JPS6316197B2 - - Google Patents
Info
- Publication number
- JPS6316197B2 JPS6316197B2 JP46380A JP46380A JPS6316197B2 JP S6316197 B2 JPS6316197 B2 JP S6316197B2 JP 46380 A JP46380 A JP 46380A JP 46380 A JP46380 A JP 46380A JP S6316197 B2 JPS6316197 B2 JP S6316197B2
- Authority
- JP
- Japan
- Prior art keywords
- water
- hydrogen peroxide
- slime
- drug
- seawater
- 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
Links
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims description 65
- 150000003839 salts Chemical class 0.000 claims description 17
- 125000004435 hydrogen atom Chemical group [H]* 0.000 claims description 4
- 125000002947 alkylene group Chemical group 0.000 claims description 3
- 125000004432 carbon atom Chemical group C* 0.000 claims description 3
- 239000004480 active ingredient Substances 0.000 claims description 2
- 125000001183 hydrocarbyl group Chemical group 0.000 claims 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 40
- 229940079593 drug Drugs 0.000 description 26
- 239000003814 drug Substances 0.000 description 26
- 230000000694 effects Effects 0.000 description 18
- 239000013535 sea water Substances 0.000 description 17
- 229920002413 Polyhexanide Polymers 0.000 description 16
- 238000012360 testing method Methods 0.000 description 14
- 239000003795 chemical substances by application Substances 0.000 description 11
- 230000002195 synergetic effect Effects 0.000 description 11
- XNCOSPRUTUOJCJ-UHFFFAOYSA-N Biguanide Chemical compound NC(N)=NC(N)=N XNCOSPRUTUOJCJ-UHFFFAOYSA-N 0.000 description 10
- 229940123208 Biguanide Drugs 0.000 description 10
- 229920000642 polymer Polymers 0.000 description 10
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 7
- 239000000460 chlorine Substances 0.000 description 7
- 229910052801 chlorine Inorganic materials 0.000 description 7
- 238000001816 cooling Methods 0.000 description 7
- 230000006698 induction Effects 0.000 description 6
- 244000005700 microbiome Species 0.000 description 6
- VAZJLPXFVQHDFB-UHFFFAOYSA-N 1-(diaminomethylidene)-2-hexylguanidine Polymers CCCCCCN=C(N)N=C(N)N VAZJLPXFVQHDFB-UHFFFAOYSA-N 0.000 description 5
- 241000238586 Cirripedia Species 0.000 description 5
- 241000196324 Embryophyta Species 0.000 description 5
- 241000237536 Mytilus edulis Species 0.000 description 5
- 239000007864 aqueous solution Substances 0.000 description 5
- 235000020638 mussel Nutrition 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- 230000000996 additive effect Effects 0.000 description 4
- 239000008235 industrial water Substances 0.000 description 4
- 230000001418 larval effect Effects 0.000 description 4
- 238000000034 method Methods 0.000 description 4
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 description 3
- 241001195836 Cypris Species 0.000 description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 3
- 230000006378 damage Effects 0.000 description 3
- 239000000645 desinfectant Substances 0.000 description 3
- 238000011161 development Methods 0.000 description 3
- 230000002262 irrigation Effects 0.000 description 3
- 238000003973 irrigation Methods 0.000 description 3
- 150000002978 peroxides Chemical class 0.000 description 3
- 241000894006 Bacteria Species 0.000 description 2
- 241001474374 Blennius Species 0.000 description 2
- KZBUYRJDOAKODT-UHFFFAOYSA-N Chlorine Chemical compound ClCl KZBUYRJDOAKODT-UHFFFAOYSA-N 0.000 description 2
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 2
- OAKJQQAXSVQMHS-UHFFFAOYSA-N Hydrazine Chemical compound NN OAKJQQAXSVQMHS-UHFFFAOYSA-N 0.000 description 2
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 2
- 239000005708 Sodium hypochlorite Substances 0.000 description 2
- 229910000831 Steel Inorganic materials 0.000 description 2
- OUUQCZGPVNCOIJ-UHFFFAOYSA-M Superoxide Chemical class [O-][O] OUUQCZGPVNCOIJ-UHFFFAOYSA-M 0.000 description 2
- 230000001464 adherent effect Effects 0.000 description 2
- 229910052783 alkali metal Inorganic materials 0.000 description 2
- 150000001340 alkali metals Chemical class 0.000 description 2
- 230000000052 comparative effect Effects 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 239000000498 cooling water Substances 0.000 description 2
- 229910001882 dioxygen Inorganic materials 0.000 description 2
