JP2012056874A - Method of treating cooling water system and treating agent set used therein - Google Patents

Method of treating cooling water system and treating agent set used therein Download PDF

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JP2012056874A
JP2012056874A JP2010200952A JP2010200952A JP2012056874A JP 2012056874 A JP2012056874 A JP 2012056874A JP 2010200952 A JP2010200952 A JP 2010200952A JP 2010200952 A JP2010200952 A JP 2010200952A JP 2012056874 A JP2012056874 A JP 2012056874A
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cooling water
slime
water system
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surfactant
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Shohei Shobu
昌平 菖蒲
Isao Matsunaga
功 松永
Kojiro Yanagisawa
浩次郎 柳澤
Yoshiteru Miyama
義輝 三山
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Swing Corp
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Swing Corp
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Abstract

PROBLEM TO BE SOLVED: To provide a slime peeling/sterilizing method which excels in the slime peeling effect and the sterilizing effect on microorganisms, furthermore has low corrosiveness and high safety, reduces the amount of a chemical used, and has high workability in the opened circulation water cooling system.SOLUTION: The treating method comprises incorporating a chlorine based oxidizing agent into the cooling water system in the first half of slime peeling and sterilization of microorganisms in the cooling water system and incorporating a surface active agent based drug into the cooling water system in the latter half.

Description

本発明は、開放型循環水式冷却水系において、スライムの剥離及び微生物の殺菌を両立させた処理方法およびそれに用いる処理剤セットに関するものである。   The present invention relates to a treatment method that achieves both exfoliation of slime and sterilization of microorganisms in an open circulating water cooling water system, and a treatment agent set used therefor.

開放型循環水式冷却水系では、細菌、真菌、藻類などの微生物群から構成されるスライムが系内に発生し、配管類や熱交換器などに付着し、通水配管の閉塞、熱効率の低下および配管類や熱交換器の局部腐食などのスライム障害の原因となる。また、スライムは細胞内寄生性のあるレジオネラ属菌等の温床となり、レジオネラ感染症などの人体への影響の原因にもなる。
このようなスライム障害の対策として、薬剤によるスライム剥離処理および殺菌処理が行われている。薬剤としては、従来から次亜塩素酸ナトリウム等の塩素系酸化剤、ヒドラジン、過酸化水素などが知られている。
In an open-type circulating water cooling water system, slime composed of microorganisms such as bacteria, fungi, and algae is generated in the system and adheres to piping and heat exchangers. In addition, it may cause slime failure such as local corrosion of piping and heat exchangers. In addition, the slime becomes a hotbed of Legionella spp. That have intracellular parasitism, and it also causes effects on the human body such as Legionella infection.
As a countermeasure against such slime failure, a slime peeling treatment and a sterilization treatment with a drug are performed. Conventionally known chemical agents include chlorine-based oxidizing agents such as sodium hypochlorite, hydrazine, and hydrogen peroxide.

次亜塩素酸ナトリウムによる処理では、殺菌スペクトル範囲が広く、細菌、真菌、藻類などの微生物群に対する殺菌効果は高いが、分散効果は低く、スライム剥離効果は低い。また、高濃度で添加した場合、配管などの金属材質の腐食が発生する問題がある。
ヒドラジンによる処理では、分散効果が高く、スライム剥離効果は高いが、細菌、真菌、藻類などの微生物群に対する殺菌効果は低い。また、発がん性物質であり、人体に対して毒性が高い。
The treatment with sodium hypochlorite has a wide sterilization spectrum range and a high sterilization effect against microbial groups such as bacteria, fungi and algae, but a low dispersion effect and a low slime peeling effect. In addition, when added at a high concentration, there is a problem that corrosion of metal materials such as piping occurs.
The treatment with hydrazine has a high dispersion effect and a high slime peeling effect, but a low bactericidal effect on microbial groups such as bacteria, fungi and algae. In addition, it is a carcinogen and is highly toxic to the human body.

過酸化水素による処理では、発泡によるスライム剥離効果は高いが、スライム剥離効果を得るのに必要な薬品使用量が多く、薬品コストの増大や作業性の悪化などの問題がある。また、廃液の中和処理を必要とするため、薬品コストはさらに増大する。
細菌、真菌、藻類などの微生物群の殺菌処理のみ、または、スライムの剥離処理のみでは、処理後に微生物群が増殖し易く、再びスライムを形成し、スライム障害の解決には至らない。
In the treatment with hydrogen peroxide, the slime peeling effect by foaming is high, but the amount of chemicals required for obtaining the slime peeling effect is large, and there are problems such as an increase in chemical cost and deterioration in workability. In addition, since the waste liquid needs to be neutralized, the chemical cost further increases.
Only sterilization treatment of microbial groups such as bacteria, fungi, and algae, or only slime exfoliation treatment easily proliferates microbial groups after the treatment, forms slime again, and does not solve the slime disorder.

このような中、二種以上の殺菌剤やスライム剥離剤を併用する技術も知られており、特許文献1には、塩素系酸化剤とスルファミン酸を併用するスライム剥離方法が、特許文献2には、次亜塩素酸塩等の遊離ハロゲン発生殺生物剤と、N−水素化合物等のハロゲン安定化剤(ヒダントイン等)及び4級アンモニウム系殺生物剤の混合物とを併用する殺菌及び殺スライム方法が、特許文献3には、前段でヒドラジンを、後段で次亜塩素酸塩又は次亜臭素酸塩を作用させるスライム剥離処理方法が、それぞれ記載されている。   Under such circumstances, a technique using two or more types of bactericides and slime removers is also known. Patent Document 1 discloses a slime peel method using a chlorine-based oxidizing agent and sulfamic acid in Patent Document 2. Is a sterilization and slime killing method using a combination of a free halogen-generating biocide such as hypochlorite and a mixture of a halogen stabilizer (such as hydantoin) such as an N-hydrogen compound and a quaternary ammonium biocide. However, Patent Document 3 describes a slime peeling treatment method in which hydrazine is used in the former stage and hypochlorite or hypobromite is used in the latter stage.

特開2003−267811号公報JP 2003-267811 A 特表2004−531579号公報JP-T-2004-531579 gazette 特開2004−12042号公報JP 2004-12042 A

殺菌剤やスライム剥離剤として知られる薬剤を併用することによって、単独で使用する場合に比して、それぞれ有利な点はあるものの、依然として十分満足できるスライム剥離効果及び微生物殺菌効果の両立は得られていない。
本発明は、開放型循環水式冷却水系において、上記従来の問題点を解決するものであり、スライム剥離効果および微生物殺菌効果に優れ、さらに、腐食性が低く、安全性が高く、薬品使用量が少なく、作業性が高いスライム剥離・殺菌方法、それに用いる薬剤を提供することを課題とする。
Combining a chemical known as a disinfectant or slime remover has advantages compared to the case where it is used alone, but both a slime exfoliation effect and a microbial disinfectant effect that are sufficiently satisfactory can still be obtained. Not.
The present invention solves the above-mentioned conventional problems in an open-type circulating water cooling water system, is excellent in slime peeling effect and microbial sterilization effect, and has low corrosiveness, high safety, and chemical use amount It is an object of the present invention to provide a slime peeling and sterilizing method with little workability and high workability, and a drug used therefor.

