JP6843329B2 - How to prevent adhesion damage of marine organisms in seawater cooling water system - Google Patents

How to prevent adhesion damage of marine organisms in seawater cooling water system Download PDF

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JP6843329B2
JP6843329B2 JP2020018045A JP2020018045A JP6843329B2 JP 6843329 B2 JP6843329 B2 JP 6843329B2 JP 2020018045 A JP2020018045 A JP 2020018045A JP 2020018045 A JP2020018045 A JP 2020018045A JP 6843329 B2 JP6843329 B2 JP 6843329B2
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村上 誠
誠 村上
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Katayama Chemical Works Co Ltd
Nalco Japan GK
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本発明は、海水冷却水系の海生生物の付着障害防止方法に関する。さらに詳しくは、本発明は、低濃度の薬剤添加でその効果を長期間持続し、しかも広範な海生生物種やスライムの付着障害を防止し得る海水冷却水系の海生生物の付着障害防止方法に関する。 The present invention relates to a method for preventing attachment disorders of marine organisms in a seawater cooling water system. More specifically, the present invention is a method for preventing adhesion disorders of marine organisms in a seawater cooling water system, which can maintain its effect for a long period of time by adding a low concentration of chemicals and can prevent attachment disorders of a wide range of marine organisms and slime. Regarding.

海水は、工業用の冷却水として、特に火力発電所や原子力発電所の復水器の冷却水として多量に使用されている。そのため、海水取水路壁や配管内および熱交換器内には、ムラサキイガイなどのイガイ類やフジツボ類、コケムシ類、ヒドロ虫類などの海生生物種が多量に付着して、様々な障害を惹き起こす。これらの中でも足糸で着生するムラサキイガイなどの二枚貝類は、成長が速く、成貝になると熱交換器チューブの一部を閉塞させて海水の通水を阻害し、また乱流を生じさせ、エロージョン腐食などの障害を惹き起こす。 Seawater is used in large quantities as industrial cooling water, especially as cooling water for condensers of thermal power plants and nuclear power plants. Therefore, a large amount of mussels such as mussels and marine species such as barnacles, mussels, and hydroins adhere to the walls of seawater intake channels, pipes, and heat exchangers, causing various obstacles. Wake up. Among these, bivalves such as mussels that grow on byssus grow fast, and when they become adults, they block part of the heat exchanger tube, obstructing the passage of seawater and causing turbulence. Causes obstacles such as erosion corrosion.

これら海生生物種の密集着生(付着)を防止するために、従来から次亜塩素酸ナトリウム、電解塩素もしくは塩素ガスなどの塩素発生剤(「塩素剤」ともいう)、過酸化水素もしくは過酸化水素発生剤(「過酸化水素剤」ともいう)の添加が行われている。
一方、二酸化塩素は、殺菌力が強く、トリハロメタンのような有害な有機塩素化合物を形成しないため、環境への影響が小さいという利点がある。
例えば、特開平1−275504号公報(特許文献1)には、二酸化塩素として少なくとも0.015ppm以上、好ましくは1ppm以上の、二酸化塩素または二酸化塩素発生剤を有効成分とする水中付着生物防除剤に関する技術が、特開平6−153759号公報(特許文献2)には、淡水または海水を使用する施設に設置された淡水または海水を通す水路に、0.1〜2.0ppmの比較的低濃度の二酸化塩素水溶液を連続的もしくは10.0〜30.0ppmの比較的高濃度の二酸化塩素水溶液を間欠的に注入することからなる、水路に付着する生物の付着防止または防除方法に関する技術が開示されている。
また、この出願の出願人は、二酸化塩素と過酸化水素とを併用する海生生物の付着防止方法およびそれに用いる付着防止剤を提案している(特許第5879596公報:特許文献3参照)。
In order to prevent the dense formation (adhesion) of these marine species, conventional chlorine generators such as sodium hypochlorite, electrolytic chlorine or chlorine gas (also called "chlorine agents"), hydrogen peroxide or excess A hydrogen peroxide generator (also referred to as a "hydrogen peroxide agent") has been added.
On the other hand, chlorine dioxide has a strong bactericidal activity and does not form harmful organic chlorine compounds such as trihalomethane, so that it has an advantage of having a small impact on the environment.
For example, Japanese Patent Application Laid-Open No. 1-275504 (Patent Document 1) relates to an aqueous solution-adhering biological control agent containing chlorine dioxide or a chlorine dioxide generator as an active ingredient, which contains at least 0.015 ppm or more, preferably 1 ppm or more of chlorine dioxide. According to Japanese Patent Application Laid-Open No. 6-153759 (Patent Document 2), a relatively low concentration of 0.1 to 2.0 ppm is found in a channel for passing fresh water or seawater installed in a facility using fresh water or seawater. A technique relating to a method for preventing or controlling the adhesion of organisms adhering to a water channel, which comprises continuously or intermittently injecting a relatively high concentration chlorine dioxide aqueous solution of 10.0 to 30.0 ppm, is disclosed. There is.
In addition, the applicant of this application has proposed a method for preventing the adhesion of marine organisms in which chlorine dioxide and hydrogen peroxide are used in combination and an anti-adhesion agent used therein (see Patent No. 5879596: Patent Document 3).

特開平1−275504号公報Japanese Unexamined Patent Publication No. 1-2755004 特開平6−153759号公報Japanese Unexamined Patent Publication No. 6-153759 特許第5879596号公報Japanese Patent No. 5879596

しかしながら、二酸化塩素は化学物質として極めて不安定であり、これを対象系に用いても海生生物の付着障害防止効果の持続性に問題があり、その貯蔵や輸送は非常に困難である。例えば、特許文献2に記載のように、二酸化塩素製造装置を用いて現場で二酸化塩素を製造することもできるが、薬剤の単価が高価になるという新たな課題が生じる。
そこで、二酸化塩素を用いて広範な海生付着生物の付着障害を有効に防止すると共に、そのランニングコストのさらなる削減が求められている。
However, chlorine dioxide is extremely unstable as a chemical substance, and even if it is used in a target system, there is a problem in sustainability of the effect of preventing adhesion disorders of marine organisms, and its storage and transportation are extremely difficult. For example, as described in Patent Document 2, chlorine dioxide can be produced on-site using a chlorine dioxide producing apparatus, but there is a new problem that the unit price of the drug becomes expensive.
Therefore, it is required to effectively prevent adhesion disorders of a wide range of marine sessile organisms by using chlorine dioxide and further reduce the running cost thereof.

本発明は、低濃度の薬剤添加でその効果を長期間持続し、しかも広範な海生生物種やスライムの付着障害を防止し得る海水冷却水系の海生生物の付着障害防止方法を提供することを課題とする。 The present invention provides a method for preventing adhesion disorders of marine organisms in a seawater cooling water system, which can maintain the effect for a long period of time by adding a low concentration of a drug and can prevent attachment disorders of a wide range of marine organisms and slimes. Is the subject.

そこで、本発明の発明者は、二酸化塩素の海水中の濃度と海生生物との接触時間などの条件を特定の範囲に設定することにより、具体的には、所望の海生生物の付着障害防止効果が得られる海水中の二酸化塩素の最小濃度を基準濃度としたときに、この基準濃度未満になるように二酸化塩素をほぼ連続的に添加しつつ、基準濃度以上になるように二酸化塩素を短時間で間欠的に添加することにより、ムラサキイガイなどのイガイ類やフジツボ類、コケムシ類、ヒドロ虫類およびスライムなどを含む広範な海生生物種の付着障害を長期間持続して有効に防止し得ること、さらには従来技術と比較して、薬剤添加量を低減させても海生生物やスライムなどの有効な付着障害防止効果が得られることを意外にも見出し、本発明を完成するに到った。
すなわち、本発明の発明者は、本発明の構成を採用することにより、薬剤の総使用量が削減されるにもかかわらず、広範な海生生物種およびスライムの付着障害を有効に防止できるという意外な効果を見出した。
Therefore, the inventor of the present invention sets conditions such as the concentration of chlorine dioxide in seawater and the contact time with marine organisms within a specific range to specifically impair the attachment of desired marine organisms. When the minimum concentration of chlorine dioxide in seawater where the preventive effect can be obtained is set as the standard concentration, chlorine dioxide is added almost continuously so as to be less than this standard concentration, and chlorine dioxide is added so as to be above the standard concentration. By adding it intermittently in a short period of time, it effectively prevents attachment disorders of a wide range of marine organisms including mussels such as purple mussels, fujitsubos, pectinatella magnifica, hydroins and slimes for a long period of time. Surprisingly, we found that even if the amount of chemicals added was reduced, an effective effect of preventing adhesion disorders such as marine organisms and slime could be obtained, and the present invention was completed. It was.
That is, the inventor of the present invention can effectively prevent a wide range of marine species and slime adhesion disorders by adopting the configuration of the present invention, even though the total amount of the drug used is reduced. I found an unexpected effect.

