JP2928536B2 - Sterilization method of composite reverse osmosis membrane separation device - Google Patents

Sterilization method of composite reverse osmosis membrane separation device

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Publication number
JP2928536B2
JP2928536B2 JP1112992A JP11299289A JP2928536B2 JP 2928536 B2 JP2928536 B2 JP 2928536B2 JP 1112992 A JP1112992 A JP 1112992A JP 11299289 A JP11299289 A JP 11299289A JP 2928536 B2 JP2928536 B2 JP 2928536B2
Authority
JP
Japan
Prior art keywords
reverse osmosis
composite reverse
osmosis membrane
membrane
chlorine
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.)
Expired - Fee Related
Application number
JP1112992A
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Japanese (ja)
Other versions
JPH02293027A (en
Inventor
忠廣 植村
哲男 井上
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
TORE KK
Original Assignee
TORE KK
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Priority to JP1112992A priority Critical patent/JP2928536B2/en
Publication of JPH02293027A publication Critical patent/JPH02293027A/en
Application granted granted Critical
Publication of JP2928536B2 publication Critical patent/JP2928536B2/en
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Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124Water desalination
    • Y02A20/131Reverse-osmosis
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124Water desalination
    • Y02A20/138Water desalination using renewable energy
    • Y02A20/144Wave energy

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  • Separation Using Semi-Permeable Membranes (AREA)

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は、逆浸透法による造水装置に関するものであ
り、特に、超純水、カン水淡水化、廃水再利用などの造
水装置に関する。
Description: TECHNICAL FIELD The present invention relates to a desalination apparatus by a reverse osmosis method, and particularly to a desalination apparatus such as ultrapure water, canned water desalination, and wastewater reuse. .

[従来の技術] 膜による分離技術は、海水及びかん水の淡水化、工業
廃水処理、医療、工業用純水の製造など、幅広い分野に
おいて利用されている。その中で、微生物による膜分離
装置汚染は、被処理液中の微粒子として超純水の水質を
悪化したり、膜面上に菌体が繁殖し、微生物およびその
代謝物などから成る有機性物質が付着し、膜の水透過性
を低下させるなど問題を生じるため、膜分離装置の殺菌
は重要である。そのため膜分離装置の微生物殺菌方法が
種々提案されており、一般的な方法としては、殺菌剤を
常時、あるいは間欠的に膜に接触する方法がとられてい
る。
[Prior Art] A membrane separation technology is used in a wide range of fields such as desalination of seawater and brackish water, industrial wastewater treatment, medical treatment, and production of industrial pure water. Among them, contamination of the membrane separation device by microorganisms may deteriorate the water quality of ultrapure water as fine particles in the liquid to be treated, or bacteria may grow on the membrane surface, and organic substances composed of microorganisms and their metabolites Therefore, sterilization of the membrane separation device is important because it causes problems such as the decrease in water permeability of the membrane. For this reason, various methods for disinfecting microorganisms in a membrane separation device have been proposed. As a general method, a method in which a disinfectant is constantly or intermittently brought into contact with a membrane is employed.

殺菌剤としては、古くから塩素系の試薬が広く用いら
れてきたが、従来の非対称酢酸セルロース膜に変わって
高性能な複合逆浸透膜が出現し、非対称酢酸セルロース
膜に対して耐塩素性が劣るため、クロラミン類、過酸化
水素、過酢酸、亜硫酸水素ナトリウムなど塩素に代わる
種々の新しい殺菌方法が提案されている。しかし、これ
らの殺菌剤は塩素に比べて価格が高い、殺菌力が弱い、
取扱が困難といった問題があり、複合逆浸透膜の高性能
を生かした運転が為されていないのが現状であった。
As a disinfectant, chlorine-based reagents have been widely used since ancient times, but high-performance composite reverse osmosis membranes have appeared in place of conventional asymmetric cellulose acetate membranes, and chlorine resistance to asymmetric cellulose acetate membranes has been demonstrated. Because of their inferiority, various new sterilization methods have been proposed to replace chlorine such as chloramines, hydrogen peroxide, peracetic acid, and sodium bisulfite. However, these disinfectants are more expensive than chlorine, have lower disinfecting power,
At present, there is a problem that handling is difficult, and operation utilizing the high performance of the composite reverse osmosis membrane has not been performed.

