
The fine particle removal rate was 99.5%. Example 4 The filtration membrane was washed in the same manner as in Example 1 except that oxygen gas-dissolved ultrapure water having a dissolved oxygen gas concentration of 35 mg / liter was used as the washing water. The number of fine particles attached to the filtration membrane was 9.48 × 10 7 before washing, and 2.23 × 10 7 after washing.
And the fine particle removal rate was 76.5%. Example 5 A filtration membrane was washed in the same manner as in Example 2, except that oxygen gas-dissolved ultrapure water having a dissolved oxygen gas concentration of 35 mg / liter was used as washing water. The number of fine particles adhering to the filtration membrane was 9.18 × 10 7 before washing, and 7.30 × 10 6 after washing.
And the fine particle removal rate was 92.0%. Example 6 The filtration membrane was washed in the same manner as in Example 3 except that ultrapure water in which 35 mg / l of oxygen gas and 1 mg / l of ammonia were dissolved was used as washing water. The number of fine particles adhering to the filtration membrane was 9.55 × 10 7 before washing, 5.69 × 10 5 after washing, and the fine particle removal rate was 99.4%. Example 7 A filtration membrane was washed in the same manner as in Example 1 except that argon-dissolved ultrapure water having a dissolved argon concentration of 30 mg / liter was used as washing water. The number of fine particles attached to the filtration membrane was 8.74 × 10 7 before washing, and 4.25 × 10 7 after washing.
And the fine particle removal rate was 51.4%. Example 8 A filtration membrane was washed in the same manner as in Example 2, except that argon-dissolved ultrapure water having a dissolved argon concentration of 30 mg / liter was used as washing water. The number of fine particles adhering to the filtration membrane was 9.56 × 10 7 before washing, and 1.51 × 10 7 after washing.
And the fine particle removal rate was 84.2%. Example 9 The filtration membrane was washed in the same manner as in Example 3 except that ultrapure water in which 35 mg / l of argon and 1 mg / l of ammonia were dissolved was used as washing water. The number of fine particles adhering to the filtration membrane was 9.59 × 10 7 before washing, 1.61 × 10 6 after washing, and the fine particle removal rate was 98.3%. Comparative Example 1 The filtration membrane was washed in the same manner as in Example 1 except that ultrapure water was used as the washing water. The number of fine particles attached to the filtration membrane was 9.78 × 10 7 before washing, and 6.81 × after washing.
The number was 10 7 , and the fine particle removal rate was 30.4%. Comparative Example 2 The filtration membrane was washed in the same manner as in Example 2 except that ultrapure water was used as the washing water. The number of fine particles attached to the filtration membrane was 8.98 × 10 7 before washing, and 2.53 × after washing.
The number was 10 7 , and the fine particle removal rate was 71.8%. Comparative Example 3 The filtration membrane was washed for 20 minutes in the same manner as in Example 1 using ultrapure water in which 1 mg / liter of ammonia was dissolved, and then rinsed with ultrapure water for 10 minutes. The number of fine particles attached to the filtration membrane was 9.63 x 1 before washing.
0 7, after washing is × 10 7 cells 5.72, particulate removal rate was 40.6%. Comparative Example 4 A filtration membrane was washed in the same manner as in Example 3 except that ultrapure water in which 1 mg / liter of ammonia was dissolved was used as washing water. The number of particles attached to the filtration membrane was 9.
The number was 21 × 10 7, the number after washing was 1.11 × 10 7 , and the fine particle removal rate was 87.9%. Table 1 shows the results of Examples 1 to 9 and Comparative Examples 1 to 4.
【0010】[0010]
【表1】 [Table 1]
【0011】第1表に見られるように、水素ガス、酸素
ガス又はアルゴンを溶解した超純水を洗浄水として用い
た実施例においては、超純水を洗浄水として用いた比較
例よりも高い除去率でろ過膜に付着した微粒子が除去さ
れている。また、水素ガス溶解超純水、酸素ガス溶解超
純水及びアルゴン溶解超純水のいずれにおいても、超音
波を伝達しない場合に比べて、超音波を伝達した場合の
方が、微粒子除去率が高くなっている。さらに、これら
のガス溶解水に、アンモニアを添加した場合には、微粒
子除去率はいっそう向上している。As can be seen from Table 1, in the examples using ultrapure water in which hydrogen gas, oxygen gas or argon is dissolved as cleaning water, the results are higher than in the comparative example using ultrapure water as cleaning water. Fine particles adhering to the filtration membrane were removed at the removal rate. Further, in any of hydrogen gas-dissolved ultrapure water, oxygen gas-dissolved ultrapure water, and argon-dissolved ultrapure water, the fine particle removal rate is higher when ultrasonic waves are transmitted than when ultrasonic waves are not transmitted. Is getting higher. Further, when ammonia is added to these gas-dissolved waters, the fine particle removal rate is further improved.