本発明は、上記課題を解決するものであり、下記(1)〜(6)の構成を有するものである。
(1)冷却水系のスライム剥離および微生物殺菌において、前段で塩素系酸化剤を冷却水系に含有させ、後段で界面活性剤系薬剤を冷却水系に含有させることを特徴とする処理方法。
(2)前段の塩素系酸化剤の添加量が、有効塩素として0.1〜1000mg/L、後段の界面活性剤系薬剤の添加量が、成分濃度として1〜1000mg/Lであることを特徴とする上記(1)に記載の処理方法。
(3)前段の塩素系酸化剤を添加してから0.1〜3時間後に後段の界面活性剤系薬剤を添加することを特徴とする上記(1)又は(2)に記載の処理方法。
(4)冷却水系内の温度を5〜70℃で処理することを特徴とする上記(1)〜(3)のいずれか1つに記載の処理方法。
(5)酸またはアルカリ剤を添加し、冷却水系内のpHを5〜12で処理することを特徴とする上記(1)〜(4)のいずれか1つに記載の処理方法。
(6)塩素系酸化剤含有薬剤及び界面活性剤系薬剤含有薬剤を組み合わせてなる、上記(1)〜(5)のいずれか1つに記載の処理方法に用いるための冷却水系処理剤セット。
This invention solves the said subject, and has the structure of following (1)-(6).
(1) A cooling water system slime peeling and microbial sterilization, wherein a chlorine-based oxidizing agent is contained in the cooling water system in the first stage, and a surfactant-based agent is contained in the cooling water system in the second stage.
(2) The addition amount of the former chlorinated oxidant is 0.1 to 1000 mg / L as effective chlorine, and the addition amount of the latter surfactant agent is 1 to 1000 mg / L as the component concentration. The processing method according to (1) above.
(3) The processing method according to (1) or (2) above, wherein the surfactant in the subsequent stage is added 0.1 to 3 hours after the addition of the chlorinated oxidizing agent in the preceding stage.
(4) The processing method according to any one of (1) to (3), wherein the temperature in the cooling water system is processed at 5 to 70 ° C.
(5) The treatment method according to any one of (1) to (4) above, wherein an acid or an alkali agent is added and the pH in the cooling water system is treated at 5 to 12.
(6) A cooling water treatment agent set for use in the treatment method according to any one of (1) to (5) above, which is a combination of a chlorine-based oxidizing agent-containing agent and a surfactant-based agent-containing agent.

本発明によれば、冷却水系のスライムに対して、前段で塩素系酸化剤を用いて、後段で界面活性剤系薬剤を用いて処理することにより、両者の相乗効果により、優れたスライム剥離効果および微生物殺菌効果が得られることが見出されたものであり、更に、金属腐食性が低く、人体影響や環境負荷が低く、薬剤使用量が少なく作業性の高い処理方法及び処理剤セットを提供することができる。   According to the present invention, a cooling water-based slime is treated with a chlorine-based oxidant in the former stage and a surfactant-based agent in the latter stage, so that a synergistic effect between the two results in an excellent slime peeling effect. In addition, it has been found that a sterilizing effect on microorganisms can be obtained, and further provides a treatment method and a treatment agent set with low metal corrosiveness, low human influence and environmental load, low chemical use, and high workability. can do.

本発明の処理方法を実施するための冷却水系の概要図である。It is a schematic diagram of the cooling water system for enforcing the processing method of the present invention.

本発明の処理方法は、開放型循環水式冷却水系において、冷却水に、前段で塩素系酸化剤を含有させ、後段で界面活性剤系薬剤を含有させて、冷却水系のスライム剥離及び微生物殺菌を行うものである。ここで、前記の「前段」とは、冷却水系の剥離処理の前段(前半)であり、「後段」とは同剥離処理の後段(後半)である。   In the treatment method of the present invention, in an open-type circulating water type cooling water system, the cooling water contains a chlorine-based oxidizing agent in the former stage and a surfactant-based agent in the latter stage, so that the slime removal and the microorganism sterilization of the cooling water system are performed. Is to do. Here, the “front stage” is a front stage (first half) of the cooling water system peeling process, and a “back stage” is a rear stage (second half) of the peeling process.

本発明の処理方法は、塩素系酸化剤と界面活性剤系薬剤の組み合わせは、両者を混合して用いることを意味するものではなく、冷却水系に塩素系酸化剤を適用した後、界面活性剤系薬剤を適用するという組み合わせであり、これにより、塩素系酸化剤と界面活性剤系薬剤との相乗効果が発揮され、優れたスライム剥離効果及び殺菌効果の両立が達成される。
塩素系酸化剤と界面活性剤系薬剤を同時に含有させても充分なスライム剥離効果及び殺菌効果の両立が得られない。これは、塩素系酸化剤と界面活性剤系薬剤が反応し、有効塩素が消費され、スライム剥離効果および微生物殺菌効果が低下するためと推定される。また、前段で界面活性剤系薬剤を含有させ、後段で塩素系酸化剤を含有させても、十分なスライム剥離効果が得られない。スライムは微生物の集合体であり、その表層は粘着性ポリマーで覆われており、スライムを形成している微生物層を保護している。そのため、通常の薬剤処理では、微生物層に薬剤が接触せず、スライムの剥離および殺菌を行うことは難しい。本発明方法では、高濃度の塩素系殺菌剤を前段で添加することで、表層の粘着性ポリマーを分解し、後段で添加する界面活性剤系薬剤と微生物層を接触し易くすることで、効果的にスライムの剥離および殺菌を行うことができるものと推定される。
In the treatment method of the present invention, the combination of the chlorine-based oxidant and the surfactant-based agent does not mean that both are mixed and used, and the surfactant is applied after the chlorine-based oxidant is applied to the cooling water system. This is a combination of applying a series of chemicals, whereby a synergistic effect between the chlorine-based oxidizing agent and the surfactant-based chemicals is exhibited, and both an excellent slime peeling effect and a bactericidal effect are achieved.
Even if a chlorine-based oxidizing agent and a surfactant-based agent are contained at the same time, sufficient compatibility between the slime peeling effect and the bactericidal effect cannot be obtained. This is presumably because the chlorine-based oxidizing agent and the surfactant-based agent react to consume effective chlorine, and the slime peeling effect and the microbial disinfection effect are reduced. Moreover, even if a surfactant-based agent is contained in the former stage and a chlorine-based oxidizing agent is contained in the latter stage, a sufficient slime peeling effect cannot be obtained. A slime is an aggregate of microorganisms, and its surface layer is covered with an adhesive polymer to protect the microorganism layer forming the slime. For this reason, in normal drug treatment, the drug does not come into contact with the microbial layer, and it is difficult to peel and sterilize the slime. In the method of the present invention, by adding a high-concentration chlorine-based disinfectant in the previous stage, the adhesive polymer in the surface layer is decomposed, and the surfactant-based drug added in the subsequent stage is easily brought into contact with the microorganism layer, thereby achieving an effect. It is estimated that the slime can be peeled and sterilized.

