JPH0629163B2 - Underwater organism control agent and aquatic organism adherence prevention method - Google Patents

Underwater organism control agent and aquatic organism adherence prevention method

Info

Publication number
JPH0629163B2
JPH0629163B2 JP63103385A JP10338588A JPH0629163B2 JP H0629163 B2 JPH0629163 B2 JP H0629163B2 JP 63103385 A JP63103385 A JP 63103385A JP 10338588 A JP10338588 A JP 10338588A JP H0629163 B2 JPH0629163 B2 JP H0629163B2
Authority
JP
Japan
Prior art keywords
chlorine dioxide
organism
control agent
seawater
prevention method
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
JP63103385A
Other languages
Japanese (ja)
Other versions
JPH01275504A (en
Inventor
耕三 藤野
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kurita Water Industries Ltd
Original Assignee
Kurita Water Industries Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP63103385A priority Critical patent/JPH0629163B2/en
Publication of JPH01275504A publication Critical patent/JPH01275504A/en
Publication of JPH0629163B2 publication Critical patent/JPH0629163B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、海水などの水中生物の付着防止に関する。TECHNICAL FIELD The present invention relates to prevention of adhesion of aquatic organisms such as seawater.

〔従来の技術〕[Conventional technology]

海水を一過式冷却水として多量に使用する火力発電所、
製鉄所、石油化学工業等では、これら冷却水系の流路や
熱交換器に、フジツボ、ムラサキイガイ、コケムシヒド
ロ虫類等の海水生物が付着し、配管などの閉塞、海水採
水量の低下、冷却効率の低下等の機能低下、更には装置
の破損など種々の障害を招くことがある。
A thermal power plant that uses a large amount of seawater as transient cooling water,
At steel mills, petrochemical industries, etc., seawater organisms such as barnacles, mussels, bryozoa, and other insects adhere to the cooling water channels and heat exchangers, causing clogging of pipes, lowering of seawater sampling, and cooling efficiency. May cause functional deterioration such as deterioration of the device, and may cause various troubles such as damage of the device.

従来、これらの付着生物による障害を防止するために、
塩素、ホルマリン、有機スズ化合物、有機イオウ化合物
等が用いられてきたが、添加量と効果の問題および魚類
等に対する蓄積毒性、残留毒性等環境破壊の問題が懸念
される。
Conventionally, in order to prevent damage due to these attached organisms,
Chlorine, formalin, organic tin compounds, organic sulfur compounds, etc. have been used, but there are concerns about problems such as the amount and effect of addition, and environmental damage such as cumulative toxicity to fish and residual toxicity.

例えば、有機スズ化合物で広く用いられているTBTO
(トリブチルチンオキサイド)については毒性の問題で
の規制が行なわれ始めており、薬剤添加による効果は使
用可能量からは期待できない。
For example, TBTO widely used in organotin compounds
With regard to (tributyltin oxide), regulations have begun to be conducted on the problem of toxicity, and the effect of the addition of a drug cannot be expected from the usable amount.

また、現在一般的に使用されている有機イオウ化合物、
塩素についても効果的に劣り、毒性が懸念される等の問
題がある。
In addition, organic sulfur compounds commonly used today,
Chlorine is also inferior in terms of effectiveness, and there are problems such as concern about toxicity.

その一例として、有機イオウ化合物として広く用いられ
ているジメチルジチオカルバミン酸塩はフジツボに対し
て効果的に劣るし、次亜塩素酸ナトリウム等塩素系薬剤
では付着防止効果はあるが残留塩素規制を行なうと効果
上の問題が生じる。又、THM(トリハロメタン)の生
成も懸念される。
As an example, dimethyldithiocarbamate, which is widely used as an organic sulfur compound, is inferior to barnacles effectively, and chlorine-based agents such as sodium hypochlorite have an anti-adhesion effect, but when residual chlorine is regulated. Effectiveness issues arise. In addition, THM (trihalomethane) may be generated.

〔発明が解決しようとする課題〕[Problems to be Solved by the Invention]

本発明は、蓄積毒性、残留毒性等の環境破壊を生じない
水中付着生物防除剤並びに防除方法を提供することを目
的とするものである。
An object of the present invention is to provide an agent for controlling organisms adhering to water and a method for controlling it, which does not cause environmental damage such as cumulative toxicity and residual toxicity.

〔課題を解決するための手段〕[Means for Solving the Problems]

本発明は、二酸化塩素または二酸化塩素発生剤を有効成
分とすることを特徴とする水中付着生物防除剤並びに同
防除剤を用いた水中生物付着防止方法に関する。
The present invention relates to an agent for controlling aquatic organisms that adheres to water, which comprises chlorine dioxide or a chlorine dioxide generator as an active ingredient, and a method for preventing the attachment of aquatic organisms using the agent.