工業的に利用されている複合逆浸透膜としては、ポリ
スルホン多孔性支持膜に実質的に膜性能を司る活性層を
被覆した複合逆浸透膜、特にポリアミド系の素材を活性
層の素材として用いた膜が高性能であり、特にある程度
の耐塩素性を有しかつ性能の高い膜として特開昭55−14
7106号公報、特開昭61−42302号公報、特開昭62−12160
3号公報等の架橋芳香族ポリアミド系膜が注目されてい
る。
As a composite reverse osmosis membrane used industrially, a composite reverse osmosis membrane in which a polysulfone porous support membrane is coated with an active layer that substantially controls the membrane performance, particularly a polyamide-based material is used as the active layer material. The membrane has a high performance, and particularly has a certain degree of chlorine resistance and high performance.
No. 7106, JP-A-61-42302, JP-A-62-12160
A crosslinked aromatic polyamide-based film such as that disclosed in Japanese Patent Publication No. 3 has been noted.

[発明が解決しようとする課題] 本発明者らはこのような複合逆浸透膜を用いた膜分離
装置によって造水を行う際に、特に問題となる殺菌用の
塩素による膜性能の変動、すなわち殺菌処理によって膜
性能が低下する問題について鋭意検討を行い、特に高い
脱塩性能と高い造水量を同時に有する複合逆浸透膜の塩
素殺菌を行う際に、ポリ燐酸塩の添加を行うことによ
り、塩素による性能低下が顕著に抑制できることを見出
だし本発明に到達した。
[Problems to be Solved by the Invention] The present inventors, when performing water production by a membrane separation device using such a composite reverse osmosis membrane, the fluctuation of the membrane performance due to chlorine for sterilization, which is particularly problematic, Intensive study on the problem that the membrane performance is reduced by the sterilization process, especially when performing chlorine sterilization of a composite reverse osmosis membrane having high desalination performance and high water production at the same time, by adding polyphosphate, chlorine The present inventors have found that the performance degradation due to the above can be remarkably suppressed, and reached the present invention.

[課題を解決するための手段] 上記目的を達成するため本発明は下記の構成を有す
る。
[Means for Solving the Problems] To achieve the above object, the present invention has the following constitution.

すなわち、 『残留塩素含有水溶液を用いて複合逆浸透膜分離装置を
殺菌する際に、ポリ燐酸塩を該水溶液に5〜10ppm添加
することを特徴とする複合逆浸透膜装置の殺菌方法。』
に関する。
That is, "a method for sterilizing a composite reverse osmosis membrane device, comprising adding 5 to 10 ppm of a polyphosphate to the aqueous solution when the composite reverse osmosis membrane separation device is sterilized using a residual chlorine-containing aqueous solution. 』
About.

本発明において、残留塩素とは、遊離塩素と結合塩素
の合計をいい、残留塩素の測定は、オルトトリジン法な
どによって、簡単に行うことができ、その方法は、JIS
−K0101に記載されている。通常の膜分離装置の殺菌の
ためには、残留塩素は水溶液中に0.1〜10ppm程度必要と
されている。しかし、この殺菌のための残留塩素の必要
量は、複合逆浸透膜を使用した造水装置における被処理
液の性状と装置の微生物繁殖状態に拠って変えられるべ
きであり、被処理液中の生菌数、有機成分濃度、微生物
によるシステムの造水量低下率等によって決定される。
In the present invention, residual chlorine refers to the sum of free chlorine and bound chlorine, and the measurement of residual chlorine can be easily performed by an ortho-tolidine method or the like, and the method is JIS.
-K0101. For disinfection of a normal membrane separation device, about 0.1 to 10 ppm of residual chlorine is required in an aqueous solution. However, the required amount of residual chlorine for this sterilization should be changed depending on the properties of the liquid to be treated in the fresh water generator using the composite reverse osmosis membrane and the microorganism propagation state of the apparatus, and It is determined by the number of viable bacteria, the concentration of organic components, the rate of decrease in the amount of fresh water produced in the system by microorganisms, etc.

