JPH03213103A - Gas or low melting point volatile organic substance-removing method - Google Patents
Gas or low melting point volatile organic substance-removing methodInfo
- Publication number
- JPH03213103A JPH03213103A JP972490A JP972490A JPH03213103A JP H03213103 A JPH03213103 A JP H03213103A JP 972490 A JP972490 A JP 972490A JP 972490 A JP972490 A JP 972490A JP H03213103 A JPH03213103 A JP H03213103A
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- Prior art keywords
- water
- volatile organic
- low
- aqueous solution
- permeated
- 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.)
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Abstract
(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は、水溶液中に溶解した気体、もしくは低沸点揮
発性有機物の除去方法に関する。DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a method for removing gases or low-boiling volatile organic substances dissolved in an aqueous solution.
〔従来の技術及び発明が解決しようとする課題〕水溶液
の使用上、その中に溶存している気体もしくは溶解して
いる有機物の除去を必要とする分野は非常に多い。[Prior Art and Problems to be Solved by the Invention] When using an aqueous solution, there are many fields in which it is necessary to remove gases or organic substances dissolved therein.
例えば分析機器関連としては液体クロマトグラフィー、
自動臨床化学分析、医用分光光度計等の脱気がある。
また工業用用途としては、イオン交換水プロセス、超純
水システム、ボイラー用水、原発用水、タービン用水等
の脱気がある。For example, regarding analytical equipment, liquid chromatography,
Automated clinical chemistry analysis, degassing of medical spectrophotometers, etc.
Industrial applications include deaeration of ion exchange water processes, ultrapure water systems, boiler water, nuclear power plant water, turbine water, etc.
例えば、液体クロマトグラフィーでは、溶媒に空気が溶
存していると、ポンプ内、弁周辺、検知器内に気泡が生
じトラブルの原因となる。 また溶存酸素は溶質と化学
反応を起こす可能性もある。For example, in liquid chromatography, if air is dissolved in the solvent, bubbles will form inside the pump, around valves, and inside the detector, causing trouble. Dissolved oxygen can also cause chemical reactions with solutes.
自動臨床化学分析では、検体量の少量化に伴い、わずか
の溶存酸素も分析精度に悪影響を及ぼす。In automated clinical chemistry analysis, as the amount of sample becomes smaller, even a small amount of dissolved oxygen has a negative impact on analysis accuracy.
また分光光度計では紫外短波長領域における溶存酸素等
による吸収の影響が大きい。 一方、イオン交換水プロ
セスでは液体中の溶存酸素や炭酸ガスがイオン交換樹脂
の寿命を短くする。 さらにボイラー用水、原発用水で
は溶存酸素が容器、配管等の腐食を促進する。In addition, spectrophotometers are greatly affected by absorption by dissolved oxygen in the ultraviolet short wavelength region. On the other hand, in the ion exchange water process, dissolved oxygen and carbon dioxide gas in the liquid shorten the life of the ion exchange resin. Furthermore, dissolved oxygen in boiler water and nuclear power plant water accelerates corrosion of containers, pipes, etc.
従来より液体中の溶存ガスを脱気するために、例えば加
熱沸騰法、減圧法、超音波法、ヘリウム法等の方法が知
られている。 しかしながら加熱沸騰法は高温操作の
ため危険性が高く、減圧法および超音波法は脱気能力が
低く、ヘリウム法は運転費が高いなど決して効果的、経
済的な方法ではなかった。BACKGROUND ART Conventionally, methods such as a heating boiling method, a depressurization method, an ultrasonic method, a helium method, and the like have been known for degassing gases dissolved in a liquid. However, the heating boiling method is highly dangerous due to its high temperature operation, the decompression method and ultrasonic method have low degassing ability, and the helium method has high operating costs, so it has never been an effective or economical method.
さらに詳しく述べると、例えばボイラー用水中に溶存し
ているガス、主に溶存酸素は、ボイラープレボイラー系
の特に孔食の主原因になるので、それを除去する処理が
必要になる。 かかる脱酸素には、脱気器を用いて加熱
沸騰法や真空法等により機械的に脱酸素する方法と、溶
存酸素を化学的に還元する例えばヒドラジンや亜硫酸ナ
トリウム等の脱酸素剤を注入する方法があり、これらの
方法を併用しなければ脱酸素効率を大きくすることがで
きず、特に中高圧ボイラーには不可欠の処理である。More specifically, for example, gases dissolved in boiler water, mainly dissolved oxygen, are the main cause of pitting corrosion in boiler pre-boiler systems, so treatment to remove them is necessary. For such deoxidation, there are two methods: mechanical deoxidation using a deaerator using a heating boiling method, a vacuum method, etc., and a method of chemically reducing dissolved oxygen, for example, by injecting an oxygen scavenger such as hydrazine or sodium sulfite. There are various methods, and unless these methods are used in combination, the deoxidation efficiency cannot be increased, and this process is especially essential for medium and high pressure boilers.