このように、本発明は塩素のかわりに塩素の2.6倍の有
効塩素量を有し、水溶性の高い二酸化塩素または二酸化
塩素発生剤を用いることにより、薬品使用量の減少をは
かり、ひいては、毒性のあるTHM(トリハロメタン)
の生成を防止しつつ、海洋中などの水中における生物付
着を防止することで成功したものである。
As described above, the present invention has an effective chlorine amount 2.6 times that of chlorine instead of chlorine, and by using a highly water-soluble chlorine dioxide or a chlorine dioxide generator, the amount of chemicals used is reduced and, in turn, toxicity is increased. THM (trihalomethane) with
It has succeeded in preventing biofouling in water such as the ocean while preventing the generation of

水に対する二酸化塩素の使用量は少くとも0.015ppm以
上、好ましくは1ppm以上である。
The amount of chlorine dioxide used relative to water is at least 0.015 ppm or more, preferably 1 ppm or more.

本発明の防除剤は、イ)二酸化塩素それ自体、ロ)二酸
化塩素発生性化合物又は組成物、ハ)前記イ)又はロ)
を適当な担体に担持させたもの、の三つに分類すること
ができる。
The control agent of the present invention comprises a) chlorine dioxide itself, b) a chlorine dioxide-generating compound or composition, and c) the above a) or b).
Can be supported on a suitable carrier and can be classified into three types.

二酸化塩素発生性化合物の例としては 亜塩素酸アルカリ金属塩とくに亜塩素酸ナトリウムを挙
げることができる。亜塩素酸ナトリウムとしての使用量
は少くとも0.025ppm好ましくは2ppm以上である。亜塩
素酸ナトリウムはつぎの種々の化合物を反応させること
により、二酸化塩素を発生する。
Examples of the chlorine dioxide-generating compound include alkali metal chlorite, particularly sodium chlorite. The amount used as sodium chlorite is at least 0.025 ppm, preferably 2 ppm or more. Sodium chlorite generates chlorine dioxide by reacting the following various compounds.

(i)強酸の添加による場合 4NaClO2+H2SO4→2ClO2+Na2SO4+NaClO3+NaCl+H2O 5NaClO2+2H2SO4→4ClO2+2Na2SO4+NaCl+2H2O (Cl-存在時) (ii)次亜塩素酸の添加による場合 2NaClO2+NaClO+H2O→2ClO2+NaCl+2NaOH (iii)被酸化物の添加による場合 (例)5NaClO2+4CH3COOH→4ClO2+4CH3COONa+NaCl+2H2O 5NaClO2+4RCOOR′+2H2O→4ClO2+4RCOONa+4R′OH R,R′は例えばアルキル、フェニルなどである。(i) By adding strong acid 4NaClO 2 + H 2 SO 4 → 2ClO 2 + Na 2 SO 4 + NaClO 3 + NaCl + H 2 O 5NaClO 2 + 2H 2 SO 4 → 4ClO 2 + 2Na 2 SO 4 + NaCl + 2H 2 O (when Cl − is present) (ii) By adding hypochlorous acid 2NaClO 2 + NaClO + H 2 O → 2ClO 2 + NaCl + 2NaOH (iii) By adding an oxide (Example) 5NaClO 2 + 4CH 3 COOH → 4ClO 2 + 4CH 3 COONa + NaCl + 2H 2 O 5NaClO 2 + 4RCOOR ′ + 2H 2 O → 4ClO 2 + 4RCOONa + 4R′OH R, R ′ is, for example, alkyl or phenyl.

(iv)還元剤の添加による場合 (例)NaClO2+2NaHSO3→NaCl+2NaHSO4 NaClO2+2Na2SO3→NaCl+2Na2SO4 これらの混合方法に制限はないが、水中に添加された
後、反応成分ができるだけ早く接触するようにするのが
好ましい。又、添加順序としては亜塩素酸ナトリウムを
先に添加し、つづいて10m以内の個所に添加成分を加え
るのが好ましい。
(iv) In the case of adding reducing agent (Example) NaClO 2 + 2NaHSO 3 → NaCl + 2NaHSO 4 NaClO 2 + 2Na 2 SO 3 → NaCl + 2Na 2 SO 4 After that, it is preferred that the reaction components come into contact as soon as possible. In addition, the order of addition is preferably such that sodium chlorite is added first, and then the additive component is added at a position within 10 m.

本発明の前記組成物として、過炭酸塩たとえば過炭酸ソ
ーダで安定化された二酸化塩素水溶液を挙げることがで
きる。この水溶液は酸性にすると二酸化塩素が遊離す
る。
The composition of the present invention may include an aqueous solution of chlorine dioxide stabilized with a percarbonate, such as sodium percarbonate. When this aqueous solution is made acidic, chlorine dioxide is liberated.