かくして、本発明によれば、二酸化塩素を一定濃度で連続的に添加したときに所望の海生生物の付着障害防止効果が得られる一過式海水冷却水系の海水中の二酸化塩素の最小濃度を基準濃度とし、
記海水中の二酸化塩素濃度が、前記基準濃度未満の低濃度の期間と前記基準濃度以上の高濃度の期間とが交互になるように、二酸化塩素または該海水中で二酸化塩素を発生し得る化合物を低濃度および高濃度で交互に添加することからなり、
前記基準濃度未満の低濃度が、前記基準濃度の1/4〜9/10の濃度であり、前記基準濃度以上の高濃度が、0.02〜0.5mg/Lであることを特徴とする一過式海水冷却水系の海生生物の付着障害防止方法が提供される。
Thus, according to the present invention, the minimum concentration of chlorine dioxide in seawater of a transient seawater cooling water system, which can obtain a desired effect of preventing adhesion disorders of marine organisms when chlorine dioxide is continuously added at a constant concentration, is determined. Use as the reference concentration
Before the chlorine dioxide concentration of Kiumi underwater, so that the periods of high concentration of more than the reference concentration and low concentration period of less than the reference concentration is alternately may generate chlorine dioxide in the chlorine dioxide or該海water It consists of alternating low and high concentrations of the compound.
Low concentrations of less than the reference concentration, Ri concentration der of 1 / 4-9 / 10 of the reference concentration, the reference concentration or a high concentration, wherein 0.02 to 0.5 / L der Rukoto A method for preventing adhesion disorders of marine organisms in a transient seawater cooling water system is provided.

本発明によれば、低濃度の薬剤添加で、薬剤の総使用量が削減されるにもかかわらず、その効果を長期間持続し、しかも広範な海生生物種やスライムの付着障害を防止し得る海水冷却水系の海生生物の付着障害防止方法を提供することができる。
すなわち、従来技術の二酸化塩素の単独添加と比較して少量添加であっても、優れた海生生物の付着障害防止効果を得ることができる。また、この薬剤添加量の削減は、薬剤使用量を含めてランニングコストのさらなる削減効果をもたらす。
また、本発明の海生生物の付着障害防止方法は、排水中の残留塩素濃度が規制対象となる塩素剤や臭素剤を用いず、殺菌力が強く、有害な有機塩素化合物を形成しない二酸化塩素を用いるため、環境への影響が小さいという利点がある。
本発明の海生生物の付着障害防止方法は、広範な海生生物種、例えば、ムラサキイガイなどのイガイ類やフジツボ類、コケムシ類、ヒドロ虫類などの海生生物やスライムの付着障害防止に有効である。
本発明のメカニズムは、次のように考えられる。
付着生物は、まず基質表面にバクテリア等が付着してスライムが形成され、次いで珪藻類(植物プランクトン)が付着してバクテリアフィルムが形成され、これらのバクテリアフィルムが酸性多糖体を生産し、大型付着生物幼生が誘引されることにより遷移するものと考えられている。
本発明の海生生物の付着障害防止方法では、高濃度の二酸化塩素が、付着生物の遷移の過程を効率的に阻害し、基準濃度よりも低濃度の期間を設けても十分な付着障害防止が得られるものと考えられる。
According to the present invention, the addition of a low concentration of a drug reduces the total amount of the drug used, but the effect is maintained for a long period of time, and the adhesion disorder of a wide range of marine organisms and slime is prevented. It is possible to provide a method for preventing adhesion disorders of marine organisms in the obtained seawater cooling water system.
That is, an excellent effect of preventing adhesion disorders of marine organisms can be obtained even if a small amount of chlorine dioxide is added as compared with the conventional method of adding chlorine dioxide alone. In addition, this reduction in the amount of the drug added brings about a further reduction effect of the running cost including the amount of the drug used.
In addition, the method for preventing adhesion disorders of marine organisms of the present invention does not use chlorine agents or bromine agents whose residual chlorine concentration in wastewater is subject to regulation, has strong bactericidal activity, and does not form harmful organic chlorine compounds. Has the advantage of having a small impact on the environment.
The method for preventing attachment disorders of marine organisms of the present invention is effective in preventing attachment disorders of a wide range of marine organism species, for example, mussels such as mussels, barnacles, mussels, hydroins and other marine organisms and slimes. Is.
The mechanism of the present invention is considered as follows.
In sessile organisms, bacteria and the like first adhere to the surface of the substrate to form slime, then diatoms (phytoplankton) adhere to form a bacterial film, and these bacterial films produce acidic polysaccharides, resulting in large attachment. It is thought that the transition is caused by the attraction of biological larvae.
In the method for preventing attachment disorders of marine organisms of the present invention, a high concentration of chlorine dioxide efficiently inhibits the succession process of attached organisms, and even if a period of concentration lower than the reference concentration is provided, sufficient prevention of adhesion disorders is provided. Is considered to be obtained.

また、本発明の海生生物の付着障害防止方法は、次の条件のいずれか1つを満たす場合に、上記の効果をより発揮する。
(1)基準濃度未満の低濃度が、基準濃度の1/4〜9/10の濃度である。
(2)基準濃度未満の低濃度が、基準濃度の1/3〜9/10の濃度である。
In addition, the method for preventing attachment disorders of marine organisms of the present invention more exerts the above effects when any one of the following conditions is satisfied.
(1) A low concentration less than the reference concentration is a concentration of 1/4 to 9/10 of the reference concentration.
(2) A low concentration less than the reference concentration is a concentration of 1/3 to 9/10 of the reference concentration.

(海生生物の付着障害防止方法)
本発明の海水冷却水系の海生生物の付着障害防止方法は、二酸化塩素を一定濃度で連続的に添加したときに所望の海生生物の付着障害防止効果が得られる海水中の二酸化塩素の最小濃度を基準濃度とし、
前記海水冷却水系の海水中の二酸化塩素濃度が、前記基準濃度未満の低濃度の期間と前記基準濃度以上の高濃度の期間とが交互になるように、二酸化塩素または該海水中で二酸化塩素を発生し得る化合物を添加することを特徴とする。
(How to prevent adhesion disorders of marine organisms)
The method for preventing adhesion disorders of marine organisms in a seawater cooling water system of the present invention is the minimum amount of chlorine dioxide in seawater that can obtain a desired effect of preventing adhesion disorders of marine organisms when chlorine dioxide is continuously added at a constant concentration. Using the concentration as the reference concentration
Chlorine dioxide or chlorine dioxide in the seawater is added so that the chlorine dioxide concentration in the seawater of the seawater cooling water system alternates between the low concentration period below the reference concentration and the high concentration period above the reference concentration. It is characterized by adding a compound that can be generated.

(二酸化塩素)
本発明において用いられる二酸化塩素は、極めて不安定な化学物質であるため、その貯蔵や輸送は非常に困難である。したがって、二酸化塩素または海水中で二酸化塩素を発生し得る化合物を海水に直接添加してもよいが、その場で公知の方法により二酸化塩素を製造(生成)するか、または海水中で二酸化塩素を発生し得る化合物を水に添加して二酸化塩素を発生させ、所望の添加濃度に調整して用いるのが好ましい。ここで、「水」としては、特に限定されず、工業用水、上水などが挙げられる。
例えば、次のような反応により二酸化塩素を製造することができ、市販の二酸化塩素発生器(装置)を用いることもできる。
(1)次亜塩素酸ナトリウムと塩酸と亜塩素酸ナトリウムとの反応
NaOCl+2HCl+2NaClO2 → 2ClO2+3NaCl+H2
(2)亜塩素酸ナトリウムと塩酸との反応
5NaClO2+4HCl → 4ClO2+5NaCl+2H2
(3)塩素酸ナトリウム、過酸化水素および硫酸との反応
2NaClO3+H22+H2SO4 → 2ClO2+Na2SO4+O2+2H2
(Chlorine dioxide)
Chlorine dioxide used in the present invention is an extremely unstable chemical substance, and therefore its storage and transportation are extremely difficult. Therefore, chlorine dioxide or a compound capable of generating chlorine dioxide in seawater may be added directly to seawater, but chlorine dioxide is produced (produced) by a known method on the spot, or chlorine dioxide is produced in seawater. It is preferable to add a compound that can be generated to water to generate chlorine dioxide and adjust the concentration to a desired value before use. Here, the "water" is not particularly limited, and examples thereof include industrial water and clean water.
For example, chlorine dioxide can be produced by the following reaction, and a commercially available chlorine dioxide generator (equipment) can also be used.
(1) Reaction of sodium hypochlorite with hydrochloric acid and sodium chlorite NaOCl + 2HCl + 2NaClO 2 → 2ClO 2 + 3NCl + H 2 O
(2) Reaction of sodium chlorite with hydrochloric acid 5NaClO 2 + 4HCl → 4ClO 2 + 5 NaCl + 2H 2 O
(3) Reaction with sodium chlorate, hydrogen peroxide and sulfuric acid 2 NaClO 3 + H 2 O 2 + H 2 SO 4 → 2ClO 2 + Na 2 SO 4 + O 2 + 2H 2 O

(基準濃度)
本発明の海生生物の付着障害防止方法では、二酸化塩素の基準濃度に基づいて、海水冷却水系の海水に特定濃度の二酸化塩素または海水中で二酸化塩素を発生し得る化合物(以下、これらを合わせて「二酸化塩素」ともいう)を特定時間添加する。
本発明において、二酸化塩素の「基準濃度」とは、二酸化塩素を一定濃度で連続的に添加したときに所望の海生生物の付着障害防止効果が得られる海水中の二酸化塩素の最小濃度を意味する。
なお、「基準濃度」は、二酸化塩素の添加時間により変動する。例えば、一日当たりの添加を考えた場合、添加時間が長ければ基準濃度は低くなる。逆に、添加時間が短ければ基準濃度は高くなる。したがって、本発明における基準濃度とは、二酸化塩素を任意の時間一定濃度で連続的に添加したとき、所望の海生生物の付着防止効果が得られる海水中の二酸化塩素の最小濃度を意味する。上記の任意の時間とは、実際に添加する時間に合わせればよい。
(Reference concentration)
In the method for preventing adhesion disorders of marine organisms of the present invention, a specific concentration of chlorine dioxide in seawater of a seawater cooling water system or a compound capable of generating chlorine dioxide in seawater based on a reference concentration of chlorine dioxide (hereinafter, these are combined). (Also called "chlorine dioxide") is added for a specific time.
In the present invention, the "reference concentration" of chlorine dioxide means the minimum concentration of chlorine dioxide in seawater where a desired effect of preventing adhesion damage to marine organisms can be obtained when chlorine dioxide is continuously added at a constant concentration. To do.
The "reference concentration" varies depending on the addition time of chlorine dioxide. For example, when considering the daily addition, the longer the addition time, the lower the reference concentration. On the contrary, the shorter the addition time, the higher the reference concentration. Therefore, the reference concentration in the present invention means the minimum concentration of chlorine dioxide in seawater at which a desired effect of preventing the adhesion of marine organisms can be obtained when chlorine dioxide is continuously added at a constant concentration for an arbitrary time. The above-mentioned arbitrary time may be adjusted to the time actually added.