上記のとおり、本発明のスライム剥離処理用薬剤の塩素系酸化剤と界面活性剤系薬剤の組合せは、両者を混合して用いることを意味するものではなく、冷却水系に塩素系酸化剤を適用した後、界面活性剤系薬剤を適用するという使用方法を前提とする組合せである。本発明では、前段の塩素系酸化剤を添加して冷却水系内に有効に適用された後、後段の界面活性剤系薬剤を添加するものであり、前段と後段との間の添加時間は特に限定されるものではないが、好ましくは0.1〜3時間、より好ましくは0.1〜1時間の間に、後段の界面活性剤系薬剤を添加することで、冷却水系のスライムおよび微生物をより簡単に、より効率良く、剥離および殺菌することができる。適用する系にもよるが、3時間以上経過した後に添加した場合には、スライム剥離効果および微生物殺菌効果は得られにくくなり、好ましくない。   As described above, the combination of the chlorine-based oxidizing agent and the surfactant-based agent in the slime peeling treatment agent of the present invention does not mean that both are used in combination, and the chlorine-based oxidizing agent is applied to the cooling water system. After that, the combination is premised on the usage method of applying a surfactant-based drug. In the present invention, after adding the former chlorinated oxidant and being effectively applied in the cooling water system, the latter surfactant is added, and the addition time between the former and the latter is particularly Although it is not limited, it is preferable that the surfactant in the subsequent stage is added during 0.1 to 3 hours, more preferably 0.1 to 1 hour, so that the slime and microorganisms in the cooling water system can be removed. It can be stripped and sterilized more easily and more efficiently. Although it depends on the system to be applied, when it is added after 3 hours or more, the slime peeling effect and the microorganism sterilizing effect are hardly obtained, which is not preferable.

本発明では、後段で界面活性剤系薬剤を冷却水系に含有させた後、冷却水系を0.1時間以上循環させることにより、冷却水系のレジオネラ属菌等の微生物群を簡単に効率良く殺菌することができる。レジオネラ属菌等の温床となるアメーバやスライムに対しても殺菌作用がおよぶため、結果として、スライムの剥離作用を助長する。後段で界面活性剤系薬剤を適用した後の循環時間は、微生物の殺菌効果を得るには0.1時間以上、スライムの剥離効果を得るには1時間以上であることが好ましい。0.1時間未満の場合には、pH、温度によっては、微生物の殺菌効果が低下する。循環時間の上限は、種々の事情によって定まるものであり特に限定されないが、作業性の観点から、通常10時間程度、好ましくは6時間である。なお循環時間が長くなるほど、金属腐食性は高くなり易い。   In the present invention, after the surfactant agent is contained in the cooling water system in the subsequent stage, the cooling water system is circulated through the cooling water system for 0.1 hour or more to easily and efficiently sterilize the microorganism group such as Legionella spp. In the cooling water system. be able to. The bactericidal action is also exerted on amoeba and slime serving as a hotbed of Legionella spp., And as a result, the exfoliating action of the slime is promoted. The circulation time after the surfactant-based agent is applied in the latter stage is preferably 0.1 hour or more for obtaining the sterilizing effect of microorganisms and 1 hour or more for obtaining the slime peeling effect. In the case of less than 0.1 hour, the sterilizing effect of microorganisms decreases depending on the pH and temperature. The upper limit of the circulation time is determined by various circumstances and is not particularly limited, but is usually about 10 hours, preferably 6 hours, from the viewpoint of workability. The longer the circulation time, the higher the metal corrosivity.

前段で冷却水系に含有させる塩素系酸化剤は、塩素系の酸化剤であれば特に限定されるものではなく、例えば、亜塩素酸またはその塩であり、無機塩素系化合物である次亜塩素酸ナトリウム、次亜塩素酸カリウムや有機塩素系化合物である塩素化イソシアヌール酸などが挙げられる。その中で、次亜塩素酸ナトリウムが好ましい。添加量は、有効塩素として0.1〜1000mg/L、好ましくは10〜200mg/Lであるのが望ましい。添加量が有効塩素として0.1mg/L以上において、十分なスライムの剥離効果および微生物の殺菌効果が得られる。また、1000mg/L以下において、配管や熱交換器などの金属材質に対しての腐食の影響を小さく抑えることができる。   The chlorinated oxidant to be contained in the cooling water system in the previous stage is not particularly limited as long as it is a chlorinated oxidant. For example, hypochlorous acid which is chlorous acid or a salt thereof and is an inorganic chlorinated compound. Examples thereof include sodium, potassium hypochlorite and chlorinated isocyanuric acid which is an organic chlorine-based compound. Among them, sodium hypochlorite is preferable. The addition amount is 0.1 to 1000 mg / L, preferably 10 to 200 mg / L as effective chlorine. When the added amount is 0.1 mg / L or more as effective chlorine, a sufficient slime peeling effect and microbial bactericidal effect can be obtained. Moreover, at 1000 mg / L or less, the influence of corrosion on metal materials such as pipes and heat exchangers can be suppressed to a low level.

後段で冷却水系に含有させる界面活性剤系薬剤は、アニオン性界面活性剤、カチオン性界面活性剤、両性界面活性剤、ノニオン性界面活性剤などが挙げられるが特に限定されるものではない。   Examples of the surfactant-based agent to be contained in the cooling water system in the subsequent stage include an anionic surfactant, a cationic surfactant, an amphoteric surfactant, and a nonionic surfactant, but are not particularly limited.

アニオン界面活性剤としては、高級脂肪酸塩、オリーブ油硫酸エステル塩、硫酸アルキルナトリウム、アルキルベンゼンスルホン酸ナトリウム、α−オレフィンスルホン酸ナトリウム、N−アシルアミノ酸ナトリウム、N−(2−スルホ)エチル−N−メチルアルカンアミドナトリウム、2−スルホコハク酸ジアルキルアミド、アルキルナフタレンスルホン酸ナトリウム、カルボン酸系ポリマーなどが挙げられる。カルボン酸系ポリマーとしては(メタ)アクリル酸、(メタ)アクリル酸エステル、スチレン、α−オレフィン、(メタ)アクリルアミド、マレイン酸、マレイン酸エステル、イタコン酸などの単重合体または共重合体が挙げられる。   As an anionic surfactant, higher fatty acid salt, olive oil sulfate ester salt, alkyl sodium sulfate, sodium alkylbenzene sulfonate, sodium α-olefin sulfonate, sodium N-acylamino acid, N- (2-sulfo) ethyl-N-methyl Examples include alkaneamide sodium, 2-sulfosuccinic acid dialkylamide, sodium alkylnaphthalenesulfonate, and carboxylic acid polymers. Examples of the carboxylic acid-based polymer include (meth) acrylic acid, (meth) acrylic acid ester, styrene, α-olefin, (meth) acrylamide, maleic acid, maleic acid ester, itaconic acid, and other homopolymers or copolymers. It is done.