- 239000007789 gas Substances 0.000 description 2
- 150000002430 hydrocarbons Chemical group 0.000 description 2
- 239000003621 irrigation water Substances 0.000 description 2
- 231100000053 low toxicity Toxicity 0.000 description 2
- 235000013372 meat Nutrition 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 150000003242 quaternary ammonium salts Chemical class 0.000 description 2
- 235000015170 shellfish Nutrition 0.000 description 2
- SUKJFIGYRHOWBL-UHFFFAOYSA-N sodium hypochlorite Chemical compound [Na+].Cl[O-] SUKJFIGYRHOWBL-UHFFFAOYSA-N 0.000 description 2
- 239000010959 steel Substances 0.000 description 2
- 150000003606 tin compounds Chemical class 0.000 description 2
- 231100000419 toxicity Toxicity 0.000 description 2
- 230000001988 toxicity Effects 0.000 description 2
- 238000012546 transfer Methods 0.000 description 2
- GSFSVEDCYBDIGW-UHFFFAOYSA-N 2-(1,3-benzothiazol-2-yl)-6-chlorophenol Chemical compound OC1=C(Cl)C=CC=C1C1=NC2=CC=CC=C2S1 GSFSVEDCYBDIGW-UHFFFAOYSA-N 0.000 description 1
- 241000251468 Actinopterygii Species 0.000 description 1
- -1 As described above Chemical class 0.000 description 1
- 206010003497 Asphyxia Diseases 0.000 description 1
- 241000206761 Bacillariophyta Species 0.000 description 1
- 241000700670 Bryozoa Species 0.000 description 1
- 241000195493 Cryptophyta Species 0.000 description 1
- 241000258937 Hemiptera Species 0.000 description 1
- 241000282412 Homo Species 0.000 description 1
- 241001465754 Metazoa Species 0.000 description 1
- 241000133262 Nauplius Species 0.000 description 1
- 239000001888 Peptone Substances 0.000 description 1
- 108010080698 Peptones Proteins 0.000 description 1
- 241000206607 Porphyra umbilicalis Species 0.000 description 1
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 1
- 208000027418 Wounds and injury Diseases 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 239000000853 adhesive Substances 0.000 description 1
- 230000001070 adhesive effect Effects 0.000 description 1
- 229910052784 alkaline earth metal Inorganic materials 0.000 description 1
- 150000001342 alkaline earth metals Chemical class 0.000 description 1
- 239000003242 anti bacterial agent Substances 0.000 description 1
- 230000001580 bacterial effect Effects 0.000 description 1
- 150000001642 boronic acid derivatives Chemical class 0.000 description 1
- 239000004202 carbamide Substances 0.000 description 1
- 150000004649 carbonic acid derivatives Chemical class 0.000 description 1
- 231100000481 chemical toxicant Toxicity 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000001186 cumulative effect Effects 0.000 description 1
- 239000001177 diphosphate Substances 0.000 description 1
- XPPKVPWEQAFLFU-UHFFFAOYSA-J diphosphate(4-) Chemical class [O-]P([O-])(=O)OP([O-])([O-])=O XPPKVPWEQAFLFU-UHFFFAOYSA-J 0.000 description 1
- 235000011180 diphosphates Nutrition 0.000 description 1
- 238000001647 drug administration Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000003203 everyday effect Effects 0.000 description 1
- 238000005187 foaming Methods 0.000 description 1
- 235000011389 fruit/vegetable juice Nutrition 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 150000004679 hydroxides Chemical class 0.000 description 1
- 230000000977 initiatory effect Effects 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 208000014674 injury Diseases 0.000 description 1
- 238000011081 inoculation Methods 0.000 description 1
- 150000002484 inorganic compounds Chemical class 0.000 description 1
- 229910010272 inorganic material Inorganic materials 0.000 description 1
- 230000007794 irritation Effects 0.000 description 1
- 230000000366 juvenile effect Effects 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 239000007769 metal material Substances 0.000 description 1
- 150000004972 metal peroxides Chemical class 0.000 description 1
- 125000001570 methylene group Chemical group [H]C([H])([*:1])[*:2] 0.000 description 1
- 150000004712 monophosphates Chemical class 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 150000002825 nitriles Chemical class 0.000 description 1
- 230000003287 optical effect Effects 0.000 description 1
- 150000002894 organic compounds Chemical class 0.000 description 1
- 150000002898 organic sulfur compounds Chemical class 0.000 description 1
- 235000019319 peptone Nutrition 0.000 description 1