また、「基準濃度」は、添加対象の海水系冷却水系の海水の汚れ状態や温度(水温)、海水に生息する海生生物種(付着生物種)などによっても変動するので、予め下記の方法により、添加対象の海水系冷却水系に水路試験装置を設けて「海生生物付着防止効果」を測定し、その結果から決定することができる。 In addition, the "reference concentration" varies depending on the pollution state and temperature (water temperature) of the seawater of the seawater system cooling water system to be added, the marine organism species (attached organism species) that inhabit the seawater, etc., so the following method is used in advance. Therefore, it is possible to provide a water channel test device in the seawater system cooling water system to be added, measure the "effect of preventing adhesion of marine organisms", and determine from the result.

(1)付着防止効果確認用のアクリル製カラム(内径64mm×長さ300mm×厚さ2mm、表面積602.88cm2)を設置した多系統の水路(試験区)に、測定対象の海水を流量1m3/hで一過式に通水する。
(2)薬剤無添加(ブランク)の水路を設け、その他の水路にそれぞれ濃度(カラム内での設定濃度)の異なる二酸化塩素を各水路のカラムの上流側(手前)から任意の時間一定濃度で連続的に添加する(一日当たり24時間未満の任意の時間でよい場合、その添加時間は一日当たり20時間添加とする)。
(3)薬剤無添加の水路のカラム内に海生生物が50g付着した時点で、海水の通水と薬剤添加を停止する。
(4)各水路のカラムを取り出し、付着した海生生物を含むカラムの質量W1(g)を計量し、予め試験前に測定しておいた乾燥時のカラムの質量W0(g)との差から付着生物量[W1−W0(g)]を求める。
(5)付着生物量が5g/600cm2以下の場合に十分な海生生物の付着防止効果があると判断し、その薬剤濃度を「基準濃度」とする。
なお、上記(3)の付着生物量が50gに満たない場合、その付着生物量の0.1倍以下になる場合を「十分な海生生物の付着障害防止効果あり」と判断し、そのときの薬剤濃度を「基準濃度」としてもよく、また海水冷却水系で薬剤添加により障害対象となる海生生物の付着がないときの薬剤最小濃度を「基準濃度」と判断してもよい。
(1) A flow rate of seawater to be measured is 1 m in a multi-system waterway (test plot) equipped with an acrylic column (inner diameter 64 mm x length 300 mm x thickness 2 mm, surface area 602.88 cm 2) for confirming the adhesion prevention effect. Water is passed transiently at 3 / h.
(2) A chemical-free (blank) channel is provided, and chlorine dioxide having different concentrations (set concentration in the column) is added to each channel from the upstream side (front) of the column in each channel at a constant concentration for an arbitrary time. Add continuously (if any time less than 24 hours per day is acceptable, the addition time shall be 20 hours per day).
(3) When 50 g of marine organisms adhere to the column of the chemical-free waterway, the passage of seawater and the addition of chemicals are stopped.
(4) The column of each channel is taken out, the mass W1 (g) of the column containing the attached marine organisms is measured, and the difference from the mass W0 (g) of the column at the time of drying measured in advance before the test. The amount of attached organisms [W1-W0 (g)] is obtained from.
(5) When the amount of attached organisms is 5 g / 600 cm 2 or less, it is judged that there is a sufficient effect of preventing the attachment of marine organisms, and the drug concentration is defined as the "reference concentration".
In addition, when the amount of attached organisms in (3) above is less than 50 g, and when the amount of attached organisms is 0.1 times or less of the amount of attached organisms, it is judged that "there is a sufficient effect of preventing attachment disorders of marine organisms". The drug concentration may be defined as the "reference concentration", and the minimum concentration of the drug when there is no attachment of marine organisms to be damaged by the addition of the drug in the seawater cooling water system may be determined as the "reference concentration".

海水を通水する期間および薬剤を添加する期間は、海水系冷却水系の海水の状態により異なるが、通常、20〜90日程度である。
試験例に記載のように、その場で二酸化塩素を調製して用いる場合には、予備試験において二酸化塩素の発生を確かめておく。
付着生物量には、ムラサキイガイなどのイガイ類やフジツボ類、コケムシ類などの海生付着生物と共に、カラムに付着するスライムの排泄物や死骸、細胞外分泌物などの有機質を多く含むデトリタス、海水中に含まれる粘度粒子や浮遊物も含めることとする。
The period for passing seawater and the period for adding chemicals vary depending on the state of seawater in the seawater system cooling water system, but are usually about 20 to 90 days.
When chlorine dioxide is prepared and used on the spot as described in the test example, the generation of chlorine dioxide should be confirmed in a preliminary test.
The amount of attached organisms includes sessile organisms such as mussels and marine attached organisms such as barnacles and mussels, as well as detritus, which contains a large amount of organic substances such as slime excreta, carcasses, and extracellular secretions that adhere to columns, in seawater. The viscous particles and suspended matter contained are also included.

また、「基準濃度」は、海生生物の付着障害を受ける熱交換器や復水器またはその前の配管などにおいて、二酸化塩素を一定濃度で連続的に添加することにより十分な海生生物の付着障害防止効果が得られる二酸化塩素の最小濃度ともいえる。
したがって、実際に海生生物の付着障害防止のために二酸化塩素を一定濃度で連続的に添加している海水冷却水系においては、熱交換器や復水器では海生生物の付着防止に有効な最小濃度が維持されていると考えられるので、出口近傍での二酸化塩素濃度を基準濃度とすることもできる。
上記のように「基準濃度」は、添加対象の海水系冷却水系の海水の汚れ状態や温度(水温)、海水に生息する海生生物種(付着生物種)などにより変動するが、通常、熱交換器や復水器の海生生物付着の対象設備出口近傍において、0.02〜0.10mg/L程度である。
In addition, the "reference concentration" is sufficient for marine organisms by continuously adding chlorine dioxide at a constant concentration in heat exchangers, condensers, or piping in front of them, which are subject to adhesion disorders of marine organisms. It can be said that it is the minimum concentration of chlorine dioxide that can prevent adhesion damage.
Therefore, in a seawater cooling water system in which chlorine dioxide is continuously added at a constant concentration to prevent adhesion damage to marine organisms, heat exchangers and condensers are effective in preventing adhesion of marine organisms. Since it is considered that the minimum concentration is maintained, the chlorine dioxide concentration near the outlet can be used as the reference concentration.
As described above, the "reference concentration" varies depending on the pollution state and temperature (water temperature) of the seawater of the seawater system cooling water system to be added, the marine organism species (attached organism species) that inhabit the seawater, etc., but usually heat It is about 0.02 to 0.10 mg / L in the vicinity of the outlet of the target facility for marine organism adhesion in the exchanger and condenser.

本発明では、「低濃度の期間」と「高濃度の期間」とを交互に設けることが必要であり、このような構成を採用することにより、薬剤の総使用量が削減されるにもかかわらず、広範な海生生物種やスライムの付着障害を持続して防止することができる。
すなわち、本発明では、二酸化塩素を用いて海水冷却水系の海生生物の付着障害を防止しようとする、例えば、熱交換器のような所望の場所における海水中の二酸化塩素が所望の濃度になるように、より具体的には「低濃度の期間」と「高濃度の期間」とが交互になるように、海水冷却水系中の任意の場所に二酸化塩素を添加して、二酸化塩素の濃度を調整する。
したがって、二酸化塩素の添加の観点では、「低濃度の期間」および「高濃度の期間」は、それぞれ「低濃度添加の期間」および「高濃度添加の期間」と言い換えてもよい。
In the present invention, it is necessary to alternately provide "low concentration period" and "high concentration period", and by adopting such a configuration, the total amount of the drug used can be reduced. However, it is possible to continuously prevent a wide range of marine species and slime adhesion disorders.
That is, in the present invention, chlorine dioxide is used to prevent adhesion damage of marine organisms in the seawater cooling water system, for example, chlorine dioxide in seawater at a desired place such as a heat exchanger has a desired concentration. So, more specifically, chlorine dioxide is added to any place in the seawater cooling water system so that the "low concentration period" and the "high concentration period" alternate to increase the concentration of chlorine dioxide. adjust.
Therefore, from the viewpoint of chlorine dioxide addition, the "low concentration period" and the "high concentration period" may be rephrased as the "low concentration addition period" and the "high concentration addition period", respectively.