カチオン界面活性剤としては、アルキルトリメチルアンモニウムハライド、アルキルピリジニウムスルファート、N−エチルアルカンアミドアンモニウムハライドなどが挙げられる。
非イオン界面活性剤としては、アルキルポリオキシエチレンエーテル、p−アルキルフェニルポリオキシエチレンエーテル、脂肪酸多価アルコールエステル、脂肪酸多価アルコールポリオキシエチレン、脂肪酸ポリオキシエチレンエステル、脂肪酸ショ糖エステル、両性界面活性剤としてはアルキルベタイン、アルキルジエチレントリアミノ酢酸などが挙げられる。
Examples of the cationic surfactant include alkyltrimethylammonium halide, alkylpyridinium sulfate, N-ethylalkanamide ammonium halide and the like.
Nonionic surfactants include alkyl polyoxyethylene ether, p-alkylphenyl polyoxyethylene ether, fatty acid polyhydric alcohol ester, fatty acid polyhydric alcohol polyoxyethylene, fatty acid polyoxyethylene ester, fatty acid sucrose ester, amphoteric interface Examples of the activator include alkylbetaines and alkyldiethylenetriaminoacetic acids.

上記の中でも、カチオン性界面活性剤が好ましく、特に4級アンモニウム塩が好ましい。さらに、4級アンモニウム塩(NRX)として、4個の置換基(R〜R)は直鎖、分枝または環状からなる置換または無置換のアルキル基、アルケニル基またはベンジル基であり、少なくとも1個の置換基(R)の総炭素数が8〜18のアルキル基で、残りの各置換基(R,R,R)の総炭素数が各1〜8のアルキル基である塩化物または臭化物(X=ClまたはBr)であることがさらに好ましい。さらに好ましい4級アンモニウム塩は、Rは総炭素数が12の直鎖の無置換のアルキル基であり、Rは総炭素数が7の環状のベンジル基であり、RおよびRは総炭素数が1のアルキル基である塩化物(X=Cl)である。 Among the above, a cationic surfactant is preferable, and a quaternary ammonium salt is particularly preferable. Further, as the quaternary ammonium salt (NR 1 R 2 R 3 R 4 X), the four substituents (R 1 to R 4 ) are linear, branched or cyclic substituted or unsubstituted alkyl groups, alkenyls Or a benzyl group, wherein at least one substituent (R 1 ) is an alkyl group having a total carbon number of 8 to 18, and the remaining substituents (R 2 , R 3 , R 4 ) have a total carbon number More preferably, it is a chloride or bromide (X = Cl or Br) which is an alkyl group of 1 to 8 each. Further preferred quaternary ammonium salts are those in which R 1 is a linear unsubstituted alkyl group having 12 carbon atoms in total, R 2 is a cyclic benzyl group having 7 carbon atoms in total, and R 3 and R 4 are It is a chloride (X = Cl) which is an alkyl group having a total carbon number of 1.

界面活性剤系薬剤の添加量は、成分濃度として1〜1000mg/L、好ましくは1〜100mg/Lであるのが望ましい。添加量が成分濃度として1mg/L以上において、十分なスライムの剥離効果が得られる。1000mg/L以下において、十分なスライム剥離効果が得られるとともに、発泡性も抑えられ、作業上も問題なく処理することができる。   The addition amount of the surfactant-based agent is 1 to 1000 mg / L, preferably 1 to 100 mg / L as the component concentration. When the addition amount is 1 mg / L or more as the component concentration, a sufficient slime peeling effect can be obtained. At 1000 mg / L or less, a sufficient slime peeling effect can be obtained, foamability can be suppressed, and processing can be performed without any problem.

また、冷却水系内の温度を好ましくは5〜70℃、より好ましくは40〜70℃で処理することで、冷却水系のスライムおよび微生物をより簡単により効率良く剥離および殺菌することができる。5℃未満では薬剤の反応性が低くなり、また、70℃以上では薬剤成分が分解し、スライム剥離効果は低下する傾向があり、好ましくない。   Further, by treating the temperature in the cooling water system preferably at 5 to 70 ° C., more preferably 40 to 70 ° C., the slime and microorganisms in the cooling water system can be peeled and sterilized more easily and efficiently. If the temperature is lower than 5 ° C, the reactivity of the drug is low, and if it is 70 ° C or higher, the drug component is decomposed and the slime peeling effect tends to decrease, which is not preferable.

また、酸またはアルカリ剤を添加し、冷却水系内のpHは特に限定されないが、例えば、後段において界面活性剤系薬剤を添加する際にはそのpHを5〜12、更には7〜10にすることが好ましく、この範囲内において、スライムの剥離効果が向上し、かつ、腐食性を低減しながらスライムの剥離処理および微生物の殺菌処理をすることができる。一般に、pHが5未満では薬剤成分が分解し易く、12以上では薬剤の反応性が低く、スライム剥離効果および微生物殺菌効果が低下する傾向があり、好ましくない。   The pH in the cooling water system is not particularly limited by adding an acid or an alkali agent. For example, when adding a surfactant-based agent in the latter stage, the pH is set to 5 to 12, and further to 7 to 10. In this range, the slime peeling effect is improved, and the slime peeling treatment and the microorganism sterilization treatment can be performed while reducing the corrosiveness. In general, when the pH is less than 5, the drug component is easily decomposed, and when it is 12 or more, the reactivity of the drug is low, and the slime peeling effect and the microbial sterilization effect tend to decrease, which is not preferable.

冷却水系に添加させることのできる酸は、特に限定されるものではなく、無機酸が好ましく、例えば、塩酸、硫酸、硝酸等が挙げられる。その中で、塩酸が好ましい。アルカリ剤は、特に限定されるものではなく、アルカリ金属水酸化物が好ましく、例えば、水酸化ナトリウム、水酸化カリウム等が挙げられる。その中で、より少ない添加量でpH調整可能な水酸化ナトリウムが好ましい。なお、アルカリ剤は、前段の塩素系酸化剤と同時またはその前に添加する。   The acid that can be added to the cooling water system is not particularly limited, and is preferably an inorganic acid, and examples thereof include hydrochloric acid, sulfuric acid, and nitric acid. Of these, hydrochloric acid is preferred. The alkali agent is not particularly limited and is preferably an alkali metal hydroxide, and examples thereof include sodium hydroxide and potassium hydroxide. Among them, sodium hydroxide capable of adjusting the pH with a smaller addition amount is preferable. The alkaline agent is added at the same time as or before the chlorinated oxidant in the previous stage.