また飲料水やビル給水中に溶存しているガス、主に溶存
酸素は、給水管の腐蝕の主原因であり、この腐蝕が赤水
の発生へとつながる。 赤水は味などの感覚的問題や洗
濯物の着色などの障害を与えるため、その発生が認めら
れた場合は何らかの対策を検討する必要が生じる。 現
在、かかる赤水対策として給水管の敷設替え、ライニン
グによる管更迭、給水用防錆剤の連続注入等が行われて
いる。 これら赤水発生防止対策は、いずれも経済性、
確実性、安全性などの面で必ずしも十分とは言えず、各
種の制約を伴う。 従って、安価で簡便かつ確実な防止
方法が望まれている。Furthermore, dissolved gases, mainly dissolved oxygen, in drinking water and building water supplies are the main cause of corrosion in water supply pipes, and this corrosion leads to the occurrence of red water. Red water causes sensory problems such as taste and causes problems such as discoloration of laundry, so if its occurrence is recognized, it is necessary to consider some countermeasures. Currently, countermeasures against such red water include re-laying water supply pipes, replacing pipes with linings, and continuously injecting rust preventive agents for water supply. These red water prevention measures are both economical and
It is not necessarily sufficient in terms of reliability, safety, etc., and comes with various limitations. Therefore, an inexpensive, simple, and reliable prevention method is desired.
また従来、超純水システムにおける脱気の目的は大きく
分けて2種類ある。 その一つはイオン交換プロセス中
の陰イオン交換樹脂の寿命を延ばすための脱溶存炭酸ガ
スであり、もう一つは超純水中での生菌の発生を抑制す
るための脱溶存酸素である。 半導体の製造において、
メモリー容量が256にビットレベルまでは、上記の目
的のための溶存酸素濃度(以下、DO値という)として
は、0.5ppmレベルで十分であった。 その結果、
脱気方法として真空脱気方法が用いられてきた。Conventionally, the purpose of deaeration in ultrapure water systems can be roughly divided into two types. One is removing dissolved carbon dioxide to extend the life of the anion exchange resin during the ion exchange process, and the other is removing dissolved oxygen to suppress the generation of viable bacteria in ultrapure water. . In semiconductor manufacturing,
When the memory capacity reached the 256-bit level, a level of 0.5 ppm was sufficient as the dissolved oxygen concentration (hereinafter referred to as DO value) for the above purpose. the result,
A vacuum deaeration method has been used as a deaeration method.
しかし近年、メモリー容量が更に大きい4Mビット、1
6MピッI・の半導体が開発されつつある。However, in recent years, 4M bits and 1
Semiconductors with 6M pins are being developed.
これら大容量の半導体の製造においては、脱気の目的と
して上記の2点以外に、溶存酸素によるシリコンウェハ
ー上の酸化被膜形成を防止する点が加わっている。 こ
の溶存酸素によるシリコンウェハーの酸化を防止するた
めには、Do値として0.01〜0.O5ppmが要求
される。 さらにユースポイント付近での脱気を行なう
必要があるため、脱気装置としても比較的小型の装置が
要求される。In the manufacture of these large-capacity semiconductors, in addition to the above two points, the purpose of degassing is to prevent the formation of an oxide film on the silicon wafer due to dissolved oxygen. In order to prevent oxidation of the silicon wafer due to this dissolved oxygen, the Do value should be 0.01 to 0. O5ppm is required. Furthermore, since it is necessary to perform degassing near the point of use, a relatively small degassing device is required.
しかしながら従来の真空脱気装置では脱溶存酸素能力が
不十分であり、また装置サイズもかなり大きくなるとい
う欠点があった。However, conventional vacuum deaerators have disadvantages in that their ability to remove dissolved oxygen is insufficient and the size of the device is also quite large.
マタ、一般にビール、ジュース、コーヒー等の飲料製造
に使用する原料水やそれらの製造工程で使用する水であ
る飲料製造用水は、製品の劣化、酸化を防止するために
溶存酸素を除去しかつ無菌のものが望ましい。Beverage manufacturing water, which is the raw water used to manufacture beverages such as beer, juice, and coffee, and the water used in those manufacturing processes, is generally sterilized by removing dissolved oxygen to prevent product deterioration and oxidation. Preferably.
従来、このような目的に使用する水を造るため、加熱沸
騰法、減圧法、二酸化炭素ガス又は二酸化炭素ガスと不
活性ガスの混合ガスを被処理水に接触させる方法等で被
処理水を脱気する方法が知られている。Conventionally, in order to produce water for such purposes, water to be treated is desorbed by heating and boiling, depressurization, or by contacting the water with carbon dioxide gas or a mixed gas of carbon dioxide gas and an inert gas. Know how to care.