複合逆浸透膜分離装置に対して塩素による殺菌を行う
場合、複合逆浸透膜の耐塩素性と分離装置の微生物繁殖
状態とを考慮して、殺菌の頻度を決定する必要がある
が、通常は1日1時間程度から1週間1時間程度の間欠
的に行う場合が多く、必要残留塩素濃度も0.1〜10ppmと
異なり、通常の河川水や井戸水の場合には、0.1〜1ppm
で十分な場合が多い。、 本発明において、ポリ燐酸塩とは、ヘキサメタ燐酸ナ
トリウムを代表とする分子内に2個以上の燐原子を有し
アルカリ金属、アルカリ土類金属と酸素原子等により結
合した重合無機燐酸系物質を言う。代表的なポリ燐酸塩
としてピロ燐酸4ナトリウム、ピロ燐酸2ナトリウム、
トリポリ燐酸ナトリウム、テトラポリ燐酸ナトリウム、
ヘプタポリ燐酸ナトリウム、デカポリ燐酸ナトリウム、
メタ燐酸ナトリウム、ヘキサメタ燐酸ナトリウム、およ
びこれらのカリウム塩などがあげられる。
When performing sterilization with chlorine on the composite reverse osmosis membrane separator, it is necessary to determine the frequency of sterilization in consideration of the chlorine resistance of the composite reverse osmosis membrane and the microorganism propagation state of the separator, but usually it is necessary to determine the frequency of sterilization. It is often performed intermittently from about 1 hour a day to about 1 hour a week, and the required residual chlorine concentration is different from 0.1 to 10 ppm. For ordinary river water and well water, 0.1 to 1 ppm
Is often sufficient. In the present invention, a polyphosphate is a polymerized inorganic phosphate-based substance having two or more phosphorus atoms in a molecule represented by sodium hexametaphosphate and bonded to an alkali metal or an alkaline earth metal by an oxygen atom or the like. To tell. Representative polyphosphates include tetrasodium pyrophosphate, disodium pyrophosphate,
Sodium tripolyphosphate, sodium tetrapolyphosphate,
Sodium heptapolyphosphate, sodium decapolyphosphate,
Examples include sodium metaphosphate, sodium hexametaphosphate, and potassium salts thereof.

本発明において、複合逆浸透膜分離装置とは、造水、
濃縮などの目的で被処理液を加圧下で複合逆浸透膜モジ
ュールに供給し、透過液と濃縮液に分離するための装置
をいい、通常は、複合逆浸透膜エレメント、耐圧容器、
加圧ポンプなどで構成されている。
In the present invention, the composite reverse osmosis membrane separation device, fresh water,
A device for supplying the liquid to be treated to the composite reverse osmosis membrane module under pressure for the purpose of concentration and the like, and separating it into a permeate and a concentrate, usually a composite reverse osmosis membrane element, a pressure vessel,
It is composed of a pressure pump and the like.

複合逆浸透膜としては、ポリアミド系の活性層を有す
る膜、特に、架橋芳香族ポリアミド系の活性層を有する
膜に対して本発明を適用すると有効である。
As the composite reverse osmosis membrane, it is effective to apply the present invention to a membrane having a polyamide-based active layer, particularly a membrane having a crosslinked aromatic polyamide-based active layer.

この様な膜は、一般にはポリスルホンなどの多孔性支
持膜上で、芳香族アミンと多官能酸塩化物とを、InSitu
法と呼ばれる界面重縮合反応を利用した方法によって反
応させ、架橋芳香族ポリアミドの超薄膜(活性層)を形
成して製造される。この種の膜は複合逆浸透膜のうちで
は比較的耐塩素性が良く、膜性能が顕著に低下するまで
に、例えば1ppmの塩素に対して約1000時間の接触が可能
と言われている。
In general, such a membrane is prepared by depositing an aromatic amine and a polyfunctional acid chloride on a porous support membrane such as polysulfone.
It is manufactured by forming an ultrathin film (active layer) of a cross-linked aromatic polyamide by reacting by a method utilizing an interfacial polycondensation reaction called a method. It is said that this type of membrane has relatively good chlorine resistance among composite reverse osmosis membranes, and that it can be contacted with, for example, 1 ppm of chlorine for about 1000 hours before the membrane performance is significantly reduced.

しかし、本発明者らは、実際にこれらの複合逆浸透膜
を分離装置に組み込んで使用すると、予想されている塩
素接触時間よりもはるかに早く膜性能が低下することが
わかり、鉄錆などの重金属によって膜の塩素劣化が触媒
され、加速されているものと推定し、さらにこれを防止
するにはポリ燐酸塩の添加が効果的であることを見出だ
した。
However, the present inventors have found that when these composite reverse osmosis membranes are actually incorporated into a separation apparatus and used, the membrane performance is reduced much faster than the expected chlorine contact time, and iron rust and the like are found. It is presumed that chlorine degradation of the film is catalyzed and accelerated by heavy metals, and it has been found that the addition of polyphosphate is effective in preventing this.