- 239000002574 poison Substances 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 231100000572 poisoning Toxicity 0.000 description 1
- 230000000607 poisoning effect Effects 0.000 description 1
- 230000035755 proliferation Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 230000009528 severe injury Effects 0.000 description 1
- 230000035939 shock Effects 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 230000000638 stimulation Effects 0.000 description 1
- 239000008399 tap water Substances 0.000 description 1
- 235000020679 tap water Nutrition 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 239000003440 toxic substance Substances 0.000 description 1
- DBGVGMSCBYYSLD-UHFFFAOYSA-N tributylstannane Chemical compound CCCC[SnH](CCCC)CCCC DBGVGMSCBYYSLD-UHFFFAOYSA-N 0.000 description 1
- NSPWVJAKNXJHEP-UHFFFAOYSA-N tripropyltin Chemical compound CCC[Sn](CCC)CCC NSPWVJAKNXJHEP-UHFFFAOYSA-N 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Landscapes
- Preventing Corrosion Or Incrustation Of Metals (AREA)
Description
本発明は用水系付着物の防除剤、とくに冷却水
系などの用水系において主に微生物に由来するス
ライムや海水を利用している流路、プラント等に
おける海水生物の増殖や付着を防除する薬剤に関
するものである。
近年、化学工業、石油化学工業及びその他の諸
工業の発展に伴い多量の工業用水が必要となつて
いる。工業用水の水源として工業用水道水の他に
海水、湖沼水、河川水及び地下水などが使用され
ている。これら工業用水中には必ず各種の微生物
が存在しており、この微生物類の中にはその存在
する水質、環境によつてはさらに増殖を続け各種
の障害を起こす原因となるものが多い、たとえ
ば、冷却用水として使用する場合に、水中に生息
している微生物が増殖し用水設備の壁などに着生
してスライムを形成し、これによる熱交換率の低
下及び流水不良などの障害が発生する。殊に、用
水の循環使用において開放型冷却塔などを用いた
開放式の場合には、系の一部で循環水が強制ばつ
気されて空気に接触し、かつ太陽光線が照射され
ることにより細菌及び藻類などの好気性微生物類
の繁殖が助長される。
これら用水系内に生育、増殖した微生物類に由
来するスライム障害を防止するためには、従来、
塩素もしくは塩素系有機化合物、塩素系無機化合
物、第四級アンモニウム塩、シアン化合物などの
殺菌剤および/または抗菌剤がそれぞれ用いられ
てきた。しかしながら、これらの薬剤は一般には
排水公害における公害源であり、現実に使用不可
能なもの、あるいは人畜または魚類などの生物に
対する毒性が大きく、また装置材質に対する腐食
性が大きいなどのために実用化困難なものが多く
無公害薬剤の開発が望まれている。
そこで、本発明者等はこのような薬剤として過
酸化水素に着目した。過酸化水素はそれ自体毒性
が低く、しかも分解して水と酸素ガスになる全く
の無公害薬剤であるという特長を有する。しかし
ながら、過酸化水素は特開昭51−94001号公報に
記載されたように0.5〜200ppm程度の低濃度でス
ライムの付着を防止することができるが、易分解
性であるため、実際の使用にあたつては、一定時
間有効濃度を維持するには分解された過酸化水素
相当量を補う必要がありその結果としてかなり大
量の過酸化水素を要する欠点がある。
また、近年、海水の工業的な利用も著しく増加
しており、例えば火力発電所、製鉄所、石油化学
工業などで一過式に多量に用いられている。さら
に、船舶ではボイラーの復水器の冷却に利用され
ている。ところが、このような海水の利用に際し
て、海水中に生息する種々の生物、例えば、ムラ
サキイガイ、フジツボ、ヒドロムシ、コケムシな
どの動物やアオノリなどの海藻類による付着障害
は無視できないものがある。特に著しい障害をひ
き起こす生物としては、ムラサキイガイとフジツ
ボがあげられる。
これらの海水生物が水路に多数付着して成長す
ると水路を狭めてしまい、また、それらが脱落し
て復水器や熱交換器に流入すると冷却効果を低下
させ、さらに、コンデンサーチユーブに詰まると
海水の乱流を起こし機械的に金属の腐食を促進さ
せる。
このような障害を防止するために、通常、薬剤
を注入する方法がとられる。従来用いられてきた
代表的な薬剤として液体塩素、次亜塩素酸ソーダ
のような有効塩素発生剤、トリ−n−プロピル
錫、トリ−n−ブチル錫、トリ−n−フエニル錫
の塩化物、酸化物、水酸化物のような有機錫化合
物があげられるが、これらの薬剤は残留毒性、蓄
積毒性があり、広く海水生物の生態環境を破壊す
るものとされている。そればかりでなく、有効塩
素発生剤の場合には、臭気、金属材質への腐食
性、泡立ち等の問題がある。さらにその上、液体
塩素の場合には輸送時の危険性、注入時の作業安
定性なども問題とされている。また、有機錫化合
物の場合も特有の刺激臭を有し、皮膚に触れると
炎症を起こし易い、ヒドロムシや海藻のような殻
を有しないソフト型汚染生物に対する効果が弱い
等の問題がある。
従つて、これらの有毒薬剤を使用せず、定期的
に人力によつて流路、プラント等への付着物を除
去することもしばしば行われるがそのためには莫
大な費用を要し、かつ付着生物の死滅などにより
腐敗性ガスの発生をみ、暗きよ等に充満するた
め、中毒による人身事故を招くこともまれではな
い。
そこで、従来の薬剤に替る安全な新しい薬剤の
開発が要望されているが、本発明者等は、このよ
うな薬剤として過酸化水素に着目した。
前述のごとく、過酸化水素はそれ自体毒性が低
く、しかも分解して水と酸素ガスになるので、残
留毒や蓄積毒などによる環境問題を起こす心配は
全くないという特長を有する。しかしながら、過
酸化水素は、それ自体でも海水生物の付着防除に
有効ではあるものの満足な付着防除効果を得るに
は比較的多量を要し、高価にすぎるという欠点が
ある。
そこで本発明者等は過酸化水素と組合せて、有
効かつ相乗的な効果をもたらす薬剤について鋭意
研究した。その結果、多くの場合には相加効果な
いしは、わずかな相乗効果した認められなかつた
のに対して、極めて著しい相乗効果を有する組合
せを見出し、本発明に到達した。
すなわち、本発明は、過酸化水素と、一般式
(式中、Rは水素原子又は炭化水素基を示し、X
及びYはそれぞれ炭素数3〜12個のアルキレン基
を示す。)の繰り返し単位からなるビグアニド重
合物、もしくはその水溶性塩とを有効成分として
含有することを特徴とする用水系付着物の防除剤
である。
本発明に用いる過酸化水素とは、過酸化水素の
種々の濃度の水溶液のほかに水や海水の存在下に
過酸化水素を発生する物質も使用できる。このよ
うな化合物としては、例えば炭酸塩、ほう酸塩、
一リン酸塩、二リン酸塩、メタケイ酸塩および尿
素などのそれぞれの過酸化水素付加物類、金属過
酸化物、例えばアルカリ金属の過酸化物およびア
ルカリ土類金属の過酸化物などの金属過酸化物
類、例えばアルカリ金属の超酸化物などの金属超
酸化物類ならびにこれらの組成物および混合物な
どが挙げられる。
また、本発明に用いるビグアニド重合物は、一
般式
の繰り返し単位からなり、式中、Rは水素原子又
は炭化水素基、好ましくは水素原子を示し、X及
びYはそれぞれ炭素数3〜12個のアルキレン基、
好ましくはメチレン基を示す。これらの水溶性塩
としては、水溶性のものであれば特に制限はない
が、一般に、塩酸、酢酸などの酸による中性塩と
するのが好ましい。さらに、分子量が900〜1200
のポリヘキサメチレンビグアニド塩酸塩は市販さ
れていて入手しやすい点から特に好ましい。
なお、ビグアニド重合物もしくはその水溶性塩
は、従来より工業用の無害性殺菌・消毒剤として
知られているが、海水中に生息する付着性生成物
に対する作用効果について解明されたものはまだ
見当らず、ましてや過酸化水素の併用下における
作用効果については本発明者等によつて初めて明
らかになつたことである。
例えばムラサキガイの場合は、トロコホア、D
状仔貝、アンボ期の幼生過程を経て稚貝から成貝
に、また、フジツボの場合は、ノープリウス、シ
プリスの幼生過程を経て、成体にそれぞれ変態す
るが、一般に、付着はこれら幼生の段階で起こる
とされている。
過酸化水素とビグアニド重合物もしくはその水
溶性塩を組合せた場合、それぞれの薬剤単独では
殆ど効果を有しないような濃度で上記幼生の活動
を停止させ仮死状態に至らしめるか、付着しても
その後の成長を阻止してしまう。
本発明において、過酸化水素とビグアニド重合