しかしながら、加熱沸騰法では、水中の溶存酸素をo、
tppm程度にするには被処理水を104°C以上に加
熱することが必要であり、この加熱によりエネルギーコ
ストが高くなり、さらに長時間の運転により装置の各部
にスケールが沈着し、その洗浄に多大な労力を必要とす
る。 減圧法は、水中の溶存酸素を0.2ppm程度ま
でしか減少させることができず脱気能力が低いという欠
点があった。 また二酸化炭素ガスを被処理水に接触さ
せる方法は、水中の溶存酸素を0.lppm程度にする
には装置内にラッシヒリニグ等の充填材をつめ、かつ温
度を70°C程度の高温にすることが必要であり、この
充填材を洗浄するのに大変な労力を必要とする。 また
コーヒー等の抽出用水に使用した場合、水中に二酸化炭
素が溶解しているため、美味で風味豊かなコーヒーが得
られない。 また二酸化炭素ガスと不活性ガスの混合ガ
スを被処理水に接触させる方法では、水中の溶存酸素を
0.O5ppm程度にするには、被処理水を101°C
以上に加熱することが必要であり、この場合も加熱によ
るエネルギーコストが高くなるうえ、上記と同様に美味
で風味豊かなコーヒーが得られないという問題があった
。However, in the heating boiling method, dissolved oxygen in water is
It is necessary to heat the water to be treated to a temperature of 104°C or higher in order to reduce the amount to 104°C. This heating increases energy costs, and long-term operation causes scale to deposit on various parts of the equipment, making cleaning difficult. It requires a lot of effort. The depressurization method has the disadvantage that it can only reduce dissolved oxygen in water to about 0.2 ppm and has a low degassing ability. In addition, the method of bringing carbon dioxide gas into contact with the water to be treated reduces dissolved oxygen in the water to 0. In order to reduce the amount to about 1 ppm, it is necessary to fill the device with a filler such as Raschchlinig and raise the temperature to a high temperature of about 70° C., and cleaning this filler requires a lot of effort. Furthermore, when used as water for brewing coffee or the like, delicious and flavorful coffee cannot be obtained because carbon dioxide is dissolved in the water. In addition, in a method in which a mixed gas of carbon dioxide gas and an inert gas is brought into contact with the water to be treated, dissolved oxygen in the water is reduced to 0. To reduce O to about 5ppm, heat the water to be treated to 101°C.
It is necessary to heat the coffee to a higher level, and in this case as well, there is a problem in that the energy cost due to heating is high and, like the above, delicious and flavorful coffee cannot be obtained.
また半導体関連等において、排水中に含まれるクロロホ
ルム、トリクロロエタン、トリクロロエチレン、四塩化
炭素、カーボンテトラクロライド、テトラクロロエチレ
ン等の低沸点揮発性有機物は、環境問題の点から回収し
なければならない。 しかし、現在用いられている活性
炭吸着法では、排水が希薄水溶液であるため、回収コス
トが非常に高くなり経済的でない。Furthermore, in semiconductor-related fields, low-boiling volatile organic substances such as chloroform, trichloroethane, trichloroethylene, carbon tetrachloride, carbon tetrachloride, and tetrachloroethylene contained in wastewater must be recovered from the viewpoint of environmental issues. However, in the currently used activated carbon adsorption method, since the wastewater is a dilute aqueous solution, the recovery cost is extremely high and it is not economical.
飲料水分野においても、水源の川や湖等の汚染により、
従来は含まれていなかった低沸点揮発性有機物が、環境
基準以上の値を示すようになったり、さらに汚染の進行
とともに塩素殺菌のため、塩素使用量が増大し、化学反
応によって塩素系有機物が生成されるようになっている
。 しかし、近年の飲料水への関心の高まりとともに、
高度処理が必要とされているにもかかわらず、コスト的
な問題から有効な処理がなされていないのが現状である
。Even in the field of drinking water, pollution of water sources such as rivers and lakes has caused
Low boiling point volatile organic substances, which were not previously included, now exceed environmental standards, and as contamination progresses, the amount of chlorine used for chlorine disinfection increases, and chlorine-based organic substances are produced by chemical reactions. It is now generated. However, with increasing interest in drinking water in recent years,
Despite the need for advanced processing, the current situation is that effective processing is not carried out due to cost issues.
以上に述べた如く、気体もしくは低沸点揮発性有機物の
除去を必要とする分野は非常に多く、いずれの分野にお
いても満足できる除去方法はなかった。As mentioned above, there are many fields that require the removal of gaseous or low-boiling volatile organic substances, and there has been no satisfactory removal method in any of these fields.
近年、シリコーン、ポリテトラフルオロエチレン等の合
成樹脂からなるチューブ(中空)状の膜を用いた脱気方
法が旋案されている(特開昭60−25514号、実開
昭63−43609号等)。In recent years, a degassing method using a tube (hollow) membrane made of synthetic resin such as silicone or polytetrafluoroethylene has been proposed (Japanese Patent Application Laid-Open No. 60-25514, Utility Model Application No. 63-43609, etc.). ).