(低濃度の期間)
本発明の海生生物の付着障害防止方法では、海水冷却水系の海水中の二酸化塩素濃度が基準濃度未満の低濃度になるように二酸化塩素を添加する期間を設ける。
基準濃度未満の低濃度は、基準濃度の1/4〜9/10の濃度であるのが好ましい。
低濃度が基準濃度の1/4未満では、十分な海生生物の付着障害防止効果が得られないことがある。一方、低濃度が基準濃度の9/10を超えると、薬剤添加量の削減効果が得られないことがある。
好ましい低濃度は、基準濃度の1/3〜9/10であり、より好ましくは2/5〜9/10の濃度、さらに好ましくは基準濃度の2/3〜9/10の濃度である。
上記のように低濃度は、添加対象の海水系冷却水系の海水の汚れ状態や温度(水温)、海水に生息する海生生物種(付着生物種)などにより変動するが、通常、海生生物付着の対象設備出口近傍において0.008〜0.09mg/L程度、好ましくは0.01〜0.05mg/L程度である。
(Period of low concentration)
In the method for preventing adhesion disorders of marine organisms of the present invention, a period for adding chlorine dioxide is provided so that the chlorine dioxide concentration in the seawater of the seawater cooling water system becomes a low concentration below the reference concentration.
A low concentration below the reference concentration is preferably a concentration of 1/4 to 9/10 of the reference concentration.
If the low concentration is less than 1/4 of the standard concentration, a sufficient effect of preventing adhesion disorders of marine organisms may not be obtained. On the other hand, if the low concentration exceeds 9/10 of the reference concentration, the effect of reducing the amount of the drug added may not be obtained.
The preferred low concentration is 1/3 to 9/10 of the reference concentration, more preferably 2/5 to 9/10, and even more preferably 2/3 to 9/10 of the reference concentration.
As described above, the low concentration varies depending on the pollution state and temperature (water temperature) of the seawater of the seawater system cooling water system to be added, the marine organism species (attached organism species) that inhabit the seawater, etc., but usually marine organisms. It is about 0.008 to 0.09 mg / L, preferably about 0.01 to 0.05 mg / L in the vicinity of the outlet of the equipment to be adhered.

「低濃度の期間」での二酸化塩素の添加時間は、二酸化塩素濃度にもよるが、その濃度が0.008〜0.09mg/Lである場合には、一日当たり6時間以上であるのが好ましい。
添加時間が6時間未満では、「高濃度の期間」を交互に設けても十分な海生生物の付着障害防止効果が得られないことがある。
より好ましい添加時間は、8時間以上、さらに好ましい順に10時間以上、16時間以上、18時間以上、20時間以上、22時間以上である。
「低濃度の期間」は、一日当たり上記時間となるように何回かに分けて添加してもよい。
The addition time of chlorine dioxide in the "low concentration period" depends on the chlorine dioxide concentration, but when the concentration is 0.008 to 0.09 mg / L, it is 6 hours or more per day. preferable.
If the addition time is less than 6 hours, a sufficient effect of preventing adhesion disorders of marine organisms may not be obtained even if "high concentration periods" are alternately provided.
More preferable addition times are 8 hours or more, and more preferably 10 hours or more, 16 hours or more, 18 hours or more, 20 hours or more, and 22 hours or more in that order.
The "low concentration period" may be added in several portions at the above time per day.

(高濃度の期間)
本発明の海生生物の付着障害防止方法では、海水冷却水系の海水中の二酸化塩素濃度が基準濃度以上の高濃度になるように二酸化塩素を添加する期間を設ける。
基準濃度以上の高濃度は、添加対象の海水系冷却水系の海水の汚れ状態や温度(水温)、海水に生息する海生生物種(付着生物種)などにより変動するが、通常、海生生物付着の対象設備出口近傍において0.02〜0.5mg/L程度、好ましくは0.03〜0.5mg/L程度、より好ましくは0.05〜0.5mg/L程度である。
(Period of high concentration)
In the method for preventing adhesion disorders of marine organisms of the present invention, a period for adding chlorine dioxide is provided so that the chlorine dioxide concentration in the seawater of the seawater cooling water system becomes a high concentration equal to or higher than the reference concentration.
High concentrations above the standard concentration vary depending on the pollution state and temperature (water temperature) of the seawater of the seawater system cooling water system to be added, marine organism species (attached organism species) that inhabit the seawater, etc., but usually marine organisms It is about 0.02 to 0.5 mg / L, preferably about 0.03 to 0.5 mg / L, and more preferably about 0.05 to 0.5 mg / L in the vicinity of the outlet of the equipment to be adhered.

「高濃度の期間」での二酸化塩素の添加時間は、二酸化塩素濃度にもよるが、その濃度が0.02〜0.5mg/Lである場合には、一日当たり0.2〜8時間であるのが好ましい。
添加時間が0.2時間未満では、「低濃度の期間」を交互に設けても十分な海生生物の付着障害防止効果が得られないことがある。一方、添加時間が8時間を超えると、薬剤添加量の削減効果が得られないことがある。
より好ましい添加時間は、0.2〜7時間であり、さらに好ましい順に0.2〜6時間、0.35〜6時間、0.35〜4時間、0.5〜4時間、1〜4時間である。
The chlorine dioxide addition time in the "high concentration period" depends on the chlorine dioxide concentration, but when the concentration is 0.02 to 0.5 mg / L, it is 0.2 to 8 hours per day. It is preferable to have it.
If the addition time is less than 0.2 hours, a sufficient effect of preventing adhesion disorders of marine organisms may not be obtained even if "low concentration periods" are alternately provided. On the other hand, if the addition time exceeds 8 hours, the effect of reducing the amount of the drug added may not be obtained.
The more preferable addition time is 0.2 to 7 hours, and more preferably 0.2 to 6 hours, 0.35 to 6 hours, 0.35 to 4 hours, 0.5 to 4 hours, and 1 to 4 hours in that order. Is.

「高濃度の期間」における二酸化塩素濃度と添加時間は、通常、所望の効果に対して、濃度が高いほど添加時間が短くなり、基準濃度に近いほど添加時間が長くなる傾向にある。
また、「低濃度の期間」と「高濃度の期間」とを、一日を超えて交互に設けてもよく、「低濃度の期間」と「高濃度の期間」との間に、薬剤無添加の期間を設けてもよい。
The chlorine dioxide concentration and the addition time in the "high concentration period" usually tend to be shorter as the concentration is higher and longer as the concentration is closer to the reference concentration, with respect to the desired effect.
Further, the "low concentration period" and the "high concentration period" may be alternately provided for more than one day, and there is no drug between the "low concentration period" and the "high concentration period". A period of addition may be provided.

(他の添加剤)
本発明の海生生物の付着障害防止方法では、当該技術分野で公知の他の海生生物付着防止剤を併用してもよく、過酸化水素;ジアミン、第3級アミン、第4級アンモニウム塩などのカチオン系界面活性剤;ジアルキルジチオカルバミン酸塩;他の塩素剤(電解塩素を含む);臭素剤を併用するのが特に好ましい。
また、本発明の海生生物の付着障害防止方法では、本発明の効果を阻害しない限りにおいて、当該技術分野で公知の他の添加剤を併用してもよく、例えば、鉄系および銅系の金属腐食防止剤、消泡剤などが挙げられる。
(Other additives)
In the method for preventing marine biofouling of the present invention, other marine biofouling preventive agents known in the art may be used in combination, and hydrogen peroxide; diamine, tertiary amine, quaternary ammonium salt may be used in combination. Cationic surfactants such as; dialkyldithiocarbamate; other chlorine agents (including electrolytic chlorine); bromine agents are particularly preferred.
Further, in the method for preventing adhesion disorders of marine organisms of the present invention, other additives known in the art may be used in combination as long as the effects of the present invention are not impaired. Examples include metal corrosion inhibitors and antifoaming agents.

(添加場所)
海水冷却水系は、例えば、取水系設備、復水器やその他機器などの冷却対象となる設備および放水系設備などからなる。取水系設備は、導水路、海水中の異物を除去するスクリーン、循環水ポンプ(取水ポンプ)および循環水管(取水管)などからなる。
(Addition place)
The seawater cooling water system includes, for example, water intake system equipment, equipment to be cooled such as a condenser and other equipment, and water discharge system equipment. The water intake system equipment consists of a headrace, a screen for removing foreign substances in seawater, a circulating water pump (water intake pump), a circulating water pipe (water intake pipe), and the like.

本発明における二酸化塩素の添加場所は、取水路、熱交換器または復水器に付帯する配管中や導水路、熱交換器の入口または復水器の入口のいずれであってもよいが、海生生物の付着による障害防止効果の点で、取水ポンプの取水口近傍、熱交換器または復水器の入口が好ましい。
また、本発明における二酸化塩素の添加場所は、1箇所に限らず、本発明の添加条件に適合する、すなわち二酸化塩素を用いて海水冷却水系の海生生物の付着障害を防止しようとする所望の場所における海水中の二酸化塩素の濃度について、「低濃度の期間」と「高濃度の期間」とが交互に設けられる限り、複数箇所設けてもよい。
The place where chlorine dioxide is added in the present invention may be in the intake channel, the pipe attached to the heat exchanger or the condenser, the headrace, the inlet of the heat exchanger or the inlet of the condenser, but the sea. In terms of the effect of preventing damage due to the adhesion of living organisms, the vicinity of the intake of the intake pump and the inlet of the heat exchanger or condenser are preferable.
Further, the place where chlorine dioxide is added in the present invention is not limited to one place, and it is desired to meet the addition conditions of the present invention, that is, to prevent adhesion damage of marine organisms in a seawater cooling water system by using chlorine dioxide. Regarding the concentration of chlorine dioxide in seawater at a place, as long as a "low concentration period" and a "high concentration period" are alternately provided, a plurality of places may be provided.