物もしくはその水溶性塩は、その必要量を用水系
に添加するものであるが、添加の方法は両薬剤を
予め混合調整して添加してもよいし、両薬剤を別
個に添加してもよい。別個に添加する場合、添加
順序等に特に制限はないが最初に添加された薬剤
が用水中に残存している間に次の薬剤の添加が開
始されるのが好ましい。
過酸化水素およびビグアニド重合物もしくはそ
の水溶性塩をスライム防除に用いる場合の使用量
は水系のスライムの種類や発生状況などにより異
なるが、一般的には水系中における濃度が過酸化
水素は0.05〜100ppm、好ましくは0.1〜50ppmと
なる量であり、ビグアニド重合物もしくはその水
溶性塩は0.01〜20ppm、好ましくは0.5〜10ppm
となる量である。薬剤の使用量が上記の範囲の下
限より低い場合には十分なスライム防除効果が得
られず、また上限より高くすることもできるが余
剰分の薬剤が浪費されることになる。
また、過酸化水素およびビグアニド重合物もし
くはその水溶性塩を海水物の付着防除に用いる場
合の使用量は、海水系の汚染の程度、付着生物の
種類などによつて異なるが、一般には海水系での
濃度が過酸化水素は0.05〜50ppm、好ましくは
0.1〜10ppm、ビグアニド重合物もしくはその水
溶性塩は0.005〜5ppm、好ましくは0.01〜1ppm
となる量であり、1日0.5〜24時間添加すればよ
い。なお、過酸化水素が0.05〜1ppm、ビグアニ
ド重合物もしくはその水溶性塩が0.005〜0.1ppm
の組合せでは殆ど付着性幼生の活動を停止せしめ
る効果を有しないが、付着後の成長を著しく停止
せしめるため、実質上十分な付着防除効果が得ら
れる。
上記の処理は、反復するのが好ましいが、必ず
しも毎日行う必要はなく、例えば海水系の汚染の
少ない冬季などは2〜3日に1回としても差支え
ない。
過酸化水素およびビグアニド重合物もしくはそ
の水溶性塩は、それぞれ使用量の全量を一挙に用
水に添加してもよく(以下、衝撃投与と記す)、
また前記の濃度となるような量を徐々に連続的に
添加(以下、連続投与と記す)してもよい。衝撃
投与は用水が循環使用されている場合に適し、ま
た連続投与は用水が用水系に循環使用されず単通
している場合、もしくは循環使用されていても水
系内の滞留時間が比較的短い冷却水系の低濃縮運
転の場合に好適である。
用水が用水系を単通する場合に連続投与するに
は用水が用水系に供給される前か、用水系を通過
中でなければならない。連続投与する場合には、
薬剤を添加する時間には特に制限はないが、一般
には0.5〜24時間であり、好ましくは6〜12時間
である。
前記の処理は、一回限りでもよいが反覆して行
うことが好ましい。反覆して行う場合には、反復
回数および各回の間隔などはスライムの種類や発
生状況などにより適宜決定しうる。各処理間の間
隔はたとえば夏季では2〜5日に1回、冬期では
4〜10日に1回とするのが好適である。
なお、本発明の付着防除剤のほかに、この分野
における公知の薬剤、例えば塩素、次亜塩素酸ソ
ーダ等の有効塩素発生剤、ヒドラジン、有機錫化
合物、第4級アンモニウム塩、ジメチルジチオカ
ルバミン酸ソーダ等の有機イオウ化合物などを併
用してもさしつかえない。
以上述べたように本発明はきわめて経済的にか
つ効率よく用水系でのスライムの発生、付着を防
除することに成功したものであり、スライム障害
を排除し、しかも公害上の問題のない工業的価値
のきわめて高いものである。
実施例によつて本発明をさらに具体的に説明す
る。
実施例 1
肉汁液体培地(肉エキス 10g/、ペプトン
10g/、NaCl 5g/、PH7.2)10mlにス
ライム起源の未同定混成細菌群を一夜培養し、こ
れを前記と同様の培地(10ml)を含むモノ−管
(φ17mm)に107個/ml程度の菌濃度となるように
接種した。35℃にて振とう培養してOD(光学密
度)による増殖の経時変化をバイオフオトレコー
ダ(TN−112D・東洋科学産業製)にて自動記録
した。得られたチヤートより増殖開始時間を決定
し相乗効果を次の如くにして示した。
薬剤を与えない場合の誘導期間の長さ t0
薬剤()を単用した場合の誘導期間の長さ t1
薬剤()を単用した場合の誘導期間の長さ t2
薬剤()および薬剤()を併用した場合の誘
導期間の長さ t1,2
薬剤()を単用した事による遅延時間(薬剤の
投与によつて延長された誘導期間を意味し、以下
単独遅延時間と記す) Δt1=t1−t0
薬剤()を単用した事による単独遅延時間
Δt2=t2−t0
薬剤()および薬剤()を併用したことによ
る遅延時間(以下併用遅延時間と記す)
Δt1,2=t1,2−t0
以上の事から、単独遅延時間の和(Δt1+Δt2)
は相加遅延時間であり、これと併用遅延時間との
差〔Δt1,2−(Δt1+Δt2)=Δt※〕は相乗遅延時間
である(以下このように記す)。
故に相乗効果は
Δt1,2−(Δt1+Δt2)/(Δt1+Δt2)×100
=Δt※/(Δt1+Δt2)×100=α(%)
となり、このα(%)を相乗効率と称し、αの値
によつて相乗効果の有無および大きさを判定し
た。
すなわち、
α=0 のとき相加効果
α>0 のとき相乗効果、またαが大きいほど
相乗効果が大きいことになる。
α<0 のとき相加効果より低くマイナスの相
乗効果(相殺効果)である。
なお、本実施例ではポリヘキサメチレンビグア
ニドもしくはその水溶性塩として平均分子量1200
のポリヘキサメチレンビグアニド塩酸塩を用い
た。結果を第1表に示す。
The present invention relates to an agent for controlling fouling in water systems, and particularly to an agent for controlling the growth and adhesion of seawater organisms in channels, plants, etc. that utilize slime and seawater mainly derived from microorganisms in water systems such as cooling water systems. It is something. In recent years, with the development of the chemical industry, petrochemical industry, and other industries, large amounts of industrial water have become necessary. In addition to industrial tap water, seawater, lake water, river water, and groundwater are used as sources of industrial water. Various types of microorganisms are always present in these industrial waters, and depending on the water quality and environment in which they exist, many of these microorganisms can continue to proliferate and cause various problems, such as: When water is used for cooling, microorganisms living in the water proliferate and grow on the walls of water facilities, forming slime, which causes problems such as a decrease in heat exchange efficiency and poor water flow. . In particular, when circulating water is used in an open system using an open cooling tower, the circulating water is forcibly aerated in a part of the system and comes into contact with the air, and is exposed to sunlight. The growth of aerobic microorganisms such as bacteria and algae is encouraged. In order to prevent slime damage caused by microorganisms that have grown and multiplied in these irrigation water systems,