ポリ燐酸塩は逆浸透分離装置の運転において、海水や
硬水中の炭酸カルシウムなどのスケール防止剤として、
また配管材料の金属に対して防錆剤として用いられる試
薬であり、この様な場合通常10ppm以上の添加量が必要
である。
In the operation of reverse osmosis separation equipment, polyphosphate is used as a scale inhibitor such as calcium carbonate in seawater or hard water.
Further, it is a reagent used as a rust preventive for the metal of the piping material. In such a case, an addition amount of usually 10 ppm or more is necessary.

しかし、本発明においては、ポリ燐酸塩は重金属封鎖
剤として、被処理液や殺菌に使用する塩素水溶液、ある
いは、膜面に存在する鉄などの重金属に作用し、重金属
とキレート化合物を形成し、重金属の触媒作用を封じて
いるものと考えられる。通常の塩素殺菌を行うために、
ポリ燐酸塩は水溶液中に5〜10ppm程度添加すれば十分
である。添加量が5ppm以下の場合、重金属の触媒作用を
十分に防止できないため塩素による殺菌に際して複合逆
浸透膜の性能低下が加速され、また10ppm以上では、透
過水の水質が悪化して好ましくない。
However, in the present invention, the polyphosphate acts as a heavy metal sequestering agent, a chlorine solution used for the liquid to be treated or sterilization, or acts on a heavy metal such as iron present on the film surface to form a chelate compound with the heavy metal. It is thought that it blocks the catalytic action of heavy metals. To perform normal chlorine sterilization,
It is sufficient to add about 5 to 10 ppm of the polyphosphate to the aqueous solution. When the addition amount is 5 ppm or less, the catalytic action of heavy metals cannot be sufficiently prevented, so that the performance of the composite reverse osmosis membrane deteriorates during sterilization with chlorine.

複合逆浸透膜エレメントの型式は、スパイラル型、チ
ューブラー型、中空系型などが一般に用いられ、本発明
はどれにも適用可能である。
As the type of the composite reverse osmosis membrane element, a spiral type, a tubular type, a hollow type and the like are generally used, and the present invention can be applied to any type.

殺菌に用いる水溶液としては、通常河川水や地下水な
どのかん水や造水システムで得られた純水をもちいるこ
とができる。水溶液のpHは、用いる膜の耐加水分解性、
配管等の部材の腐蝕性などを考慮して決定されるが、一
般にpH4〜7、好ましくは、5〜6.5程度の範囲にするの
が好ましい。
As the aqueous solution used for sterilization, it is possible to use usually irrigation water such as river water or groundwater or pure water obtained by a desalination system. The pH of the aqueous solution depends on the hydrolysis resistance of the membrane used,
The pH is determined in consideration of the corrosiveness of members such as piping, etc., but is generally in the range of pH 4 to 7, preferably 5 to 6.5.

[実施例] 以下の実施例によって更に詳細に説明するが、本発明
はこれら実施例により何ら限定されるものではない。
[Examples] The present invention will be described in more detail with reference to the following examples, but the present invention is not limited to these examples.

なお、実施例において、排除(脱塩)率は、次式によ
り求めた。
In Examples, the exclusion (desalting) rate was determined by the following equation.

実施例1 原水に地下水を井戸で汲み上げた水をもちい、この水
に塩素1ppm、ヘキサメタ燐酸ナトリウムを7ppmを添加
し、硫酸でpHを6.7に調整した後、熱交換器で水温を25
℃に調節した。この時の原水の導電率は、約200μS/cm
であった。高圧ポンプで15気圧に加圧した原水を、東レ
製複合逆浸透膜エレメントSU−710に供給し、回収率10
%でこの逆浸透装置の運転を1000時間行なった。運転中
の透過水量と透過水質の変化を表1にまとめた。
Example 1 Groundwater was pumped from a well into raw water, 1 ppm of chlorine and 7 ppm of sodium hexametaphosphate were added to the water, and the pH was adjusted to 6.7 with sulfuric acid.
Adjusted to ° C. The conductivity of the raw water at this time is about 200 μS / cm
Met. Raw water pressurized to 15 atm with a high-pressure pump is supplied to Toray's composite reverse osmosis membrane element SU-710, and a recovery rate of 10
% Of this reverse osmosis device was operated for 1000 hours. The amount of permeated water and the change in permeated water quality during operation are summarized in Table 1.

実施例2 実施例1の原水に、さらにニッケル、クロム、銅を各
0.1ppm添加し、その他の条件を同じにして1000時間の運
転を行なった。運転中の透過水質の変化を表1にまとめ
た。
Example 2 To the raw water of Example 1, nickel, chromium and copper were further added.
0.1 ppm was added, and the operation was performed for 1000 hours under the same other conditions. Table 1 summarizes changes in permeated water quality during operation.