(添加方法)
本発明における二酸化塩素の添加方法としては、注入ポンプなどを用いた方法が挙げられる。本発明において微量の薬剤を海水冷却水系中に、迅速にかつ実質的に均一に拡散させるためには、従来の物理的手段を用いることができる。具体的には、該水系中への拡散器、撹拌装置や邪魔板などの設置が挙げられる。また、これらに該当する設備は海水冷却水系に付設されているので、これを転用してもよい。
(Addition method)
Examples of the method for adding chlorine dioxide in the present invention include a method using an injection pump or the like. In the present invention, conventional physical means can be used to diffuse a trace amount of the drug into the seawater cooling water system quickly and substantially uniformly. Specific examples thereof include installation of a diffuser, a stirrer, a baffle plate, etc. in the water system. In addition, since the equipment corresponding to these is attached to the seawater cooling water system, it may be diverted.

本発明を以下の試験例により具体的に説明するが、本発明はこれらにより限定されるものではない。 The present invention will be specifically described with reference to the following test examples, but the present invention is not limited thereto.

[試験例1]
二酸化塩素による海生生物の付着障害防止効果を確認した。
太平洋に面した和歌山県沿岸の某所に水路試験装置を設け、試験を行った。
水中ポンプを用いて揚水した未濾過の海水(pH8)を、5系統に分岐させた水路
(試験区)に流量1m3/hで70日間(2018年8月〜同年10月)、一過式に通水し、各水路に二酸化塩素を、表1に示す薬剤濃度および一日当たりの添加時間になるように添加した。
[Test Example 1]
We confirmed the effect of chlorine dioxide on preventing adhesion disorders of marine organisms.
A waterway test device was installed somewhere along the coast of Wakayama Prefecture facing the Pacific Ocean, and tests were conducted.
Unfiltered seawater (pH 8) pumped using a submersible pump is placed in a channel (test plot) branched into 5 systems at a flow rate of 1 m 3 / h for 70 days (August 2018 to October 2018). Chlorine dioxide was added to each channel so as to have the drug concentration shown in Table 1 and the addition time per day.

上記の「基準濃度」の決定方法に準拠した予備試験により、基準濃度を測定した。すなわち、二酸化塩素の添加時間を24時間として21日間海水を通水した。その結果、薬剤無添加の水路のカラム内に海生生物が50g付着した。そこで、通水と薬剤添加を停止し、二酸化塩素をそれぞれの濃度で添加した水路のカラムを取り出し、海生生物が付着したカラムの付着生物量を求め、付着生物量が5g/600cm2以下となった二酸化塩素の添加量を基準濃度とした。その結果、本試験の水系における二酸化塩素の基準濃度は、0.025mg/Lであると判断したので、「低濃度の期間」の濃度として0.010mg/Lを設定し、「高濃度の期間」の濃度として0.10mg/Lと0.19mg/Lを設定した。
なお、薬剤濃度は下記の付着障害防止効果確認用のアクリル製カラム内での設定濃度であるが、本試験例では、薬剤添加後に下記するテストチューブから放出されるまでの経路が短く、設定濃度が放出濃度とほぼ同程度であることを確認している。
The reference concentration was measured by a preliminary test based on the above method for determining the "reference concentration". That is, seawater was passed for 21 days with the addition time of chlorine dioxide being 24 hours. As a result, 50 g of marine organisms adhered to the column of the water channel to which no chemical was added. Therefore, water flow and chemical addition were stopped, the column of the channel to which chlorine dioxide was added at each concentration was taken out, and the amount of attached organisms on the column to which marine organisms were attached was determined, and the amount of attached organisms was 5 g / 600 cm 2 or less. The amount of chlorine dioxide added was used as the reference concentration. As a result, it was determined that the standard concentration of chlorine dioxide in the water system of this test was 0.025 mg / L, so 0.010 mg / L was set as the concentration for the "low concentration period" and the "high concentration period" was set. The concentrations of "." Were set to 0.10 mg / L and 0.19 mg / L.
The drug concentration is the set concentration in the acrylic column for confirming the effect of preventing adhesion disorders below, but in this test example, the route from the addition of the drug to the release from the test tube described below is short, and the set concentration. Has been confirmed to be about the same as the released concentration.

各水路内には、付着障害防止効果確認用にアクリル製カラム(内径64mm×長さ300mm×厚さ2mm、表面積602.88cm2)を挿入し、通水終了後にカラムに付着した付着生物量を測定し、付着障害防止効果を評価した。
また、各水路内には、スライム汚れ防止効果確認用にチタン管からなるテストチューブ(内径23.4mm、長さ1000mm、肉厚1.0mm)を設置し、通水終了後にテストチューブの内面に形成されたスライムを主体とする汚れ量を測定し、汚れ防止効果を評価した。なお、ブランクとして薬剤無添加についても試験した。
得られた結果を、薬剤濃度および一日当たりの添加時間と共に表1に示す。
An acrylic column (inner diameter 64 mm x length 300 mm x thickness 2 mm, surface area 602.88 cm 2 ) is inserted into each channel to check the effect of preventing adhesion obstacles, and the amount of attached organisms attached to the column after water flow is completed. It was measured and the effect of preventing adhesion damage was evaluated.
In addition, a test tube (inner diameter 23.4 mm, length 1000 mm, wall thickness 1.0 mm) made of titanium tube is installed in each water channel to confirm the slime stain prevention effect, and is placed on the inner surface of the test tube after water flow is completed. The amount of stains mainly composed of the formed slime was measured, and the stain prevention effect was evaluated. In addition, it was also tested that no drug was added as a blank.
The results obtained are shown in Table 1 along with the drug concentration and the time of addition per day.

(二酸化塩素)
二酸化塩素は、表1に示す濃度の二酸化塩素が得られるように、亜塩素酸ナトリウムおよび塩酸をそれぞれ適宜純水で希釈した水溶液を、薬剤添加ポイント前のチューブ内で混合し、1時間の滞留時間を持たせることで発生した二酸化塩素水溶液を付着障害防止効果確認用アクリル製カラムおよびチタン管からなるテストチューブの手前から定量ポンプを用いて添加した。なお、二酸化塩素の発生については、予備試験においてその発生を確認している。
(Chlorine dioxide)
As for chlorine dioxide, an aqueous solution obtained by appropriately diluting sodium chlorite and hydrochloric acid with pure water is mixed in a tube before the chemical addition point and retained for 1 hour so that chlorine dioxide having the concentration shown in Table 1 can be obtained. An aqueous solution of chlorine dioxide generated after a long period of time was added using a metering pump from the front of a test tube composed of an acrylic column for confirming the effect of preventing adhesion damage and a titanium tube. Regarding the generation of chlorine dioxide, the generation has been confirmed in a preliminary test.

(付着障害防止効果の確認)
試験後、水路から取り外したカラムの質量Wa(g)を測定した。予め試験前に測定しておいた乾燥時のカラムの質量Wb(g)と共に、次式により付着生物量(g)を算出した。
付着生物量(g)=Wa−Wb
この試験期間における海水温は28〜26℃で推移し、薬剤無添加の水路のカラム内の付着生物量は326g/600cm2と多く、付着生物は、主としてミドリイガイなどのイガイ類やフジツボ類、コケムシ類などの海生付着生物に由来する。また、カラムには、付着生物やスライムの排泄物や死骸、細胞外分泌物などの有機質を多く含むデトリタス、海水中に含まれる粘度粒子や浮遊物も付着するが、これらも付着生物量に含める。
ブランクでの海生生物の付着状況から、本試験例では付着生物量が15g以下の場合に十分な海生生物の付着障害防止効果があると判断できる。また、付着生物量が5g以下の場合には、生物や汚れの付着が目視では全く確認されず、最良の海生生物の付着障害防止と判断できる。
(Confirmation of adhesion failure prevention effect)
After the test, the mass Wa (g) of the column removed from the water channel was measured. The amount of attached organisms (g) was calculated by the following formula together with the mass Wb (g) of the column at the time of drying, which was measured in advance before the test.
Adherent biological amount (g) = Wa-Wb
During this test period, the seawater temperature changed from 28 to 26 ° C, and the amount of sessile organisms in the column of the chemical-free channel was as large as 326 g / 600 cm 2, and the sessile organisms were mainly mussels such as green mussels, barnacles, and bryozoa. Derived from marine sessile organisms such as species. In addition, detritus containing a large amount of organic substances such as adhering organisms, slime excrement and carcasses, and extracellular secretions, and viscous particles and suspended matter contained in seawater also adhere to the column, and these are also included in the amount of attached organisms.
From the state of attachment of marine organisms in the blank, it can be judged that in this test example, there is a sufficient effect of preventing attachment disorders of marine organisms when the amount of attached organisms is 15 g or less. Further, when the amount of attached organisms is 5 g or less, no attachment of organisms or dirt is visually confirmed, and it can be judged that the best prevention of attachment disorders of marine organisms is achieved.