Disinfectants and/or antibacterial agents such as chlorine or chlorine-based organic compounds, chlorine-based inorganic compounds, quaternary ammonium salts, and cyanide compounds have been used, respectively. However, these agents are generally a source of pollution in wastewater pollution, and cannot be put into practical use because they are either unusable, highly toxic to living things such as humans, animals, or fish, or highly corrosive to equipment materials. Many of these are difficult, and the development of non-polluting drugs is desired. Therefore, the present inventors focused on hydrogen peroxide as such a drug. Hydrogen peroxide itself has the advantage of being a completely non-polluting agent that has low toxicity and decomposes into water and oxygen gas. However, hydrogen peroxide can prevent slime adhesion at a low concentration of about 0.5 to 200 ppm as described in JP-A No. 51-94001, but it is easily degradable, so it cannot be used in actual use. However, in order to maintain an effective concentration for a certain period of time, it is necessary to replace the equivalent amount of decomposed hydrogen peroxide, resulting in the disadvantage that a considerably large amount of hydrogen peroxide is required. In addition, in recent years, the industrial use of seawater has increased significantly, and large amounts of seawater are used in temporary quantities, for example, in thermal power plants, steel plants, petrochemical industries, and the like. Additionally, it is used to cool boiler condensers on ships. However, when using seawater in this way, adhesion problems caused by various organisms that live in seawater, such as mussels, barnacles, water bugs, bryozoans, and seaweed such as blue laver, cannot be ignored. Creatures that cause particularly severe damage include mussels and barnacles. When these seawater organisms grow and grow in large numbers in waterways, they narrow the waterways, and when they fall off and flow into condensers and heat exchangers, they reduce the cooling effect.Furthermore, when they clog condenser tubes, seawater This causes turbulent flow and mechanically accelerates metal corrosion. To prevent such damage, a method of injecting drugs is usually used. Typical agents conventionally used include liquid chlorine, effective chlorine generators such as sodium hypochlorite, tri-n-propyltin, tri-n-butyltin, tri-n-phenyltin chlorides, Examples include organic tin compounds such as oxides and hydroxides, but these agents have residual toxicity and cumulative toxicity, and are widely considered to destroy the ecological environment of seawater organisms. In addition, effective chlorine generating agents have problems such as odor, corrosiveness to metal materials, and foaming. Furthermore, in the case of liquid chlorine, there are also problems such as danger during transportation and work stability during injection. In addition, organic tin compounds also have problems, such as having a unique pungent odor, being likely to cause irritation if they come in contact with the skin, and being less effective against soft contaminants that do not have shells, such as water bugs and seaweed. Therefore, instead of using these toxic chemicals, it is often done manually to remove the deposits from flow channels, plants, etc., but this requires a huge amount of money and also increases the risk of deposits from deposits. As the gases die, putrefactive gases are generated and fill dark rooms, which often results in personal injury due to poisoning. Therefore, there is a demand for the development of a new, safe drug to replace conventional drugs, and the present inventors focused on hydrogen peroxide as such a drug. As mentioned above, hydrogen peroxide itself has low toxicity, and since it decomposes into water and oxygen gas, it has the advantage that there is no need to worry about causing environmental problems due to residual or accumulated poisons. However, although hydrogen peroxide itself is effective in preventing the adhesion of marine organisms, it has the disadvantage that a relatively large amount is required to obtain a satisfactory adhesion-controlling effect, and it is too expensive. Therefore, the inventors of the present invention have conducted extensive research into drugs that produce effective and synergistic effects when combined with hydrogen peroxide. As a result, while in many cases additive effects or slight synergistic effects were not observed, combinations with extremely significant synergistic effects were discovered and the present invention was achieved. That is, the present invention provides hydrogen peroxide and the general formula (In the formula, R represents a hydrogen atom or a hydrocarbon group, and