上記冷却水系には、他に必要に応じて本発明の効果を有効に発揮させ得る範囲で、ポリマー系分散剤、ヒドラジン、グルタルアルデヒド、過酸化水素、スルファミン酸、炭酸水素ナトリウム、キレート剤等を含有させることができる。   In the cooling water system, a polymer dispersant, hydrazine, glutaraldehyde, hydrogen peroxide, sulfamic acid, sodium hydrogen carbonate, a chelating agent, etc. are added to the extent that the effects of the present invention can be effectively exhibited as necessary. It can be included.

本発明のスライム剥離処理方法について、図を用いて更に具体的に説明する。図1は、本発明のスライム剥離処理方法を実施するための冷却水系の概要図である。
図1において、冷却水系1は、大略でいうと、冷却塔2とその下方の冷却水槽6と冷却水槽6内の冷却水7を冷却塔2に送るための、途中にポンプ9と熱交換器10を備えた冷却水循環配管8とから構成されている。冷却塔2は、通常使用されている形式であって、塔内に充填材層3と上部に設置された送風用のファン4と、充填材層3上に配置された散水管5が設けられている。
The slime peeling treatment method of the present invention will be described more specifically with reference to the drawings. FIG. 1 is a schematic view of a cooling water system for carrying out the slime peeling treatment method of the present invention.
In FIG. 1, a cooling water system 1 generally includes a cooling tower 2, a cooling water tank 6 below the cooling water tank 6, and a pump 9 and a heat exchanger in the middle for sending the cooling water 7 in the cooling water tank 6 to the cooling tower 2. And a cooling water circulation pipe 8 provided with 10. The cooling tower 2 is a type that is usually used, and is provided with a filler layer 3, a blower fan 4 installed on the top, and a water pipe 5 disposed on the filler layer 3 in the tower. ing.

冷却水槽6には、本発明の特徴である処理ユニット11が設置され、その処理ユニット11は、前段の薬剤(塩素系酸化剤)を供給するための薬剤タンク12と注入ポンプ13、後段の薬剤(界面活性剤系薬剤)を供給するための薬剤タンク14と注入ポンプ15、冷却水槽6内の冷却水7の残留ハロゲン濃度を測定するための残留ハロゲン計16から構成されており、残留ハロゲン計16で測定した残留ハロゲン濃度の信号を制御装置17に送り、その信号で注入ポンプ13又は注入ポンプ15を作動させて、前段の薬剤(塩素系酸化剤)又は後段の薬剤(界面活性剤系薬剤)を供給するように制御する。   The cooling water tank 6 is provided with a processing unit 11 which is a feature of the present invention. The processing unit 11 includes a chemical tank 12 and an infusion pump 13 for supplying a pre-stage chemical (chlorine oxidant), and a post-stage chemical. It comprises a chemical tank 14 for supplying (surfactant-based chemical), an injection pump 15, and a residual halogen meter 16 for measuring the residual halogen concentration of the cooling water 7 in the cooling water tank 6. The residual halogen concentration signal measured in 16 is sent to the control device 17, and the infusion pump 13 or the infusion pump 15 is operated by the signal, and the upstream chemical (chlorine oxidant) or the downstream chemical (surfactant chemical). ) To supply.

以下に、本発明の実施例を示すが、本発明はこれらの実施例に限定されるものではない。   Examples of the present invention are shown below, but the present invention is not limited to these examples.

<実施例1、比較例1〜8及び参考例1>
容量1Lのガラスビーカーに水道水を1000ml入れ、下水由来の混合生汚泥を3ml、表1に示す組成の栄養源を1ml入れ、400rpmで攪拌した。このビーカーにSUS製の0.37×20メッシュの金網担体を浸漬させ、室温で1週間混合培養した。培養中は、栄養源を1ml/日添加した。スライムが付着した金網担体を洗浄・殺菌試験用の試験片とした。
<Example 1, Comparative Examples 1-8 and Reference Example 1>
1000 ml of tap water was placed in a glass beaker having a capacity of 1 L, 3 ml of mixed raw sludge derived from sewage, and 1 ml of a nutrient source having the composition shown in Table 1 were stirred at 400 rpm. A SUS 0.37 × 20 mesh wire mesh carrier was immersed in this beaker and mixed and cultured at room temperature for 1 week. During the cultivation, 1 ml / day of a nutrient source was added. The wire mesh carrier to which the slime adhered was used as a test piece for cleaning and sterilization tests.

Figure 2012056874
Figure 2012056874

次に、容量1Lのガラスビーカーに試水を1000ml入れ、試験片を浸漬させ、600rpmで攪拌した。試水は、無処理の冷却水でレジオネラ属菌が検出されたものを用いた。その後、表2に記載のとおりの処理薬剤を表2に記載のとおりの所定量及び処理時間で添加し、添加直後から3時間後までの試験片のスライムの剥離状態を目視観察し、また、試験後のビーカー内の水質項目として濁度および一般細菌数を測定し、スライム剥離効果および微生物殺菌効果の評価を行った。   Next, 1000 ml of test water was put into a 1 L glass beaker, the test piece was immersed, and stirred at 600 rpm. The sample water used was untreated cooling water in which Legionella was detected. Thereafter, treatment chemicals as shown in Table 2 were added in a predetermined amount and treatment time as shown in Table 2, and the slime peeling state of the test piece from immediately after the addition until 3 hours was visually observed, Turbidity and the number of general bacteria were measured as water quality items in the beaker after the test, and the slime peeling effect and the microbial bactericidal effect were evaluated.

スライム剥離の評価は、試験後に試験片に残存したスライムと金網担体の面積の割合を目視にて観察し、評価した。スライムの剥離状態が90〜100%で◎、70〜90%で○、50〜70%で△〜○、30〜50%で△、0〜30%で×とし、濁度が高いほど剥離効果が高いと評価した。微生物殺菌効果の評価方法は、一般細菌数が低いほど殺菌効果が高いと評価した。
また濁度は、積分球式濁度計(SEP-PT-706D、三菱化学社製)にて測定し、微生物菌数は、一般生菌用シート培地(サニ太くん(チッソ社の登録商標)、チッソ社製)を用いて、35℃、48時間培養し、コロニー数をカウントすることで測定した。
The evaluation of slime peeling was performed by visually observing the area ratio between the slime remaining on the test piece after the test and the wire mesh carrier. The slime peeling state is 90 to 100%, 70, 70 to 90% ○, 50 to 70% Δ to ○, 30 to 50% Δ, 0 to 30% ×, and the higher the turbidity, the more the peeling effect Was rated high. The evaluation method of the microbial bactericidal effect evaluated that the bactericidal effect was so high that the number of general bacteria was low.
Turbidity was measured with an integrating sphere turbidimeter (SEP-PT-706D, manufactured by Mitsubishi Chemical Corporation), and the number of microbial bacteria was measured using a sheet medium for general living bacteria (Sani-kun (registered trademark of Chisso Corporation)). , Manufactured by Chisso Corp.) and cultured at 35 ° C. for 48 hours and counted by counting the number of colonies.