前記担体としては、ゼオライト、ケイソウ、土軽石、ア
ルミナ活性炭、シリカゲル、モンモリロナイトなどをあ
げることができる。また、ゼラチン、寒天、PVA、な
どを二酸化塩素や二酸化塩素発生性化合物の水溶液でゲ
ル化した組成物として使用することもできる。
Examples of the carrier include zeolite, diatomaceous earth, pumice stone, alumina activated carbon, silica gel, montmorillonite and the like. It is also possible to use gelatin, agar, PVA, etc. as a composition gelled with an aqueous solution of chlorine dioxide or a chlorine dioxide-generating compound.

二酸化塩素の有効塩素発生過程は第1段階が酸化反応で
あって、瞬間的に反応してClO2 -になるものと考えら
れ、ついでClO2 -の酸化反応がおきるものと考えられ
る。
It is considered that the first stage of the effective chlorine generation process of chlorine dioxide is an oxidation reaction, and it is considered that ClO 2 is instantaneously reacted and then ClO 2 is oxidized.

つぎに本発明の防除剤の有効性をたしかめるため、下記
の試験を行った。
Next, the following tests were conducted in order to confirm the effectiveness of the control agent of the present invention.

〔試験方法〕〔Test method〕

海水汚損生物中で動物性生物の主体となるフジツボと比
較的生物活性に相関性があるとされるアルテミア幼生を
用いて試験を行った(アルテミアスケール法)。
The test was performed using Artemia larvae, which are said to have a relatively high correlation with biological activity in barnacles, which are the main animal species in seawater fouling organisms (Artemia scale method).

試験に用いたアルテミア幼生は、通常市販されているブ
ラインシュリンプの乾燥卵を28℃の恒温槽で人工海水を
用いて浮化させる。浮化して1日後浮化した幼生のみを
別容器に分離し、更に1日飼育した幼生のみを用いて試
験した(同時期に浮化した幼生を1〜2日間別に飼育し
た内元気に泳ぎ回っている幼生を用いないと誤差が大き
くなる。)。
The Artemia reared larvae used in the test are floated with commercially available brine shrimp dried eggs in a 28 ° C thermostat with artificial seawater. Only one day after levitation, only the larvae that floated were separated into separate containers, and further tested using only the larvae that had been bred for one day. If you do not use the larvae, the error will increase.

200mビーカーに評価薬剤が所定濃度になるように100m
調整し、その中に約50体のアルテミア幼生を入れて、
経過時間とともにその状態を観察し抑制率および致死率
を求めた。抑制率は衰弱および死亡した総数の割合で示
し、致死率はまさに死亡した割合を示す。アルテミアは
一般的に死亡した場合、底部に沈降し、体が細くなり、
わずかに色が白っぽくなる。その変化がハッキリしない
ものは細いガラス棒で刺激し動かなければ死亡したもの
とみなした。また、最後の24時間後にハッキリしないも
ののみ取り出し顕微鏡にて生死の確認を行なった。
100m in a 200m beaker so that the evaluation chemicals have a specified concentration
Adjust and put about 50 Artemia larvae in it,
The state was observed with the passage of time and the inhibition rate and lethality rate were calculated. Suppression rate is expressed as a percentage of the total number of deaths and deaths, and lethality rate is the exact rate of deaths. If Artemia generally dies, it will settle to the bottom, slimming,
The color becomes slightly whitish. If the change was not obvious, it was considered to have died unless stimulated with a thin glass rod and moved. In addition, after the last 24 hours, only those that were not clearly visible were taken out and checked for life or death with a microscope.

結果を表1に示す。The results are shown in Table 1.

〔実施例1〕 第1図のようなモデル水路を用い各薬剤の評価を行なっ
た。海水はモデル水路1に水中ポンプ2で供給する。3
は薬剤タンクであり、貯留された薬剤はケミカルポンプ
でモデル水路1に所定量供給される。尚4は分岐ヘッダ
ーである。
Example 1 Each drug was evaluated using a model water channel as shown in FIG. Seawater is supplied to the model waterway 1 by an underwater pump 2. Three
Is a medicine tank, and a predetermined amount of the stored medicine is supplied to the model waterway 1 by a chemical pump. Incidentally, 4 is a branch header.

このモデル水路の出口側近くに10×20cmの塩ビ製の付着
板を浸漬し、海水を約0.3m/secで一過式に通水し各薬剤
を所定量ケミカルポンプで注入し90日経過後の海水生物
の付着量を調べた。付着量については1m2当たりの個数
に換算した結果を表2に示す。
Immerse a 10 × 20 cm vinyl-made adhering plate near the outlet side of this model waterway, pass seawater transiently at about 0.3 m / sec and inject each chemical with a predetermined amount of chemical pump and after 90 days have elapsed The amount of marine organisms attached was investigated. Table 2 shows the results of conversion of the adhered amount into the number per 1 m 2 .