しかしながら、かかる合成樹脂からなる薄膜は機械的強
度上及び成形上限界があり、実用的に脱気用膜として使
用するには、経済効率を決定する脱気速度が小さくなる
ほど膜厚を大きくしなければならないという問題があっ
た。However, thin films made of such synthetic resins have limits in terms of mechanical strength and moldability, and in order to be used practically as a degassing membrane, the film thickness must be increased as the degassing rate, which determines economic efficiency, decreases. There was a problem that it had to be done.
〔課題を解決するための手段]
本発明者らは、種々の水溶液中に溶存する気体もしくは
低沸点揮発性有機物の除去における前記問題点を解決す
るために鋭意研究した結果、水不透過性膜を介して、他
方を、水溶液成分の蒸気圧をゼロに近づけることにより
、効率よく上記成分を除去することができることを見い
出して、本発明に至ったものである。[Means for Solving the Problems] As a result of intensive research to solve the above-mentioned problems in removing gases or low-boiling volatile organic substances dissolved in various aqueous solutions, the present inventors have developed a water-impermeable membrane. The present invention was achieved by discovering that the above component can be efficiently removed by bringing the vapor pressure of the other aqueous component close to zero through the above steps.
即ち本発明は、水不透過性膜を介して、一方に、気体溶
解水溶液もしくは低沸点揮発性有機物溶解水溶液を接触
させ、他方を、該水溶液成分の蒸気圧をゼロに近づける
ことにより、透過する溶解成分を除去することを特徴と
する気体もしくは低沸点揮発性有機物の除去方法を提供
する。That is, the present invention allows the water to permeate through a water-impermeable membrane by contacting one side with a gas-dissolved aqueous solution or a low-boiling volatile organic substance-dissolved aqueous solution and bringing the vapor pressure of the aqueous solution components close to zero on the other side. Provided is a method for removing gases or low-boiling volatile organic substances, which is characterized by removing dissolved components.
本発明が適用される水溶液は、その中に気体が溶存して
いる水溶液もしくは低沸点揮発性有機物が溶解している
水溶液であれば、特に限定されない。The aqueous solution to which the present invention is applied is not particularly limited as long as it contains a gas dissolved therein or a low-boiling volatile organic substance dissolved therein.
例えば、液体クロマトグラフィー、自動臨床化学分析、
医用分光光度計等の分析機器関連、イオン交換水プロセ
ス、半導体製造用の超純水システム、発電用、一般産業
用、船舶用ボイラー等に用いられるボイラー用水、原発
用水、タービン用水等の工業用途関連に用いられる液体
及び排水等が挙げられる。 これらの液体は通常、河川
水、井水、水道水、工業”用水、局方常水等を含み、−
76にCa、Mg、Na、に等の陽イオン、塩素イオン
、硫酸イオン、炭酸水素イオン等の陰イオン、往動が腐
敗分解した有機物を含有している液体である。 また、
コロイド粒子、懸濁粒子等の水に対して溶解性を示さな
い物質を含有している液体も含まれる。For example, liquid chromatography, automated clinical chemistry analysis,
Industrial applications such as analytical instruments such as medical spectrophotometers, ion exchange water processes, ultrapure water systems for semiconductor manufacturing, power generation, general industry, boiler water used in ship boilers, nuclear power plant water, turbine water, etc. Examples include liquids and wastewater used in connection. These liquids usually include river water, well water, tap water, industrial water, pharmacopoeia regular water, etc.
It is a liquid containing 76, cations such as Ca, Mg, Na, etc., anions such as chlorine ions, sulfate ions, hydrogen carbonate ions, etc., and organic matter that has been putrefied and decomposed. Also,
Also included are liquids containing substances that are not soluble in water, such as colloidal particles and suspended particles.
また本発明は一般家庭用水道配管、ビル給水管、クーリ
ングタワー、循環水配管等の内部を流れる飲料水やビル
給水にも通用できる。The present invention can also be applied to drinking water flowing inside general household water pipes, building water supply pipes, cooling towers, circulating water pipes, etc. and building water supply.
また本発明は醤油等の製造用水、ビール、酒、ジュース
、コーヒー等の飲料の製造に使用する原料水や製造工程
で使用する水にも適用できる。The present invention can also be applied to water used in the production of soy sauce, raw water used in the production of beverages such as beer, alcohol, juice, coffee, and water used in the production process.
上記の種々の水溶液に溶解している気体とは、酸素、炭
酸ガス、窒素、塩素、アンモニア等である。The gases dissolved in the various aqueous solutions mentioned above include oxygen, carbon dioxide, nitrogen, chlorine, and ammonia.