以上のスライム剥離・殺菌試験結果を表2に示す。なお、塩素系酸化剤の薬剤添加率は有効塩素濃度として、その他の処理薬剤の薬剤添加率は成分濃度として示す。
表2に本発明の方法で行ったスライム剥離・殺菌試験の結果(実施例1)および従来公知のスライム剥離剤または殺菌剤によるスライム剥離・殺菌試験の結果(比較例1〜8)を示す。ブランクとして薬剤処理しない時の試験結果は比較例8に示す。
The results of the above slime peeling / sterilization test are shown in Table 2. In addition, the chemical | medical agent addition rate of a chlorine-type oxidizing agent is shown as effective chlorine concentration, and the chemical | medical agent addition rate of another process chemical | medical agent is shown as a component concentration.
Table 2 shows the results (Example 1) of the slime peeling / sterilization test performed by the method of the present invention and the results (Comparative Examples 1-8) of the slime peeling / sterilization test using a conventionally known slime remover or fungicide. The test result when no chemical treatment is performed as a blank is shown in Comparative Example 8.

Figure 2012056874
Figure 2012056874

次亜塩素酸ナトリウム単独、4級アンモニウム塩単独、ヒドラジン単独、グルタルアルデヒド単独および過酸化水素単独で処理した場合(比較例1〜5)、スライム剥離効果および殺菌効果は低かった。例えば、次亜塩素酸ナトリウム単独処理(比較例1)では、スライム剥離効果が低下し、4級アンモニウム塩単独処理(比較例2)では、スライム剥離効果が極端に低下し、殺菌効果も低かった。本発明方法による前段処理として次亜塩素酸ナトリウムを50mg/L添加し、0.5時間後に後段処理として4級アンモニウム塩を50mg/L添加し、3時間攪拌することで(実施例1)、良好なスライム剥離効果が得られ、一般細菌数は1×10CFU/ml以下であり、良好な殺菌効果も得られた。 When treated with sodium hypochlorite alone, quaternary ammonium salt alone, hydrazine alone, glutaraldehyde alone and hydrogen peroxide alone (Comparative Examples 1 to 5), the slime peeling effect and bactericidal effect were low. For example, in the sodium hypochlorite single treatment (Comparative Example 1), the slime peeling effect was lowered, and in the quaternary ammonium salt single treatment (Comparative Example 2), the slime peeling effect was extremely lowered and the bactericidal effect was also low. . By adding 50 mg / L of sodium hypochlorite as a pretreatment according to the method of the present invention, and adding 50 mg / L of quaternary ammonium salt as a posttreatment after 0.5 hours, and stirring for 3 hours (Example 1), A good slime peeling effect was obtained, the number of general bacteria was 1 × 10 2 CFU / ml or less, and a good bactericidal effect was also obtained.

更に、本発明の方法で処理することでレジオネラ属菌数は10CFU/ml以下となり、レジオネラ属菌に対する良好な殺菌効果が得られた。4級アンモニウム塩単独(比較例2)、ヒドラジン単独(比較例3)及び過酸化水素単独処理(比較例5)では、レジオネラ属菌数はそれぞれ8×10CFU/ml、7×10CFU/ml及び1×10CFU/mlであり、レジオネラ属菌に対する殺菌効果は低かった。 Furthermore, the Legionella genus count became 10 CFU / ml or less by processing by the method of this invention, and the favorable bactericidal effect with respect to Legionella genus bacteria was acquired. In the case of quaternary ammonium salt alone (Comparative Example 2), hydrazine alone (Comparative Example 3) and hydrogen peroxide alone (Comparative Example 5), the number of Legionella bacteria is 8 × 10 2 CFU / ml and 7 × 10 2 CFU, respectively. / Ml and 1 × 10 3 CFU / ml, and the bactericidal effect against Legionella was low.

一方、次亜塩素酸ナトリウムと4級アンモニウム塩を同時に添加した場合(比較例6)、実施例1と比べて、スライム剥離効果および殺菌効果はいずれも低かった。また、添加順を逆にした場合、すなわち、前段処理として4級アンモニウム塩を50mg/L添加し、0.5h後に後段処理として次亜塩素酸ナトリウムを50mg/L添加し、3h攪拌処理した場合(比較例7)、実施例1と比べて、殺菌効果は同程度であったが、十分なスライム剥離効果が得られていない。   On the other hand, when sodium hypochlorite and a quaternary ammonium salt were added simultaneously (Comparative Example 6), both the slime peeling effect and the bactericidal effect were low as compared with Example 1. When the order of addition is reversed, that is, when 50 mg / L of a quaternary ammonium salt is added as a pre-treatment, and 50 mg / L of sodium hypochlorite is added as a post-treatment after 0.5 h, and stirred for 3 h. (Comparative Example 7) Compared with Example 1, the bactericidal effect was comparable, but a sufficient slime peeling effect was not obtained.

また、軟鋼の腐食速度を、下記の方法により測定して、金属腐食性を評価したところ、次亜塩素酸ナトリウムを単独で用いた場合(比較例1)以外はすべて500mdd未満であり、金属腐食性に問題がなかった。
〔金属腐食性の測定方法〕
軟鋼のテストピースを浸漬させ、試験後にテストピースを取り出し、表面の汚れや腐食生成物を除去した後の重量を測定し、浸漬前後の重量差より腐食速度(mdd)を算出した(mddとは、1日当たりの表面積1dmの腐食量(mg)を言う)。
Moreover, when the corrosion rate of mild steel was measured by the following method to evaluate the metal corrosivity, it was less than 500 mdd except when sodium hypochlorite was used alone (Comparative Example 1). There was no problem with sex.
[Measuring method for metal corrosion]
A test piece of mild steel was immersed, the test piece was taken out after the test, the weight after removing dirt and corrosion products on the surface was measured, and the corrosion rate (mdd) was calculated from the weight difference before and after the immersion (mdd) Corrosion amount (mg) of 1 dm 2 surface area per day).

<実施例2及び3>
実施例1において、前段処理剤である次亜塩素酸ナトリウムと後段処理剤である4級アンモニウム塩のそれぞれの添加量を表3に記載のとおりに種々変更した以外は実施例1と同様にして、スライム剥離効果及び殺菌効果を評価した。その結果を表3に示す。なお、表3において、金属腐食性は、上記軟鋼の腐食速度が、10mdd以下の場合を○、10〜100mddの場合を△〜○、100〜500mddの場合を△、500mdd以上の場合を×とした。
<Examples 2 and 3>
In Example 1, the same procedure as in Example 1 was conducted, except that the addition amounts of sodium hypochlorite as the pretreatment agent and quaternary ammonium salt as the posttreatment agent were variously changed as shown in Table 3. The slime peeling effect and the bactericidal effect were evaluated. The results are shown in Table 3. In Table 3, the metal corrosivity indicates that the corrosion rate of the mild steel is ◯ when the corrosion rate is 10 mdd or less, Δ is ◯ when the corrosion rate is 10 to 100 mdd, Δ is when the corrosion rate is 100 to 500 mdd, and × when the corrosion rate is 500 mdd or more. did.