(汚れ防止効果の確認)
試験後、水路から取り外したテストチューブの内面に形成されたスライムを主体とする汚れを掻き取り、100mLのメスシリンダーに回収し、4時間静置後の湿体積を計量した。
ブランクにおいて掻き取ったスライムは主にテストチューブに付着した微生物に由来する。カラムでの付着防止効果の確認と同様に、テストチューブの内面に付着したスライムにもデトリタスが含まれるが、テストチューブのチタン管径はカラム径の約1/3であり、その管内の海水冷却水の流速は速く、ムラサキイガイなどのイガイ類やフジツボ類、コケムシ類などの海生付着生物の付着はないことを確認している。
ブランクでのスライムの付着状況から、本試験例では湿体積が5mL以下の場合に十分なスライムの付着障害防止効果があると判断できる。また、湿体積が2mL以下の場合には、スライムの付着が目視では全く確認されず、最良の海生生物の付着障害防止と判断できる。
(Confirmation of stain prevention effect)
After the test, dirt mainly composed of slime formed on the inner surface of the test tube removed from the water channel was scraped off, collected in a 100 mL graduated cylinder, and the wet volume after standing for 4 hours was measured.
The slime scraped off in the blank is mainly derived from microorganisms attached to the test tube. Similar to the confirmation of the adhesion prevention effect on the column, the slime adhering to the inner surface of the test tube also contains detritus, but the titanium tube diameter of the test tube is about 1/3 of the column diameter, and seawater cooling inside the tube. It has been confirmed that the flow velocity of water is high and that there is no attachment of mussels such as mussels and marine sessile organisms such as barnacles and mussels.
From the state of slime adhesion on the blank, it can be judged that in this test example, there is a sufficient effect of preventing slime adhesion failure when the wet volume is 5 mL or less. Further, when the wet volume is 2 mL or less, the adhesion of slime is not visually confirmed at all, and it can be judged that it is the best prevention of adhesion obstacles of marine organisms.

Figure 0006843329
Figure 0006843329

表1の結果から次のことがわかる。
(1)二酸化塩素を一日当たり20〜22時間低濃度添加すると共に、二酸化塩素を一日当たり2〜4時間高濃度添加した場合(実施例1および2)に優れた付着障害防止効果が得られること
さらに詳しくは、積算量(薬剤の総使用量)が同じでも、二酸化塩素の添加を「基準濃度」で連続的に行う方法(比較例1)と比較して、「低濃度の期間(基準濃度の2/5の濃度で一日当たり20〜22時間添加)」と「高濃度の期間(基準濃度の7.6倍または4倍の濃度で一日当たり2〜4時間)」とが交互になるように行うことにより(実施例1および2)、「付着生物量」が減少すること
(2)濃度0.010mg/Lの二酸化塩素を10時間で2回低濃度添加し、濃度0.10mg/Lの二酸化塩素を2時間で2回高濃度添加した場合(実施例2)には、濃度0.010mg/Lの二酸化塩素を22時間低濃度添加し、2時間だけ濃度0.19mg/Lの二酸化塩素を高濃度添加した場合(実施例1)と比較して、試験後のカラムについて付着物量が少ないこと
さらに詳しくは、二酸化塩素の添加を「低濃度の期間(基準濃度の2/5の濃度で10時間添加)」と「高濃度の期間(基準濃度の4倍の濃度で2時間添加)」とが交互になるように一日当たり2回繰り返すことにより(実施例2)、「付着生物量」が顕著に減少すること
The following can be seen from the results in Table 1.
(1) When chlorine dioxide is added in a low concentration for 20 to 22 hours per day and chlorine dioxide is added in a high concentration for 2 to 4 hours per day (Examples 1 and 2), an excellent effect of preventing adhesion disorders can be obtained. More specifically, even if the integrated amount (total amount of the drug used) is the same, compared with the method of continuously adding chlorine dioxide at the "reference concentration" (Comparative Example 1), "a period of low concentration (reference concentration)""2/5 of the concentration added for 20 to 22 hours per day)" and "High concentration period (7.6 times or 4 times the standard concentration for 2 to 4 hours per day)" alternate. (Examples 1 and 2), the "adherent biological amount" is reduced. (2) A low concentration of 0.010 mg / L of chlorine dioxide is added twice in 10 hours to a concentration of 0.10 mg / L. When the high concentration of chlorine dioxide was added twice in 2 hours (Example 2), a low concentration of 0.010 mg / L of chlorine dioxide was added for 22 hours, and the concentration of 0.19 mg / L of dioxide was only 2 hours. Compared with the case where high concentration of chlorine was added (Example 1), the amount of deposits on the column after the test was small. More specifically, the addition of chlorine dioxide was carried out during the period of low concentration (concentration of 2/5 of the standard concentration). By repeating twice a day (Example 2) so that "addition for 10 hours" and "period of high concentration (addition for 2 hours at a concentration four times the standard concentration)" are repeated (Example 2), "Amount of adherent organisms". Is significantly reduced

[試験例2]
二酸化塩素を「低濃度の期間」と「高濃度の期間」とが交互になるように添加したときの海生生物の付着障害防止効果を確認した。
太平洋に面した和歌山県沿岸の某所に水路試験装置を設け、試験を行った。
水中ポンプを用いて揚水した未濾過の海水(pH8)を、6系統に分岐させた水路(試験区)に流量1m3/hで76日間(2019年3月〜同年6月)、一過式に通水し、各水路に二酸化塩素を、表2に示す薬剤濃度および一日当たりの添加時間になるように添加した。
[Test Example 2]
It was confirmed that chlorine dioxide was added so that the "low concentration period" and the "high concentration period" alternated, and the effect of preventing adhesion damage to marine organisms was confirmed.
A waterway test device was installed somewhere along the coast of Wakayama Prefecture facing the Pacific Ocean, and tests were conducted.
Unfiltered seawater (pH 8) pumped using a submersible pump is placed in a channel (test plot) branched into 6 systems at a flow rate of 1 m 3 / h for 76 days (March 2019 to June 2019). Chlorine dioxide was added to each channel so as to have the drug concentration shown in Table 2 and the addition time per day.

上記の「基準濃度」の決定方法に準拠した予備試験により、基準濃度を測定した。すなわち、二酸化塩素の添加時間を24時間として50日間海水を通水した。その結果、薬剤無添加の水路のカラム内に海生生物が45g付着した。付着生物量が50gに達成しなかったが、通水と薬剤添加を停止し、二酸化塩素をそれぞれの濃度で添加した水路のカラムを取り出し、海生生物が付着したカラムの付着生物量を求め、付着生物量が4.5g/600cm2以下となった二酸化塩素の添加量を基準濃度とした。その結果、本試験の水系における二酸化塩素の基準濃度は、0.025mg/Lであると判断したので、「低濃度の期間」の濃度として0.020mg/Lを設定し、「高濃度の期間」の濃度として0.030mg/L〜0.070mg/Lを設定した。
なお、薬剤濃度は下記の付着障害防止効果確認用のアクリル製カラム内での設定濃度であるが、本試験例では、薬剤添加後に下記するテストチューブから放出されるまでの経路が短く、設定濃度が放出濃度とほぼ同程度であることを確認している。
The reference concentration was measured by a preliminary test based on the above method for determining the "reference concentration". That is, seawater was passed for 50 days with the addition time of chlorine dioxide being 24 hours. As a result, 45 g of marine organisms adhered to the column of the water channel to which no chemical was added. Although the amount of attached organisms did not reach 50 g, the water flow and the addition of chemicals were stopped, the column of the channel to which chlorine dioxide was added at each concentration was taken out, and the amount of attached organisms on the column to which marine organisms were attached was determined. The amount of chlorine dioxide added when the amount of attached organisms was 4.5 g / 600 cm 2 or less was used as the reference concentration. As a result, it was determined that the standard concentration of chlorine dioxide in the water system of this test was 0.025 mg / L, so 0.020 mg / L was set as the concentration for the "low concentration period" and the "high concentration period" was set. The concentration was set to 0.030 mg / L to 0.070 mg / L.
The drug concentration is the set concentration in the acrylic column for confirming the effect of preventing adhesion disorders below, but in this test example, the route from the addition of the drug to the release from the test tube described below is short, and the set concentration. Has been confirmed to be about the same as the released concentration.

各水路内には、付着障害防止効果確認用にアクリル製カラム(内径64mm×長さ300mm×厚さ2mm、表面積602.88cm2)を挿入し、通水終了後にカラムに付着した付着生物量を測定し、付着障害防止効果を評価した。
また、各水路内には、スライム汚れ防止効果確認用にチタン管からなるテストチューブ(内径23.4mm、長さ1000mm、肉厚1.0mm)を設置し、通水終了後にテストチューブの内面に形成されたスライムを主体とする汚れ量を測定し、汚れ防止効果を評価した。なお、ブランクとして薬剤無添加についても試験した。
得られた結果を、薬剤濃度および一日当たりの添加時間と共に表2に示す。
An acrylic column (inner diameter 64 mm x length 300 mm x thickness 2 mm, surface area 602.88 cm 2 ) is inserted into each channel to check the effect of preventing adhesion obstacles, and the amount of attached organisms attached to the column after water flow is completed. It was measured and the effect of preventing adhesion damage was evaluated.
In addition, a test tube (inner diameter 23.4 mm, length 1000 mm, wall thickness 1.0 mm) made of titanium tube is installed in each water channel to confirm the slime stain prevention effect, and is placed on the inner surface of the test tube after water flow is completed. The amount of stains mainly composed of the formed slime was measured, and the stain prevention effect was evaluated. In addition, it was also tested that no drug was added as a blank.
The results obtained are shown in Table 2 along with the drug concentration and the time of addition per day.