また、低沸点揮発性有機物とは、水より沸点が低い物質
であり、その蒸気圧が同温度で大きいものを指す。 例
えば、メタノール、エタノール、ブタノール、プロパツ
ール等の低級アルコール、四塩化炭素、クロロホルム、
フロン等のハロゲン炭化水素、その他メチルエーテル、
エチルエーテル等のエーテル類、メチルエチルケトン、
アセトン等のケトン類等が挙げられる。Furthermore, a low-boiling volatile organic substance refers to a substance that has a boiling point lower than that of water and has a large vapor pressure at the same temperature. For example, lower alcohols such as methanol, ethanol, butanol, propatool, carbon tetrachloride, chloroform,
Halogen hydrocarbons such as chlorofluorocarbons, other methyl ethers,
Ethers such as ethyl ether, methyl ethyl ketone,
Examples include ketones such as acetone.
本発明においては、上記水溶液を水不透過性膜の一方に
接触させ、他方において水溶液成分の蒸気圧をゼロに近
づけることにより、透過する溶解成分を除去する。In the present invention, the permeating dissolved components are removed by bringing the aqueous solution into contact with one side of the water-impermeable membrane and bringing the vapor pressure of the aqueous solution components close to zero on the other side.
かかる水溶液成分の蒸気圧をゼロに近づける方法は、特
に限定されないが、例えば、真空ポンプ等で機械的に透
過成分を除去する方法、不活性ガスを流して透過成分を
除去する方法、透過成分と化学反応を起こし、透過成分
を蒸発させない物質を流して透過成分を除去する方法、
透過成分が水より溶解度の高い溶媒を流して透過成分を
除去する方法等が挙げられる。The method of bringing the vapor pressure of the aqueous solution component close to zero is not particularly limited, but examples include a method of mechanically removing the permeate component using a vacuum pump, a method of removing the permeate component by flowing an inert gas, and a method of removing the permeate component by flowing an inert gas. A method of removing permeated components by causing a chemical reaction and flowing a substance that does not evaporate the permeated components;
Examples include a method of removing the permeated component by flowing a solvent in which the permeated component has a higher solubility than water.
ここで、真空ポンプ等で機械的に透過成分を除去する場
合、透過成分として被除去成分以外に水蒸気が透過して
、真空ポンプの負荷が増大し運転コストが増加する場合
がある。 また不活性ガスを流して透過成分を除去する
場合には、不活性ガスへ被除去成分以外の水蒸気が透過
し、目的成分の除去効率が落ちる恐れがある。 よって
、真空ポンプを用いる場合は、操作温度の飽和水蒸気以
上に、真空度を上げないようにしたり、不活性ガスを用
いる場合には、あらかじめ操作温度の水蒸気を含ませた
湿った不活性ガス、すなわち操作温度における飽和水蒸
気と平衡な不活性ガスを流すことが好ましく、これによ
り、さらに効率よく透過成分を除去できる。Here, when the permeated components are mechanically removed using a vacuum pump or the like, water vapor may permeate in addition to the components to be removed as the permeated components, increasing the load on the vacuum pump and increasing the operating cost. Furthermore, when the permeated components are removed by flowing an inert gas, water vapor other than the components to be removed may permeate the inert gas, which may reduce the removal efficiency of the target component. Therefore, when using a vacuum pump, make sure not to increase the degree of vacuum above saturated steam at the operating temperature, and when using an inert gas, use moist inert gas that has been pre-impregnated with water vapor at the operating temperature. That is, it is preferable to flow an inert gas that is in equilibrium with saturated water vapor at the operating temperature, thereby allowing more efficient removal of permeated components.
本発明において用いる不活性ガスは、特に制限されない
が、例えば通常、窒素、アルゴン、ヘリウム等が挙げら
れ、透過成分によっては空気や炭酸ガス等も使用できる
。The inert gas used in the present invention is not particularly limited, but typically includes nitrogen, argon, helium, etc., and air, carbon dioxide, etc. can also be used depending on the permeate component.
また本発明において用いる、透過成分と化学反応する成
分は、その透過成分に応じて適宜選ばれ、例えば透過成
分が酸素の場合、ヒドラジン、亜硫酸ナトリウム等が用
いられる。Further, the component used in the present invention that chemically reacts with the permeation component is appropriately selected depending on the permeation component. For example, when the permeation component is oxygen, hydrazine, sodium sulfite, etc. are used.
また本発明において用いられる、透過成分を溶かす溶媒
も、その透過成分に応じて適宜選ばれ、例えば、低沸点
揮発性有機物としてエタノールを含む水溶液に対しては
、メチルエーテル、エチルエーテル等のエーテル類が用
いられる。In addition, the solvent used in the present invention that dissolves the permeate component is also appropriately selected depending on the permeate component. For example, for an aqueous solution containing ethanol as a low-boiling volatile organic substance, ethers such as methyl ether and ethyl ether is used.