以上の結果より海水生物付着防止効果について亜塩素酸
ナトリウム単独でも従来処理程度の効果を示すが、亜塩
素酸ナトリウムを活性化し二酸化塩素にすることで著し
い効果をあげることができる。
From the above results, with regard to the effect of preventing the adhesion of organisms in seawater, sodium chlorite alone shows the effect of the conventional treatment, but by activating sodium chlorite to chlorine dioxide, a remarkable effect can be obtained.

実施例2 モデル水路の末端に滞留時間30分の滞留槽を設け、その
前後に付着板を浸漬し、薬剤は亜塩素酸ナトリウムと次
亜塩素酸ナトリウムとを併用した以外は、実施例1と同
様に付着試験を行った。その結果を表3に示す。
Example 2 Except that a retention tank was provided at the end of the model water channel for a retention time of 30 minutes, an adhering plate was immersed before and after that, and sodium chlorite and sodium hypochlorite were used in combination as the chemical agent. An adhesion test was conducted in the same manner. The results are shown in Table 3.

〔効果〕 (1)有効塩素発生剤である次亜塩素酸ナトリウムと比較
し少量で効果がある。
[Effect] (1) Compared with sodium hypochlorite, which is an effective chlorine generator, it is effective in a small amount.

更にトリハロメタンの発生がなく、環境汚染がない。Furthermore, there is no generation of trihalomethane and no environmental pollution.

(2)反応生成物は海水中に存在するイオンのみで構成さ
れ、残留、蓄積毒性がない。
(2) The reaction product is composed of only the ions present in seawater and has no residual or cumulative toxicity.

【図面の簡単な説明】[Brief description of drawings]

第1図は本発明の一実施例を説明するためのものであ
る。
FIG. 1 is for explaining one embodiment of the present invention.

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】海水の一過式冷却水系の水中に添加する二
酸化塩素または二酸化塩素発生剤を有効成分とすること
を特徴とする水中付着生物防除剤。
1. An agent for controlling aquatic organisms that adheres to water, which comprises chlorine dioxide or a chlorine dioxide generator added to the water of a transient cooling water system of seawater as an active ingredient.
【請求項2】亜塩素酸ナトリウムと次亜塩素酸ナトリウ
ムを海水の一過式冷却水中に加えることを特徴とする水
中生物付着防止方法。
2. A method for preventing adherence of aquatic organisms, which comprises adding sodium chlorite and sodium hypochlorite to the transient cooling water of seawater.
JP63103385A 1988-04-26 1988-04-26 Underwater organism control agent and aquatic organism adherence prevention method Expired - Lifetime JPH0629163B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP63103385A JPH0629163B2 (en) 1988-04-26 1988-04-26 Underwater organism control agent and aquatic organism adherence prevention method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63103385A JPH0629163B2 (en) 1988-04-26 1988-04-26 Underwater organism control agent and aquatic organism adherence prevention method

Publications (2)

Publication Number Publication Date
JPH01275504A JPH01275504A (en) 1989-11-06
JPH0629163B2 true JPH0629163B2 (en) 1994-04-20

Family

ID=14352611

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JPH0629163B2 (en)

Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2552998B2 (en) * 1992-12-22 1996-11-13 株式会社荏原製作所 Purification treatment sludge separation water treatment method and device
JP4856811B2 (en) * 2001-02-26 2012-01-18 三菱瓦斯化学株式会社 Oberias adhesion control method
JP5802058B2 (en) * 2011-06-03 2015-10-28 稔 豊島 Marine organism adhesion prevention paint
WO2014083624A1 (en) * 2012-11-28 2014-06-05 旭化成イーマテリアルズ株式会社 Coating material for preventing adhesion of marine organisms, and additive for said coating material
JP6944154B2 (en) * 2017-02-02 2021-10-06 株式会社片山化学工業研究所 Adhesion prevention method for marine organisms and adhesion prevention agent used for it
CN112153900B (en) * 2018-04-03 2022-09-13 本部三庆株式会社 Method for producing novel oxychloride composition from deteriorated hypochlorite
JP6843329B2 (en) * 2019-02-25 2021-03-17 株式会社片山化学工業研究所 How to prevent adhesion damage of marine organisms in seawater cooling water system

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS54140718A (en) * 1978-04-20 1979-11-01 Arigaa Howaado Sterilizing method and composition
JPS60184002A (en) * 1984-03-01 1985-09-19 Daiichi Seimo Kk Agent for controlling fungus of red rot disease or green laver

Also Published As

Publication number Publication date
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