比較例1 実施例1において、ヘキサメタ燐酸ナトリウムを添加
せずに、その他の条件を同じにして1000時間の運転を行
なった。運転中の透過水質の変化を表1にまとめた。
Comparative Example 1 The same operation as in Example 1 was performed except that sodium hexametaphosphate was not added and the other conditions were the same, and the operation was performed for 1000 hours. Table 1 summarizes changes in permeated water quality during operation.

比較例2 実施例2において、ヘキサメタ燐酸ナトリウムを添加
せずに、その他の条件を同じにして1000時間の運転を行
なった。運転中の透過水質の変化を表1にまとめた。
Comparative Example 2 The same operation as in Example 2 was performed except that sodium hexametaphosphate was not added and the other conditions were the same, and the operation was performed for 1000 hours. Table 1 summarizes changes in permeated water quality during operation.

比較例3 実施例2において、ヘキサメタ燐酸ナトリウムを20pp
m添加し、その他の条件を同じにして1000時間の運転を
行なった。運転中の透過水質の変化を表1にまとめた。
Comparative Example 3 In Example 2, 20 pp of sodium hexametaphosphate was used.
m, and the operation was performed for 1000 hours under the same other conditions. Table 1 summarizes changes in permeated water quality during operation.

[発明の効果] 本発明により、従来高性能でありながら殺菌の難しさ
により、使用範囲の限られていた複合逆浸透膜による造
水が、ヘキサメタ燐酸ナトリウムを少量添加することに
より、経済性良く、また、信頼性良く行うことが可能と
なった。
[Effects of the Invention] According to the present invention, water production by a composite reverse osmosis membrane whose use range is limited due to the difficulty of sterilization while having high performance has been improved by adding a small amount of sodium hexametaphosphate, thereby improving economical efficiency. In addition, it has become possible to carry out with high reliability.

Claims (7)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】残留塩素含有水溶液を用いて複合逆浸透膜
分離装置を殺菌する際に、ポリ燐酸塩を該水溶液に5〜
10ppm添加することを特徴とする複合逆浸透膜装置の殺
菌方法。
(1) When sterilizing a composite reverse osmosis membrane separation device using a residual chlorine-containing aqueous solution, a polyphosphate is added to the aqueous solution in an amount of 5 to 50%.
A method for sterilizing a composite reverse osmosis membrane device, comprising adding 10 ppm.
【請求項2】0.1〜10ppmの残留塩素と5〜10ppmのポリ
燐酸塩とを含有する水溶液を用いることを特徴とする請
求項1記載の殺菌方法。
2. The method according to claim 1, wherein an aqueous solution containing 0.1 to 10 ppm of residual chlorine and 5 to 10 ppm of polyphosphate is used.
【請求項3】ポリ燐酸塩がヘキサメタ燐酸塩であること
を特徴とする請求項1記載の殺菌方法。
3. The method according to claim 1, wherein the polyphosphate is hexametaphosphate.
【請求項4】水溶液のpHが、4〜7であることを特徴と
する請求項1記載の殺菌方法。
4. The sterilization method according to claim 1, wherein the pH of the aqueous solution is 4-7.
【請求項5】水溶液のpHが、5〜6.5であることを特徴
とする請求項1記載の殺菌方法。
5. The sterilization method according to claim 1, wherein the pH of the aqueous solution is 5 to 6.5.
【請求項6】複合逆浸透膜が、ポリアミド系膜であるこ
とを特徴とする請求項1記載の殺菌方法。
6. The sterilization method according to claim 1, wherein the composite reverse osmosis membrane is a polyamide-based membrane.
【請求項7】複合逆浸透膜が、芳香族ポリアミド系膜で
あることを特徴とする請求項1記載の殺菌方法。
7. The sterilization method according to claim 1, wherein the composite reverse osmosis membrane is an aromatic polyamide-based membrane.
JP1112992A 1989-05-02 1989-05-02 Sterilization method of composite reverse osmosis membrane separation device Expired - Fee Related JP2928536B2 (en)

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JP2928536B2 true JP2928536B2 (en) 1999-08-03

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Publication number Priority date Publication date Assignee Title
JPH08108048A (en) 1994-10-12 1996-04-30 Toray Ind Inc Reverse osmosis separator and reverse osmosis separating method
JP4580589B2 (en) * 2001-06-15 2010-11-17 アムテック株式会社 Cleaning method of separation membrane

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