本発明において用いる水不透過性膜は、特にその構造に
限定されないが、例えば非多孔質活性薄膜からなる均質
膜や、緻密層または活性緻密層とこれを一体に支持する
多孔質層とからなる非対称膜や、かかる非対称膜上に非
多孔質活性薄膜が形成されてなる複合膜、好ましくは非
対称膜の緻密層中に非多孔質活性薄膜が一部しみこんで
形成されてなる複合nり等である。 ここで活性とは、
溶存物質と液体とを分離する性質を有するという意味で
ある。The water-impermeable membrane used in the present invention is not particularly limited in its structure, but includes, for example, a homogeneous membrane consisting of a non-porous active thin membrane, a dense layer or an active dense layer and a porous layer that integrally supports it. An asymmetric membrane, a composite membrane formed by forming a non-porous active thin film on such an asymmetric membrane, preferably a composite membrane formed by partially penetrating the non-porous active thin film into the dense layer of the asymmetric membrane, etc. be. Here, activity means
This means that it has the property of separating dissolved substances and liquid.
上記水不透過性膜の30°Cにおける窒素ガス透過速度
は、7 Xl0−’〜2 XIO2Nm/ nl、h
、atm、好ましくは、3 Xl0−3〜5 Xl0O
Nrd/rtr−h −atmである。 窒素ガス透過
速度が7X10−’Nn(/ボ・h−atIllより小
さい場合、溶存物質の透過速度が小さくなる恐れがあり
、一方 2X102Nrrr/ rrf・h・atmよ
り大きい場合は、水不透過性が維持できなくな名可能性
があるため好ましくない
上記均質膜や非多孔質活性薄膜の具体例としては、シリ
コーン、ポリ(4−メチルペンテン−1)、天然ゴム、
ポリ(2,6−シメチルフエニレンオキシド、テフロン
、ネオブレン、ポリエチレン、ポリスチレン、ポリプロ
ピレン等が挙げられる。The nitrogen gas permeation rate of the water-impermeable membrane at 30°C is 7 Xl0-'~2 XIO2Nm/nl, h
, atm, preferably 3 Xl0-3 to 5 Xl0O
Nrd/rtr-h-atm. If the nitrogen gas permeation rate is less than 7X10-'Nn(/bo・h-atIll), the permeation rate of dissolved substances may become small; on the other hand, if it is greater than 2X102Nrrr/rrf・h・atm, the water impermeability may decrease. Specific examples of the above-mentioned homogeneous membranes and non-porous active thin membranes, which are undesirable because they may become unsustainable, include silicone, poly(4-methylpentene-1), natural rubber,
Examples include poly(2,6-dimethylphenylene oxide, Teflon, neorene, polyethylene, polystyrene, polypropylene, etc.).
また本発明において用いる非対称膜は特に限定されない
が、例えば芳香族ポリスルホン系、芳香族ポリアミド系
、芳香族ポリイミド系等が挙げられるが、特に耐塩素性
、耐pH性、耐熱性等の水系での耐久性を有するという
理由により、芳香族ポリスルホン系が好ましく用いられ
る。Furthermore, the asymmetric membrane used in the present invention is not particularly limited, but examples include aromatic polysulfone, aromatic polyamide, and aromatic polyimide. Aromatic polysulfones are preferably used because of their durability.
前記水不透過性膜の形状は特に限定されないが、中空系
状または平膜状が好ましく、不織布のような補強材上に
形成されていてもよい。Although the shape of the water-impermeable membrane is not particularly limited, it is preferably hollow or flat, and may be formed on a reinforcing material such as a nonwoven fabric.
かかる水不透過性112及びその膜を内蔵してなるモジ
ュールの形状は何ら限定されないが、通常中空糸状の膜
を束ねて内蔵させた所謂中空糸膜モジュールが好ましく
用いられる。 またそれ以外にシート状の膜を巻回して
なる所謂スパイラル型モジュールやその他の構造のモジ
ュールも用いることができる。Although the shape of the water-impermeable module 112 and the module containing the membrane thereof are not limited in any way, a so-called hollow fiber membrane module in which hollow fiber membranes are usually bundled and incorporated therein is preferably used. In addition, a so-called spiral type module formed by winding a sheet-like membrane or a module having another structure can also be used.
〔発明の効果]
本発明の方法によれば、従来の合成樹脂のチューブを用
いた場合に比べて、蒸気透過速度を大きくでき、かつ水
蒸気の透過を抑えることができるため、設備費、運転費
、メンテナンス費等が低減できるという利点がある。[Effects of the Invention] According to the method of the present invention, compared to the case of using conventional synthetic resin tubes, the vapor transmission rate can be increased and the permeation of water vapor can be suppressed, so equipment costs and operating costs can be reduced. This has the advantage that maintenance costs can be reduced.