(二酸化塩素)
二酸化塩素は、試験例1と同様に発生させ、添加も同様の方法で実施した。
(Chlorine dioxide)
Chlorine dioxide was generated in the same manner as in Test Example 1, and addition was carried out in the same manner.

(付着障害防止効果の確認)
試験例1と同様にして、カラムの付着生物量(g)を算出し、海生生物の付着防止効果を確認した。
この試験期間における海水温は15〜22℃で推移し、薬剤無添加の水路のカラム内の付着生物量は233g/600cm2と多く、付着生物は、主としてムラサキイガイなどのイガイ類やフジツボ類、コケムシ類などの海生付着生物に由来する。また、カラムには、付着生物やスライムの排泄物や死骸、細胞外分泌物などの有機質を多く含むデトリタス、海水中に含まれる粘度粒子や浮遊物も付着するが、これらも付着生物量に含める。
ブランクでの海生生物の付着状況から、本試験例では付着生物量が15g以下の場合に十分な海生生物の付着障害防止効果があると判断できる。また、付着生物量が5g以下の場合には、生物や汚れの付着が目視では全く確認されず、最良の海生生物の付着障害防止と判断できる。
(Confirmation of adhesion failure prevention effect)
In the same manner as in Test Example 1, the amount of attached organisms (g) on the column was calculated, and the effect of preventing the attachment of marine organisms was confirmed.
During this test period, the seawater temperature changed from 15 to 22 ° C, and the amount of sessile organisms in the column of the chemical-free waterway was as large as 233 g / 600 cm 2, and the sessile organisms were mainly mussels such as mussels, mussels, and mussels. Derived from marine sessile organisms such as species. In addition, detritus containing a large amount of organic substances such as adhering organisms, slime excrement and carcasses, and extracellular secretions, and viscous particles and suspended matter contained in seawater also adhere to the column, and these are also included in the amount of attached organisms.
From the state of attachment of marine organisms in the blank, it can be judged that in this test example, there is a sufficient effect of preventing attachment disorders of marine organisms when the amount of attached organisms is 15 g or less. Further, when the amount of attached organisms is 5 g or less, no attachment of organisms or dirt is visually confirmed, and it can be judged that the best prevention of attachment disorders of marine organisms is achieved.

(汚れ防止効果の確認)
試験例1と同様にして、4時間静置後の湿体積を計量し、汚れ防止効果を確認した。
ブランクにおいて掻き取ったスライムは主にテストチューブに付着した微生物に由来する。カラムでの付着防止効果の確認と同様に、テストチューブの内面に付着したスライムにもデトリタスが含まれるが、テストチューブのチタン管径はカラム径の約1/3であり、その管内の海水冷却水の流速は速く、ムラサキイガイなどのイガイ類やフジツボ類、コケムシ類などの海生付着生物の付着はないことを確認している。
ブランクでのスライムの付着状況から、本試験例では湿体積が5mL以下の場合に十分なスライムの付着障害防止効果があると判断できる。また、湿体積が2mL以下の場合には、スライムの付着が目視では全く確認されず、最良の海生生物の付着障害防止と判断できる。
(Confirmation of stain prevention effect)
In the same manner as in Test Example 1, the wet volume after standing for 4 hours was measured, and the stain prevention effect was confirmed.
The slime scraped off in the blank is mainly derived from microorganisms attached to the test tube. Similar to the confirmation of the adhesion prevention effect on the column, the slime adhering to the inner surface of the test tube also contains detritus, but the titanium tube diameter of the test tube is about 1/3 of the column diameter, and seawater cooling inside the tube. It has been confirmed that the flow velocity of water is high and that there is no attachment of mussels such as mussels and marine sessile organisms such as barnacles and mussels.
From the state of slime adhesion on the blank, it can be judged that in this test example, there is a sufficient effect of preventing slime adhesion failure when the wet volume is 5 mL or less. Further, when the wet volume is 2 mL or less, the adhesion of slime is not visually confirmed at all, and it can be judged that it is the best prevention of adhesion obstacles of marine organisms.

Figure 0006843329
Figure 0006843329

表2の結果から次のことがわかる。
(1)二酸化塩素の添加を「基準濃度」で一日当たり22時間連続的に行う方法(比較例3)と比較して、「低濃度の期間(基準濃度の4/5の濃度で一日当たり18時間添加)」と「高濃度の期間(基準濃度の2.8倍の濃度で一日当たり2時間)」とを交互になるように行うことにより(実施例3)、積算量(薬剤の総使用量)が削減できること
実際の使用場面を想定することにより、本発明の二酸化塩素の添加積算量の削減効果の優れていることがわかる。例えば、実施例3の積算量0.50mg/L×時間/日は、比較例3の積算量0.55mg/L×時間/日に対して、0.05mg/L×時間/日の削減効果があり、これを一般的な火力発電所の冷却用の海水取水量15万m3/時間に当てはめると、225kg/月の二酸化塩素の削減になる。
The following can be seen from the results in Table 2.
(1) Compared with the method in which chlorine dioxide is continuously added at a "reference concentration" for 22 hours per day (Comparative Example 3), "a period of low concentration (a concentration of 4/5 of the reference concentration is 18 per day). By alternating between "time addition" and "high concentration period (2.8 times the standard concentration for 2 hours per day)" (Example 3), the integrated amount (total use of the drug) The amount) can be reduced. By assuming an actual usage situation, it can be seen that the effect of reducing the accumulated amount of chlorine dioxide added of the present invention is excellent. For example, the integrated amount of 0.50 mg / L × hours / day in Example 3 has a reduction effect of 0.05 mg / L × hours / day with respect to the integrated amount of 0.55 mg / L × hours / day in Comparative Example 3. If this is applied to the amount of seawater intake for cooling a general thermal power plant of 150,000 m 3 / hour, the amount of chlorine dioxide will be reduced by 225 kg / month.

(2)二酸化塩素の添加を「基準濃度」で一日当たり22時間連続的に行う方法(比較例3)と比較して、「低濃度の期間(基準濃度の4/5の濃度で一日当たり18時間添加)」と「高濃度の期間(基準濃度の2.4倍の濃度で一日当たり3時間)」とを交互になるように行うことにより(実施例4)、同等の積算量(薬剤の総使用量)で「付着生物量」が顕著に減少すること
(3)二酸化塩素の添加を「基準濃度」の4/5の濃度で一日当たり24時間連続的に行う方法(比較例4)と比較して、「低濃度の期間(基準濃度の4/5の濃度で一日当たり18時間添加)」と「高濃度の期間(基準濃度の1.2倍の濃度で一日当たり4時間)」とを交互になるように行うことにより(実施例5)、同等の積算量(薬剤の総使用量)で「付着生物量」が顕著に減少すること
(2) Compared with the method in which chlorine dioxide is continuously added at a "reference concentration" for 22 hours per day (Comparative Example 3), "a period of low concentration (a concentration of 4/5 of the reference concentration is 18 per day). By alternately performing "time addition)" and "high concentration period (3 hours per day at a concentration 2.4 times the standard concentration)" (Example 4), an equivalent integrated amount (of the drug) The "total amount used" significantly reduces the "adherent biological amount" (3) A method in which chlorine dioxide is continuously added at a concentration of 4/5 of the "standard concentration" for 24 hours per day (Comparative Example 4). In comparison, "low concentration period (addition of 18 hours per day at a concentration of 4/5 of the standard concentration)" and "high concentration period (4 hours per day at a concentration 1.2 times the standard concentration)" (Example 5), the "adhered biological amount" is significantly reduced at the same integrated amount (total amount of the drug used).

[試験例3]
二酸化塩素を「低濃度の期間」と「高濃度添加の期間」とが交互になるように添加したときの海生生物の付着障害防止効果を確認した。
太平洋に面した和歌山県沿岸の某所に水路試験装置を設け、試験を行った。
水中ポンプを用いて揚水した未濾過の海水(pH8)を、4系統に分岐させた水路(試験区)に流量1m3/hで79日間(2019年8月〜同年10月)、一過式に通水し、各水路に二酸化塩素を、表2に示す薬剤濃度および一日当たりの添加時間になるように添加した。
[Test Example 3]
We confirmed the effect of preventing adhesion damage to marine organisms when chlorine dioxide was added so that the "low-concentration period" and the "high-concentration addition period" alternated.
A waterway test device was installed somewhere along the coast of Wakayama Prefecture facing the Pacific Ocean, and tests were conducted.
Unfiltered seawater (pH 8) pumped using a submersible pump is placed in a channel (test plot) branched into four systems at a flow rate of 1 m 3 / h for 79 days (August 2019 to October 2019). Chlorine dioxide was added to each channel so as to have the drug concentration shown in Table 2 and the addition time per day.