Figure 2012056874
Figure 2012056874

前段の次亜塩素酸ナトリウムの添加率を200mg/L添加することで、実施例1と比べて、より良好なスライム剥離効果が得られた。また、10mg/Lと減らして処理した場合でも、スライムの剥離効果および殺菌効果は若干低下するが、スライムは7割程剥離されており、一般細菌数も1×10CFU/mlと十分なスライム剥離効果および殺菌効果が得られた。また、後段の4級アンモニウム塩の添加率を1mg/Lと減らして処理した場合、実施例1と比べて、スライムの剥離効果は若干低下するが、殺菌効果は同等であった。 Compared with Example 1, a better slime peeling effect was obtained by adding 200 mg / L of the sodium hypochlorite addition rate in the previous stage. Even when the treatment is reduced to 10 mg / L, the exfoliation effect and the bactericidal effect of the slime are slightly reduced, but the slime is exfoliated by about 70%, and the number of general bacteria is sufficiently 1 × 10 2 CFU / ml. Slime peeling effect and bactericidal effect were obtained. Further, when the treatment was performed with the addition rate of the quaternary ammonium salt in the subsequent stage reduced to 1 mg / L, the slime peeling effect was slightly reduced as compared with Example 1, but the bactericidal effect was equivalent.

<実施例4>
実施例1において、前段処理剤を添加してから後段処理剤を添加するまでの時間を、表4に示すとおりに変更した以外は実施例1と同様にして、スライム剥離効果及び殺菌効果を評価した。その結果を表4に示す。
<Example 4>
In Example 1, the slime peeling effect and bactericidal effect were evaluated in the same manner as in Example 1 except that the time from the addition of the pre-treatment agent to the addition of the post-treatment agent was changed as shown in Table 4. did. The results are shown in Table 4.

Figure 2012056874
Figure 2012056874

前段処理剤を添加してから後段処理剤を添加するまでの時間を0.1時間と短くして処理した場合(実施例4−1)および1時間(実施例4−2)と長くして処理した場合、スライム剥離効果および殺菌効果は、実施例1(0.5時間)の場合と比べて同等であった。また、前段への次亜塩素酸ナトリウム添加後3時間以上経過した後に後段処理として4級アンモニウム塩を添加した場合(実施例4−3、実施例4−4)でも十分なスライム剥離効果及び殺菌効果が得られるが、0.5時間後に添加した場合(実施例1)に比してスライム剥離効果が低下しており、一定時間内に後段処理をした方が好ましいことが分かる。   When the treatment from the addition of the pre-treatment agent to the addition of the post-treatment agent was shortened to 0.1 hour (Example 4-1) and 1 hour (Example 4-2), the time was increased. When treated, the slime peeling effect and the bactericidal effect were equivalent to those of Example 1 (0.5 hours). Moreover, even when 3 hours or more have elapsed after the addition of sodium hypochlorite to the former stage, when a quaternary ammonium salt is added as a later stage treatment (Example 4-3, Example 4-4), sufficient slime peeling effect and sterilization Although an effect is acquired, it turns out that the slime peeling effect has fallen compared with the case where it adds 0.5 hours later (Example 1), and it is more preferable to carry out a post-process within a fixed time.

<実施例5>
実施例1において、前段及び後段の処理温度を表5に示すとおりに変更した以外は実施例1と同様にして、スライム剥離効果及び殺菌効果を評価した。その結果を表5に示す。
<Example 5>
In Example 1, the slime peeling effect and the bactericidal effect were evaluated in the same manner as in Example 1 except that the treatment temperatures of the former stage and the latter stage were changed as shown in Table 5. The results are shown in Table 5.

Figure 2012056874
Figure 2012056874

表5の結果から、前段および後段の処理温度を40〜70℃で処理することで(実施例5−2、5−3)、20℃で処理している実施例1と比べて、より良好なスライム剥離効果が得られた。また、表5の結果から、処理温度が2℃又は80℃の場合は、スライム剥離状態があまり良好ではなく(参考例5−1、5−2)、本発明の処理には、好適な温度領域があることが分かる。   From the result of Table 5, it is better compared with Example 1 currently processed at 20 degreeC by processing the process temperature of a front | former stage and a back | latter stage at 40-70 degreeC (Example 5-2, 5-3). A slime peeling effect was obtained. Moreover, from the results of Table 5, when the treatment temperature is 2 ° C. or 80 ° C., the slime peeled state is not so good (Reference Examples 5-1 and 5-2), and a suitable temperature for the treatment of the present invention. You can see that there is a region.

<実施例6>
実施例1において、前段及び後段の処理pHを表6に示すとおりに変更した以外は実施例1と同様にして、スライム剥離効果及び殺菌効果を評価した。その結果を表6に示す。
前段処理において、水酸化ナトリウムを添加し、処理pHを9.6で処理することで、pH8.2で処理している実施例1と比べて、より良好なスライム剥離効果が得られた。
<Example 6>
In Example 1, the slime peeling effect and the bactericidal effect were evaluated in the same manner as in Example 1 except that the treatment pH of the former stage and the latter stage was changed as shown in Table 6. The results are shown in Table 6.
In the former treatment, sodium hydroxide was added and the treatment pH was treated at 9.6, so that a better slime peeling effect was obtained as compared with Example 1 where treatment was carried out at pH 8.2.

Figure 2012056874
Figure 2012056874

<実施例7>
実施例1において、後段処理後の循環時間を表7に示すとおりに変更した以外は実施例1と同様にして、スライム剥離効果及び殺菌効果を評価した。その結果を表7に示す。
後段処理後の攪拌時間が0.1時間以上であれば(実施例7−1)、一定のスライム剥離効果及び殺菌効果を得ることができる。また後段処理後の攪拌時間を6時間とすることで(実施例7−3)、より良好なスライム剥離効果が得られた。
<Example 7>
In Example 1, the slime peeling effect and the bactericidal effect were evaluated in the same manner as in Example 1 except that the circulation time after the post-treatment was changed as shown in Table 7. The results are shown in Table 7.
If the stirring time after the post-treatment is 0.1 hour or more (Example 7-1), a certain slime peeling effect and bactericidal effect can be obtained. Moreover, the more favorable slime peeling effect was acquired by making the stirring time after a back | latter stage process into 6 hours (Example 7-3).

Figure 2012056874
Figure 2012056874

<実施例8>
実施例1において、後段処理で使用する界面活性剤系薬剤を表8に示すとおりに変更した以外は実施例1と同様にして、スライム剥離効果及び殺菌効果を評価した。その結果を表8に示す。
<Example 8>
In Example 1, the slime peeling effect and the bactericidal effect were evaluated in the same manner as in Example 1 except that the surfactant-based chemical used in the subsequent treatment was changed as shown in Table 8. The results are shown in Table 8.