〔実施例]
以下に実施例により本発明を説明するが、本発明はこれ
ら実施例に何ら限定されるものではない。[Examples] The present invention will be explained below with reference to Examples, but the present invention is not limited to these Examples at all.
以下において部は重量部を意味する。In the following, parts mean parts by weight.
実施例1
不織布上に形成されたポリスルホン多孔質膜上に、ポリ
(4−メチルペンテン−1)を1μmの厚みで形成させ
て複合膜を得た。 かかる複合膜の30°Cにおける窒
素ガス透過速度は、0.75Nrrr/rd−h −a
tmであった。Example 1 A composite membrane was obtained by forming poly(4-methylpentene-1) to a thickness of 1 μm on a polysulfone porous membrane formed on a nonwoven fabric. The nitrogen gas permeation rate of this composite membrane at 30°C is 0.75Nrrr/rd-h-a
It was tm.
かかる膜(膜面積r 140c+fl)の一方に、溶
存酸素8.llppm (25°C)の超純水250
−を、流速20cm/Sで180分間循環し、他方を真
空ポンプにより真空度−759mm11gに保った結果
、溶存酸素濃度は0.008PPm、水蒸気透過量は2
1.2g/rrf−h −armになった。On one side of such a membrane (membrane area r 140c+fl), dissolved oxygen 8. llppm (25°C) ultrapure water 250
- was circulated at a flow rate of 20 cm/s for 180 minutes, and the other side was maintained at a vacuum level of -759 mm and 11 g using a vacuum pump. As a result, the dissolved oxygen concentration was 0.008 PPm, and the amount of water vapor permeation was 2.
It became 1.2g/rrf-h-arm.
実施例2
実施例1において、真空度を25°Cにおける飽和水蒸
気圧23mm11gを除いた−737 mm11gとし
た以外は、実施例1と同様に処理した結果、溶存酸素濃
度は0、009ppm、水蒸気透過量は1.5 g/r
l(−h −atmになった。Example 2 The same procedure as in Example 1 was carried out except that the degree of vacuum was -737 mm and 11 g, excluding the saturated water vapor pressure of 23 mm and 11 g at 25°C. As a result, the dissolved oxygen concentration was 0.009 ppm, and the water vapor permeation was The amount is 1.5 g/r
l(-h - became atm.
実施例3
実施例2における超純水温度を50″Cにし、飽和水蒸
気圧92mm11gを除いた−668 mm11gとし
た以外は、実施例2と同様に処理した結果、溶存酸素濃
度は0.007ppm、水蒸気透過量は15.3g/n
L h −atmになった。Example 3 The same process as in Example 2 was performed except that the ultrapure water temperature in Example 2 was 50"C and the saturated water vapor pressure was -668 mm11 g excluding 92 mm11 g. As a result, the dissolved oxygen concentration was 0.007 ppm, Water vapor permeation amount is 15.3g/n
It became Lh-ATM.
実施例4
実施例1で得た膜を用いて、膜面積6.65n(のスパ
イラル型モジュールを成型し、真空度−720M11[
の状態で、溶存酸素8.llppm (25°C)の
超純水を流12.5t/hで通水した結果、出口溶存酸
素濃度は、0.495ppmになった。Example 4 Using the membrane obtained in Example 1, a spiral type module with a membrane area of 6.65n was molded and the vacuum degree was -720M11 [
Dissolved oxygen in the state of 8. As a result of passing ultrapure water of 1ppm (25°C) at a flow rate of 12.5t/h, the outlet dissolved oxygen concentration was 0.495ppm.
実施例5
実施例1における真空の代わりに、純窒素ガス(99,
99χ)を流量201 /minで流すこと以外、実施
例1と同様の方法で得られた超純水酸素濃度は0゜O2
0ppmであった。Example 5 Instead of vacuum in Example 1, pure nitrogen gas (99,
The oxygen concentration of ultrapure water obtained in the same manner as in Example 1 except that 99χ) was flowed at a flow rate of 201/min was 0°O2.
It was 0 ppm.
実施例6
純窒素ガスを十分に脱ガスされた25°Cの超純水中へ
暴気しながら、飽和水蒸気を含む純窒素ガスとしたもの
を、実施例5と同様の方法で処理した結果、得られた超
純水酸素濃度は0.O20ppmであった。Example 6 Results of treating pure nitrogen gas containing saturated water vapor in the same manner as in Example 5 by aerating pure nitrogen gas into sufficiently degassed ultrapure water at 25°C. , the obtained ultrapure water oxygen concentration was 0. O was 20 ppm.
実施例7
実施例1における真空の代わりに、亜硫酸ナトリウム飽
和水溶液を流速5 cyn / Sで流すこと以外、実
施例1と同様の方法で得られた溶存酸素濃度は、0.2
35ppmであった。Example 7 The dissolved oxygen concentration obtained in the same manner as in Example 1, except that instead of the vacuum in Example 1, a saturated aqueous sodium sulfite solution was flowed at a flow rate of 5 cyn/S, the dissolved oxygen concentration was 0.2
It was 35 ppm.