上記の「基準濃度」の決定方法に準拠した予備試験により、基準濃度を測定した。すなわち、二酸化塩素の添加時間を24時間として50日間海水を通水した。その結果、薬剤無添加の水路のカラム内に海生生物が50g付着した。そこで、通水と薬剤添加を停止し、二酸化塩素をそれぞれの濃度で添加した水路のカラムを取り出し、海生生物が付着したカラムの付着生物量を求め、付着生物量が5g/600cm2以下となった二酸化塩素の添加量を基準濃度とした。その結果、本試験の水系における二酸化塩素の基準濃度は、0.015mg/Lであると判断したので、「低濃度の期間」の濃度として0.012mg/Lを設定し、「高濃度の期間」の濃度として0.020mg/Lを設定した。
なお、薬剤濃度は下記の付着障害防止効果確認用のアクリル製カラム内での設定濃度であるが、本試験例では、薬剤添加後に下記するテストチューブから放出されるまでの経路が短く、設定濃度が放出濃度とほぼ同程度であることを確認している。
The reference concentration was measured by a preliminary test based on the above method for determining the "reference concentration". That is, seawater was passed for 50 days with the addition time of chlorine dioxide being 24 hours. As a result, 50 g of marine organisms adhered to the column of the water channel to which no chemical was added. Therefore, water flow and chemical addition were stopped, the column of the channel to which chlorine dioxide was added at each concentration was taken out, and the amount of attached organisms on the column to which marine organisms were attached was determined, and the amount of attached organisms was 5 g / 600 cm 2 or less. The amount of chlorine dioxide added was used as the reference concentration. As a result, it was determined that the standard concentration of chlorine dioxide in the water system of this test was 0.015 mg / L, so 0.012 mg / L was set as the concentration for the "low concentration period" and the "high concentration period" was set. The concentration was set to 0.020 mg / L.
The drug concentration is the set concentration in the acrylic column for confirming the effect of preventing adhesion disorders below, but in this test example, the route from the addition of the drug to the release from the test tube described below is short, and the set concentration. Has been confirmed to be about the same as the released concentration.

各水路内には、付着障害防止効果確認用にアクリル製カラム(内径64mm×長さ300mm×厚さ2mm、表面積602.88cm2)を挿入し、通水終了後にカラムに付着した付着生物量を測定し、付着障害防止効果を評価した。
また、各水路内には、スライム汚れ防止効果確認用にチタン管からなるテストチューブ(内径23.4mm、長さ1000mm、肉厚1.0mm)を設置し、通水終了後にテストチューブの内面に形成されたスライムを主体とする汚れ量を測定し、汚れ防止効果を評価した。なお、ブランクとして薬剤無添加についても試験した。
得られた結果を、薬剤濃度および一日当たりの添加時間と共に表3に示す。
An acrylic column (inner diameter 64 mm x length 300 mm x thickness 2 mm, surface area 602.88 cm 2 ) is inserted into each channel to check the effect of preventing adhesion obstacles, and the amount of attached organisms attached to the column after water flow is completed. It was measured and the effect of preventing adhesion damage was evaluated.
In addition, a test tube (inner diameter 23.4 mm, length 1000 mm, wall thickness 1.0 mm) made of titanium tube is installed in each water channel to confirm the slime stain prevention effect, and is placed on the inner surface of the test tube after water flow is completed. The amount of stains mainly composed of the formed slime was measured, and the stain prevention effect was evaluated. In addition, it was also tested that no drug was added as a blank.
The results obtained are shown in Table 3 along with the drug concentration and the time of addition per day.

(二酸化塩素)
二酸化塩素は、試験例1と同様に発生させ、添加も同様の方法で実施した。
(Chlorine dioxide)
Chlorine dioxide was generated in the same manner as in Test Example 1, and addition was carried out in the same manner.

(付着障害防止効果の確認)
試験例1と同様にして、カラムの付着生物量(g)を算出し、海生生物の付着防止効果を確認した。
この試験期間における海水温は29〜24℃で推移し、薬剤無添加の水路のカラム内の付着生物量は147g/600cm2と多く、付着生物は、主としてミドリイガイなどのイガイ類やフジツボ類、コケムシ類などの海生付着生物に由来する。また、カラムには、付着生物やスライムの排泄物や死骸、細胞外分泌物などの有機質を多く含むデトリタス、海水中に含まれる粘度粒子や浮遊物も付着するが、これらも付着生物量に含める。
(Confirmation of adhesion failure prevention effect)
In the same manner as in Test Example 1, the amount of attached organisms (g) on the column was calculated, and the effect of preventing the attachment of marine organisms was confirmed.
During this test period, the seawater temperature changed from 29 to 24 ° C, and the amount of sessile organisms in the column of the chemical-free waterway was as large as 147 g / 600 cm 2, and the sessile organisms were mainly mussels such as green mussels, barnacles, and bryozoa. Derived from marine sessile organisms such as species. In addition, detritus containing a large amount of organic substances such as adhering organisms, slime excrement and carcasses, and extracellular secretions, and viscous particles and suspended matter contained in seawater also adhere to the column, and these are also included in the amount of attached organisms.

(汚れ防止効果の確認)
試験例1と同様にして、4時間静置後の湿体積を計量し、汚れ防止効果を確認した。
(Confirmation of stain prevention effect)
In the same manner as in Test Example 1, the wet volume after standing for 4 hours was measured, and the stain prevention effect was confirmed.

Figure 0006843329
Figure 0006843329

表3の結果から次のことがわかる。
(1)二酸化塩素の添加を「基準濃度」で連続的に行う方法(比較例5)と比較して、「低濃度の期間(基準濃度の4/5の濃度で一日当たり17時間添加)」と「高濃度の期間(基準濃度の4/3倍の濃度で一日当たり7時間)」とが交互になるように行うことにより(実施例6)、積算量(薬剤の総使用量)が少ないにもかかわらず「湿体積量」が1/3以下に減少すること
(2)二酸化塩素の添加を「低濃度の期間(基準濃度の4/5の濃度で8.5時間添加)」と「高濃度の期間(基準濃度の4/3倍の濃度で3.5時間添加)」とが交互になるように一日当たり2回繰り返すことにより(実施例7)、積算量(薬剤の総使用量)が少ないにもかかわらず「付着生物量」が減少するとともに、「湿体積量」が1/2程度に減少すること
The following can be seen from the results in Table 3.
(1) Compared with the method of continuously adding chlorine dioxide at a "reference concentration" (Comparative Example 5), "a period of low concentration (addition at a concentration of 4/5 of the reference concentration for 17 hours per day)". And "a period of high concentration (7 hours per day at a concentration of 4/3 times the standard concentration)" are performed alternately (Example 6), so that the integrated amount (total amount of the drug used) is small. Nevertheless, the "wet volume" is reduced to 1/3 or less. (2) Addition of chlorine dioxide is added to "low concentration period (addition at a concentration of 4/5 of the standard concentration for 8.5 hours)" and " By repeating twice a day so that "a high concentration period (added at a concentration of 4/3 times the reference concentration for 3.5 hours)" alternates (Example 7), the integrated amount (total amount of the drug used). ) Is small, but the "adherent biological amount" is reduced and the "wet volume amount" is reduced to about 1/2.

海生生物は付着幼生期に付着し、その付着のメカニズムは一般的に形成されたスライム状の生物被膜に付着するものとされている。本試験の湿体積量はスライム量であり、その付着基盤となるスライム量が少ない状況を作ることは、海生生物の付着およびそれによる障害を未然に防止することにつながる。そのため湿体積量がほとんど確認できないような2mL以下であれば、薬剤による直接的な海生生物への付着防止だけでなく、間接的な付着防止効果の両面から付着障害を防止できるものと考えられる。 Marine organisms attach during the attached larval stage, and the mechanism of their attachment is generally assumed to be attached to the formed slime-like biofilm. The amount of wet volume in this test is the amount of slime, and creating a situation where the amount of slime, which is the basis for adhesion, is small leads to prevention of marine organism adhesion and damage caused by it. Therefore, if the wet volume is 2 mL or less, which can hardly be confirmed, it is considered that not only the direct adhesion prevention effect of the drug to marine organisms but also the indirect adhesion prevention effect can prevent the adhesion disorder. ..

Claims (2)

二酸化塩素を一定濃度で連続的に添加したときに所望の海生生物の付着障害防止効果が得られる一過式海水冷却水系の海水中の二酸化塩素の最小濃度を基準濃度とし、
記海水中の二酸化塩素濃度が、前記基準濃度未満の低濃度の期間と前記基準濃度以上の高濃度の期間とが交互になるように、二酸化塩素または該海水中で二酸化塩素を発生し得る化合物を低濃度および高濃度で交互に添加することからなり、
前記基準濃度未満の低濃度が、前記基準濃度の1/4〜9/10の濃度であり、前記基準濃度以上の高濃度が、0.02〜0.5mg/Lであることを特徴とする一過式海水冷却水系の海生生物の付着障害防止方法。
The minimum concentration of chlorine dioxide in the seawater of the transient seawater cooling water system, which can obtain the desired effect of preventing adhesion damage to marine organisms when chlorine dioxide is continuously added at a constant concentration, is used as the reference concentration.
Before the chlorine dioxide concentration of Kiumi underwater, so that the periods of high concentration of more than the reference concentration and low concentration period of less than the reference concentration is alternately may generate chlorine dioxide in the chlorine dioxide or該海water It consists of alternating low and high concentrations of the compound.
Low concentrations of less than the reference concentration, Ri concentration der of 1 / 4-9 / 10 of the reference concentration, the reference concentration or a high concentration, wherein 0.02 to 0.5 / L der Rukoto A method for preventing adhesion disorders of marine organisms in the transient seawater cooling water system.
前記基準濃度未満の低濃度が、前記基準濃度の1/3〜9/10の濃度である請求項1に記載の一過式海水冷却水系の海生生物の付着障害防止方法。 The method for preventing adhesion disorders of marine organisms in a transient seawater cooling water system according to claim 1, wherein a low concentration less than the reference concentration is a concentration of 1/3 to 9/10 of the reference concentration.
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