【0012】[0012]
【発明の効果】本発明のろ過膜の洗浄方法によれば、ろ
過膜に付着した微粒子を簡単な処理により高い除去率で
除去し、清浄化することができる。本発明方法により清
浄化処理したろ過膜を、超純水中の微粒子を捕捉して識
別計測するために用いると、少ない通水量かつ短時間で
正しい測定結果を得ることができる。According to the method for cleaning a filtration membrane of the present invention, fine particles adhering to the filtration membrane can be removed by a simple treatment at a high removal rate and cleaned. When the filtration membrane cleaned by the method of the present invention is used for identifying and measuring fine particles in ultrapure water, correct measurement results can be obtained in a small amount of water and in a short time.
【図1】図1は、バブルジェット流体用のノズルの断面
図及び平面図である。FIG. 1 is a cross-sectional view and a plan view of a nozzle for a bubble jet fluid.
【図2】図2は、キャビテーションジェット流体用のノ
ズルの断面図及び平面図である。FIG. 2 is a sectional view and a plan view of a nozzle for a cavitation jet fluid.
1 送水管 2 送気管 3 ノズル 4 ノズル出口 5 高圧水送水管 6 低圧水送水管 7 小面積の開口部 8 大面積の開口部 DESCRIPTION OF SYMBOLS 1 Water supply pipe 2 Air supply pipe 3 Nozzle 4 Nozzle outlet 5 High pressure water supply pipe 6 Low pressure water supply pipe 7 Small area opening 8 Large area opening
───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4D006 GA06 GA07 KC07 KC16 KC19 KC20 KD17 LA08 MA03 MA22 MC03 MC11 MC28 MC48 MC49 PA01 PB02 PB20 PB70 PC02 ──────────────────────────────────────────────────続 き Continued on the front page F term (reference) 4D006 GA06 GA07 KC07 KC16 KC19 KC20 KD17 LA08 MA03 MA22 MC03 MC11 MC28 MC48 MC49 PA01 PB02 PB20 PB70 PC02
Claims (1)
ス、窒素ガス又は希ガスを溶解したガス溶解水と接触さ
せて洗浄することを特徴とするろ過膜の洗浄方法。1. A method for cleaning a filtration membrane, comprising contacting the filtration membrane with a gas-dissolved water in which an oxygen gas, a hydrogen gas, a carbon dioxide gas, a nitrogen gas or a rare gas is dissolved to clean the filtration membrane.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP11100343A JP2000288362A (en) | 1999-04-07 | 1999-04-07 | Cleaning method of filtration membrane |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP11100343A JP2000288362A (en) | 1999-04-07 | 1999-04-07 | Cleaning method of filtration membrane |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JP2000288362A true JP2000288362A (en) | 2000-10-17 |
Family
ID=14271484
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP11100343A Pending JP2000288362A (en) | 1999-04-07 | 1999-04-07 | Cleaning method of filtration membrane |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2000288362A (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2007070126A (en) * | 2005-09-02 | 2007-03-22 | Japan Organo Co Ltd | Method for producing filtering membrane for capturing particulate, filtering membrane for capturing particulate, and method for measuring particulate in ultrapure water |
| WO2018163705A1 (en) * | 2017-03-09 | 2018-09-13 | オルガノ株式会社 | Method for evaluating cleanliness of hollow fiber membrane device, cleaning method, and cleaning device for hollow fiber membrane device |
| CN118001931A (en) * | 2023-12-22 | 2024-05-10 | 巢湖皖维金泉实业有限公司 | Carbon dioxide recovery device for beer fermentation |
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1999
- 1999-04-07 JP JP11100343A patent/JP2000288362A/en active Pending
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2007070126A (en) * | 2005-09-02 | 2007-03-22 | Japan Organo Co Ltd | Method for producing filtering membrane for capturing particulate, filtering membrane for capturing particulate, and method for measuring particulate in ultrapure water |
| WO2018163705A1 (en) * | 2017-03-09 | 2018-09-13 | オルガノ株式会社 | Method for evaluating cleanliness of hollow fiber membrane device, cleaning method, and cleaning device for hollow fiber membrane device |
| JP2018144013A (en) * | 2017-03-09 | 2018-09-20 | オルガノ株式会社 | Method for evaluating cleanliness of hollow fiber membrane device, cleaning method, and cleaning device for hollow fiber membrane device |
| CN110382092A (en) * | 2017-03-09 | 2019-10-25 | 奥加诺株式会社 | It evaluates the method for the cleannes level of hollow fiber membrane device, wash the method for hollow fiber membrane device and the wash mill for hollow fiber membrane device |
| CN110382092B (en) * | 2017-03-09 | 2021-10-01 | 奥加诺株式会社 | Method for evaluating cleanliness level of hollow fiber membrane device, method for washing hollow fiber membrane device, and washing device for hollow fiber membrane device |
| US11351507B2 (en) | 2017-03-09 | 2022-06-07 | Organo Corporation | Method of evaluating level of cleanliness of hollow fiber membrane device, method of washing hollow fiber membrane device, and washing device for hollow fiber membrane device |
| CN118001931A (en) * | 2023-12-22 | 2024-05-10 | 巢湖皖维金泉实业有限公司 | Carbon dioxide recovery device for beer fermentation |
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