実施例8
実施例1における超純水の代わりに、2%エタノール水
溶液を流した以外は実施例1と同様に処理した結果、得
られたエタノール溶液の濃度は、0.27%であった。Example 8 The same procedure as in Example 1 was carried out except that a 2% aqueous ethanol solution was flowed instead of the ultrapure water in Example 1. As a result, the concentration of the obtained ethanol solution was 0.27%.
実施例9
実施例8におけるエタノール濃度を0.2%とした以外
は実施例8と同様の方法で得られた溶液のエタノール濃
度は、0.045%であった。Example 9 The ethanol concentration of a solution obtained in the same manner as in Example 8 except that the ethanol concentration in Example 8 was 0.2% was 0.045%.
(以上 )(that's all )
Claims (7)
沸点揮発性有機物が溶解している水溶液を接触させ、他
方を、該水溶液成分の蒸気圧をゼロに近づけることによ
り、透過する溶解成分を除去することを特徴とする気体
もしくは低沸点揮発性有機物の除去方法。(1) Through a water-impermeable membrane, one side is brought into contact with an aqueous solution in which a gas or a low-boiling volatile organic substance is dissolved, and the other side is permeated by bringing the vapor pressure of the aqueous solution components close to zero. A method for removing gases or low-boiling volatile organic substances, characterized by removing dissolved components.
、真空ポンプ等で機械的に透過成分を除去することを特
徴とする請求項(1)記載の気体もしくは低沸点揮発性
有機物の除去方法。(2) The method for removing gases or low-boiling volatile organic substances according to claim (1), wherein the method for bringing the vapor pressure of the aqueous solution components close to zero includes mechanically removing the permeated components using a vacuum pump or the like.
げないことにより、水蒸気の透過量を抑制することを特
徴とする請求項(2)記載の気体もしくは低沸点揮発性
有機物の除去方法。(3) The method for removing gases or low-boiling volatile organic substances according to claim (2), characterized in that the amount of permeation of water vapor is suppressed by not lowering the degree of vacuum below the saturated water vapor pressure at the operating temperature.
、不活性ガスを流して、透過成分を除去することを特徴
とする請求項(1)記載の気体もしくは低沸点揮発性有
機物の除去方法。(4) The method for removing gases or low-boiling volatile organic substances according to claim (1), characterized in that the method for bringing the vapor pressure of the aqueous solution components close to zero is to remove the permeated components by flowing an inert gas.
を流すことにより、水蒸気の透過量を抑制することを特
徴とする請求項(4)記載の気体もしくは低沸点揮発性
有機物の除去方法。(5) The method for removing gases or low-boiling volatile organic substances according to claim (4), characterized in that the amount of permeation of water vapor is suppressed by flowing an inert gas that is in equilibrium with saturated water vapor at the operating temperature.
、透過成分と化学反応する成分を流して、透過成分を除
去することを特徴とする請求項(1)記載の気体もしく
は低沸点揮発性有機物の除去方法。(6) The gas or low-boiling volatile organic substance according to claim (1), characterized in that the method for bringing the vapor pressure of the aqueous solution component close to zero is to remove the permeated component by flowing a component that chemically reacts with the permeated component. How to remove.
、透過成分が水より溶解度の高い溶媒を流して、透過成
分を除去することを特徴とする請求項(1)記載の気体
もしくは低沸点揮発性有機物の除去方法。(7) The method of bringing the vapor pressure of the aqueous solution component close to zero is to remove the permeated component by flowing a solvent in which the permeated component has a higher solubility than water. How to remove organic matter.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP972490A JP2954629B2 (en) | 1990-01-18 | 1990-01-18 | Removal method of gas or low boiling volatile organic matter |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP972490A JP2954629B2 (en) | 1990-01-18 | 1990-01-18 | Removal method of gas or low boiling volatile organic matter |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH03213103A true JPH03213103A (en) | 1991-09-18 |
| JP2954629B2 JP2954629B2 (en) | 1999-09-27 |
Family
ID=11728253
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP972490A Expired - Lifetime JP2954629B2 (en) | 1990-01-18 | 1990-01-18 | Removal method of gas or low boiling volatile organic matter |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2954629B2 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6315815B1 (en) * | 1999-12-16 | 2001-11-13 | United Technologies Corporation | Membrane based fuel deoxygenator |
-
1990
- 1990-01-18 JP JP972490A patent/JP2954629B2/en not_active Expired - Lifetime
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6315815B1 (en) * | 1999-12-16 | 2001-11-13 | United Technologies Corporation | Membrane based fuel deoxygenator |
Also Published As
| Publication number | Publication date |
|---|---|
| JP2954629B2 (en) | 1999-09-27 |
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