and Y each represents an alkylene group having 3 to 12 carbon atoms. ) or a water-soluble salt thereof as an active ingredient. As the hydrogen peroxide used in the present invention, in addition to aqueous solutions of hydrogen peroxide with various concentrations, substances that generate hydrogen peroxide in the presence of water or seawater can also be used. Such compounds include, for example, carbonates, borates,
respective hydrogen peroxide adducts such as monophosphates, diphosphates, metasilicates and urea; metal peroxides, such as peroxides of alkali metals and peroxides of alkaline earth metals; Peroxides include metal superoxides, such as superoxides of alkali metals, and compositions and mixtures thereof. Moreover, the biguanide polymer used in the present invention has the general formula In the formula, R represents a hydrogen atom or a hydrocarbon group, preferably a hydrogen atom, and X and Y each represent an alkylene group having 3 to 12 carbon atoms,
Preferably it represents a methylene group. These water-soluble salts are not particularly limited as long as they are water-soluble, but neutral salts with acids such as hydrochloric acid and acetic acid are generally preferred. In addition, the molecular weight is 900-1200
Polyhexamethylene biguanide hydrochloride is particularly preferred because it is commercially available and easily available. Although biguanide polymers or their water-soluble salts have been known as harmless industrial disinfectants and disinfectants, their effects on adhesive products living in seawater have not yet been elucidated. First of all, the effects of the combined use of hydrogen peroxide were clarified for the first time by the present inventors. For example, in the case of mussels, trochophore, D
The juvenile shellfish undergoes the larval stage of larval stage and the ambo stage, and then metamorphoses into the adult shellfish, and in the case of barnacles, it passes through the larval stage of nauplius and cypris, and then metamorphoses into the adult body, but in general, attachment occurs during these larval stages. It is said to occur in When hydrogen peroxide and biguanide polymers or their water-soluble salts are combined, the larvae either stop their activity and enter a state of asphyxia at concentrations that would have little effect on each drug alone, or even if they attach to the larvae, they do not survive. will inhibit the growth of In the present invention, hydrogen peroxide and a biguanide polymer or a water-soluble salt thereof are added to the water system in required amounts, but the method of addition may be such that both drugs are mixed and adjusted in advance. , both drugs may be added separately. When adding them separately, there is no particular restriction on the order of addition, etc., but it is preferable that the addition of the next drug is started while the first drug added remains in the water. When using hydrogen peroxide and biguanide polymers or their water-soluble salts for slime control, the amount used varies depending on the type of slime in the water system and the situation in which it occurs, but in general, the concentration of hydrogen peroxide in the water system is 0.05~ The amount is 100 ppm, preferably 0.1 to 50 ppm, and the biguanide polymer or its water-soluble salt is 0.01 to 20 ppm, preferably 0.5 to 10 ppm.
This is the amount. If the amount of the chemical used is lower than the lower limit of the above range, a sufficient slime control effect will not be obtained, and although it can be made higher than the upper limit, the excess amount of the chemical will be wasted. In addition, when using hydrogen peroxide and biguanide polymers or their water-soluble salts to prevent seawater deposits, the amount used varies depending on the degree of contamination of the seawater system, the type of adherent organisms, etc. The concentration of hydrogen peroxide is 0.05~50ppm, preferably
0.1-10ppm, biguanide polymer or its water-soluble salt 0.005-5ppm, preferably 0.01-1ppm
It can be added for 0.5 to 24 hours a day. In addition, hydrogen peroxide is 0.05 to 1 ppm, and biguanide polymer or its water-soluble salt is 0.005 to 0.1 ppm.