Figure 2012056874
Figure 2012056874

後段処理で使用する界面活性剤系薬剤をカチオン性界面活性剤、アニオン性界面活性剤、両性界面活性剤およびノニオン界面活性剤を用いて実施例1と同じ条件で処理しても、スライム剥離効果および殺菌効果は良好であった。その中で、カチオン性界面活性剤である4級アンモニウム塩を用いた場合、スライム剥離効果および殺菌効果は最も良好であった。   Even if the surfactant-based agent used in the post-treatment is treated with a cationic surfactant, an anionic surfactant, an amphoteric surfactant and a nonionic surfactant under the same conditions as in Example 1, slime release effect And the bactericidal effect was good. Among them, when a quaternary ammonium salt which is a cationic surfactant was used, the slime peeling effect and the bactericidal effect were the best.

1 冷却水系
2 冷却塔
3 充填材層
4 送風ファン
5 散水管
6 冷却水槽
7 冷却水
8 冷却水循環配管
9 ポンプ
10 熱交換器
11 処理ユニット
12 薬剤タンク(塩素系酸化剤用)
13 注入ポンプ
14 薬剤タンク(界面活性剤系薬剤用)
15 注入ポンプ
16 残留ハロゲン計
17 制御装置
DESCRIPTION OF SYMBOLS 1 Cooling water system 2 Cooling tower 3 Filling material layer 4 Blower fan 5 Sprinkling pipe 6 Cooling water tank 7 Cooling water 8 Cooling water circulation piping 9 Pump 10 Heat exchanger 11 Processing unit 12 Chemical tank (for chlorine-based oxidizing agent)
13 Infusion pump 14 Drug tank (for surfactant-based drugs)
15 Infusion pump 16 Residual halogen meter 17 Controller

Claims (6)

冷却水系のスライム剥離および微生物殺菌において、前段で塩素系酸化剤を冷却水系に含有させ、後段で界面活性剤系薬剤を冷却水系に含有させることを特徴とする処理方法。   A cooling water-based slime stripping and microbial sterilization, wherein a chlorine-based oxidizing agent is contained in the cooling water system in the former stage and a surfactant-based agent is contained in the cooling water system in the latter stage. 前段の塩素系酸化剤の添加量が、有効塩素として0.1〜1000mg/L、後段の界面活性剤系薬剤の添加量が、成分濃度として1〜1000mg/Lであることを特徴とする請求項1記載の処理方法。   The amount of addition of the chlorinated oxidizer in the former stage is 0.1 to 1000 mg / L as effective chlorine, and the amount of addition of the surfactant-type chemical in the latter stage is 1-1000 mg / L as the component concentration. Item 2. A processing method according to Item 1. 前段の塩素系酸化剤を添加してから0.1〜3時間後に後段の界面活性剤系薬剤を添加することを特徴とする請求項1又は2記載の処理方法。   The treatment method according to claim 1 or 2, wherein the surfactant in the subsequent stage is added 0.1 to 3 hours after the addition of the chlorinated oxidant in the preceding stage. 冷却水系内の温度を5〜70℃で処理することを特徴とする請求項1〜3のいずれか1項に記載の処理方法。   The processing method according to any one of claims 1 to 3, wherein the temperature in the cooling water system is processed at 5 to 70 ° C. 酸またはアルカリ剤を添加し、冷却水系内のpHを5〜12で処理することを特徴とする請求項1〜4のいずれか1項に記載の処理方法。   The treatment method according to any one of claims 1 to 4, wherein an acid or an alkali agent is added, and the pH in the cooling water system is treated at 5 to 12. 塩素系酸化剤含有薬剤及び界面活性剤系薬剤含有薬剤を組み合わせてなる、請求項1〜5のいずれか1項に記載の処理方法に用いるための冷却水系処理剤セット。   The cooling water type processing agent set for using for the processing method of any one of Claims 1-5 which combines a chlorine-type oxidizing agent containing chemical | medical agent and surfactant type chemical | medical agent containing chemical | medical agent.
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP7340205B2 (en) 2018-07-23 2023-09-07 株式会社片山化学工業研究所 Method for preventing adhesion of marine organisms and slime, anti-adhesion agent, and anti-adhesion kit

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08260392A (en) * 1993-03-30 1996-10-08 Daiwa Kagaku Kogyo Kk Suppression of microorganism in paper sheet-forming process and treating agent for deposit formed of slime and pitch
JP2001300546A (en) * 2000-04-28 2001-10-30 Kao Corp Production method of sterilized water
JP2003164882A (en) * 2001-11-29 2003-06-10 Kurita Water Ind Ltd Antibacterial method for industrial water system containing reducing substance
JP2003267811A (en) * 2002-03-14 2003-09-25 Kurita Water Ind Ltd Slime peeling agent, slime peeling agent composition and slime peeling method
JP2004267896A (en) * 2003-03-07 2004-09-30 Katayama Chem Works Co Ltd Contamination preventing method for industrial/waste water system
JP2009154113A (en) * 2007-12-27 2009-07-16 Aquas Corp Sterilization treatment method for water system water
WO2009104707A1 (en) * 2008-02-21 2009-08-27 栗田工業株式会社 Method for disinfection of aqueous systems
JP2010065017A (en) * 2008-09-10 2010-03-25 Moltec Co Ltd Pipe cleansing germicidal composition
JP2010513275A (en) * 2006-12-13 2010-04-30 アーチ ケミカルズ,インコーポレイテッド Biocidal composition and method for treating water recycling system

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08260392A (en) * 1993-03-30 1996-10-08 Daiwa Kagaku Kogyo Kk Suppression of microorganism in paper sheet-forming process and treating agent for deposit formed of slime and pitch
JP2001300546A (en) * 2000-04-28 2001-10-30 Kao Corp Production method of sterilized water
JP2003164882A (en) * 2001-11-29 2003-06-10 Kurita Water Ind Ltd Antibacterial method for industrial water system containing reducing substance
JP2003267811A (en) * 2002-03-14 2003-09-25 Kurita Water Ind Ltd Slime peeling agent, slime peeling agent composition and slime peeling method
JP2004267896A (en) * 2003-03-07 2004-09-30 Katayama Chem Works Co Ltd Contamination preventing method for industrial/waste water system
JP2010513275A (en) * 2006-12-13 2010-04-30 アーチ ケミカルズ,インコーポレイテッド Biocidal composition and method for treating water recycling system
JP2009154113A (en) * 2007-12-27 2009-07-16 Aquas Corp Sterilization treatment method for water system water
WO2009104707A1 (en) * 2008-02-21 2009-08-27 栗田工業株式会社 Method for disinfection of aqueous systems
JP2010065017A (en) * 2008-09-10 2010-03-25 Moltec Co Ltd Pipe cleansing germicidal composition

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP7340205B2 (en) 2018-07-23 2023-09-07 株式会社片山化学工業研究所 Method for preventing adhesion of marine organisms and slime, anti-adhesion agent, and anti-adhesion kit

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