Although the combination has almost no effect on stopping the activity of adherent larvae, it significantly stops the growth after attachment, so a substantially sufficient adhesion control effect can be obtained. Although it is preferable to repeat the above treatment, it is not necessarily necessary to perform it every day; for example, in winter when the seawater system is less contaminated, it may be performed once every 2 to 3 days. The entire amount of hydrogen peroxide and biguanide polymer or water-soluble salt thereof may be added to the water at once (hereinafter referred to as impact administration),
Alternatively, an amount to achieve the above-mentioned concentration may be gradually and continuously added (hereinafter referred to as continuous administration). Shock dosing is suitable when the water is used in a cyclical manner, and continuous dosing is suitable for cases where the water is not recirculated but is passed through the water system in a single manner, or for cooling purposes where the residence time in the water system is relatively short even if the water is recirculated. Suitable for low concentration operation of aqueous systems. When water passes through the irrigation system, continuous administration requires that the water is either before being supplied to the irrigation system or while it is passing through the irrigation system. For continuous administration,
There is no particular restriction on the time for adding the drug, but it is generally 0.5 to 24 hours, preferably 6 to 12 hours. The above treatment may be carried out only once, but it is preferably carried out repeatedly. When performing the process repeatedly, the number of repetitions and the interval between each time can be determined as appropriate depending on the type of slime, the situation of occurrence, etc. The interval between each treatment is preferably once every 2 to 5 days in summer, and once every 4 to 10 days in winter. In addition to the adhesion control agent of the present invention, known agents in this field, such as chlorine, effective chlorine generators such as sodium hypochlorite, hydrazine, organotin compounds, quaternary ammonium salts, and sodium dimethyldithiocarbamate, may also be used. It is okay to use organic sulfur compounds such as As described above, the present invention has succeeded in controlling the generation and adhesion of slime in irrigation water systems extremely economically and efficiently, eliminates slime troubles, and is suitable for industrial use without any pollution problems. It is extremely valuable. The present invention will be explained in more detail with reference to Examples. Example 1 Meat juice liquid medium (meat extract 10g/, peptone
Unidentified mixed bacteria of slime origin were cultured overnight in 10ml (10g/, NaCl 5g/, PH7.2), and then transferred to a mono-tube (φ17mm) containing the same medium (10ml) as above at 10 7 cells/ml. The inoculation was carried out to achieve a bacterial concentration of about 100%. Culture was carried out with shaking at 35°C, and changes in growth over time in terms of OD (optical density) were automatically recorded using a biophoto recorder (TN-112D, manufactured by Toyo Kagaku Sangyo). The proliferation initiation time was determined from the obtained chart, and the synergistic effect was demonstrated as follows. Length of the induction period when no drug is given t 0 Length of the induction period when the drug () is used alone t 1 Length of the induction period when the drug () is used alone t 2 Length of the induction period when the drug () is used alone Length of induction period when () is used in combination t Delay time due to single use of 1,2 drug () (means the induction period extended by drug administration, hereinafter referred to as independent delay time) Δt 1 = t 1 − t 0 Single delay time due to single use of drug ()
Δt 2 = t 2 − t 0 Delay time due to combined use of drug () and drug () (hereinafter referred to as combination delay time)
Since Δt 1,2 = t 1,2 − t 0 or more, the sum of individual delay times (Δt 1 + Δt 2 )
is the additive delay time, and the difference between this and the combined delay time [Δt 1,2 −(Δt 1 +Δt 2 )=Δt*] is the synergistic delay time (hereinafter written as such). Therefore, the synergistic effect is Δt 1,2 - (Δt 1 + Δt 2 ) / (Δt 1 + Δt 2 ) × 100 = Δt* / (Δt 1 + Δt 2 ) × 100 = α (%), and this α (%) is The presence or absence of a synergistic effect and its magnitude were determined by the value of α, which is called efficiency. That is, when α=0, there is an additive effect; when α>0, there is a synergistic effect, and the larger α is, the greater the synergistic effect is. When α<0, it is a negative synergistic effect (offsetting effect), which is lower than the additive effect. In this example, polyhexamethylene biguanide or its water-soluble salt was used with an average molecular weight of 1200.
Polyhexamethylene biguanide hydrochloride was used. The results are shown in Table 1.
【表】【table】
【表】
第1表から明らかなように過酸化水素と平均分
子量1200のポリヘキサメチレンビグアニド塩酸塩
とから成る本発明のスライム防除剤を使用するこ
とにより77〜314%の相乗効率を得ることができ
た。
実施例 2
東京地区の某化学工場内に設置した循環式冷却
水系のモデルプラントにおいて本発明薬剤のスラ
イム防除効果を試験した。モデルプラントの仕様
は下記の如くである。
保有水量 () 940
循環水量 (/hr) 4100
補給水量 (/hr) 114
ブローダウン水量(/hr) 49
飛散水量 (/hr) 8
濃縮倍数 2
熱媒温度 (℃) 56
冷却塔戻水温度 (℃) 37〜38
冷却塔送水温度 (℃) 30
熱交換器管内流速(m/sec) 0.5
総伝熱面積 (m2) 0.707
補給水としては東京都城北工業用水に一部河川
水の混合されたものを使用した。また、スライム
の発生、付着を促進させるために試験開始時に同
一の補給水を使用している現場冷却塔から採取し
たズーグレアと珪藻を主成分とするスライム400
ml(30分後の沈降容積、乾燥重量約10g相当)を
投入した。
試験は1試験区について20日間ずつ実施し、薬
効の評価は熱交換器の総括伝熱係数(U)変化、
及び20日後の熱交換器チユーブ(SUS304)壁面
へのスライム付着量を測定することによつて行つ
た。
なお、この試験において、過酸化水素は35w/
w%水溶液を使用し、ポリヘキサメチレンビグア
ニドもしくはその水溶性塩は平均分子量900のポ
リヘキサメチレンビグアニド塩酸塩の20w/w%
水溶液を使用し両薬剤を予め混合後添加した。混
合割合は以下の如くである。
35w/w%過酸化水素 80部
20w/w%ポリヘキサメチレンビグアニド塩
酸塩 20部
結果を第2表に示す。[Table] As is clear from Table 1, a synergistic efficiency of 77 to 314% can be obtained by using the slime control agent of the present invention consisting of hydrogen peroxide and polyhexamethylene biguanide hydrochloride having an average molecular weight of 1200. did it. Example 2 The slime control effect of the agent of the present invention was tested in a model plant with a circulating cooling water system installed in a certain chemical factory in the Tokyo area. The specifications of the model plant are as follows. Amount of water held () 940 Amount of circulating water (/hr) 4100 Amount of make-up water (/hr) 114 Amount of blowdown water (/hr) 49 Amount of scattered water (/hr) 8 Concentration multiple 2 Heat medium temperature (℃) 56 Cooling tower return water temperature ( ℃) 37~38 Cooling tower water supply temperature (℃) 30 Flow velocity in heat exchanger pipes (m/sec) 0.5 Total heat transfer area (m 2 ) 0.707 As make-up water, some river water is mixed with Tokyo Johoku industrial water. I used something similar. In addition, in order to promote slime generation and adhesion, 400% of slime containing zooglaia and diatoms as main components was collected from the on-site cooling tower where the same make-up water was used at the start of the test.
ml (sedimentation volume after 30 minutes, equivalent to about 10 g of dry weight) was added. The test was conducted for 20 days in each test area, and the medicinal efficacy was evaluated based on the overall heat transfer coefficient (U) change of the heat exchanger,
After 20 days, the amount of slime adhering to the wall of the heat exchanger tube (SUS304) was measured. In addition, in this test, hydrogen peroxide was 35w/
Using w% aqueous solution, polyhexamethylene biguanide or its water-soluble salt is 20w/w% of polyhexamethylene biguanide hydrochloride having an average molecular weight of 900.
Both drugs were mixed in advance and added using an aqueous solution. The mixing ratio is as follows. 35w/w% hydrogen peroxide 80 parts 20w/w% polyhexamethylene biguanide hydrochloride 20 parts The results are shown in Table 2.
【表】
第2表からわかるように無処理区のU低下は
350kcal/m2・hr・℃であるのに対して、試験区
のそれはいずれも100kcal/m2・hr・℃以下であ
り、またスライム付着も試験区の無処理区に対す
る付着率は15〜23%まで低下し外観ではスライム
付着は認められず良好なスライムコントロールが
なされた。
実施例 3
温度刺激法によつて人工ふ化、飼育したムラサ
キイガイD状仔貝幼生、及び発生の進んだ成体か
らふ出、飼育したフジツボシプリス幼生を用いて
本発明薬剤の効果を試験した。試験はφ24mmの試
験管にD状仔貝幼生もしくはシプリス幼生を含む
海水20ml(幼生密度約50個/ml)を取り、薬剤を
所定濃度に調整して1時間ごとに24時間にわたつ
て実体顕微鏡で幼生の活動状況を観察し100%活
動を停止せしめるのに要する時間を求めた。
なお、本試験ではポリヘキサメチレンビグアニ
ドもしくはその水溶性塩として、平均分子量1200
のポリヘキサメチレンビグアニドの塩酸塩を用い
た。
また、比較のために過酸化水素もしくはポリヘ
キサメチレンビグアニド塩酸塩のみを用いた場合
の効果も試験した。結果を第3表に示す。[Table] As can be seen from Table 2, the decrease in U in the untreated area was
350kcal/ m2・hr・℃, while that in the test plots was less than 100kcal/ m2・hr・℃, and the slime adhesion rate in the test plots was 15 to 23% compared to the untreated plot. %, no slime adhesion was observed in appearance, and good slime control was achieved. Example 3 The effects of the drug of the present invention were tested using D-shaped mussel larvae that were artificially hatched and reared by the temperature stimulation method, and barnacle cypris larvae that were hatched from developed adults and reared. For the test, 20ml of seawater containing D-shaped larvae or cypris larvae (density of approximately 50 larvae/ml) was placed in a φ24mm test tube, and the drug was adjusted to the specified concentration using a stereomicroscope every hour for 24 hours. The activity status of the larvae was observed and the time required to stop 100% activity was determined. In this test, polyhexamethylene biguanide or its water-soluble salt was used with an average molecular weight of 1200.
The hydrochloride of polyhexamethylene biguanide was used. For comparison, the effects of using only hydrogen peroxide or polyhexamethylene biguanide hydrochloride were also tested. The results are shown in Table 3.
【表】【table】
【表】
かつたことを示す。
実施例 4
臨海地区の某製鉄工場に設置した一過式のモデ
ル水路で、ムラサキイガイの付着期である春季に
1ケ月間の通水試験を実施した。モデル水路は5
列の水路からなり、各水路の海水流量は10m2/
hr、平均流速は0.3m/sである。
この試験において、過酸化水素は35w/w%水
溶液を使用し、ポリヘキサメチレンビグアニドも
しくはその水溶性塩は平均分子量900のポリヘキ
サメチレンビグアニド塩酸塩の20w/w%水溶液
を使用し、それぞれ別個に注入した。結果を第4
表に示す。[Table] Shows what happened.
Example 4 A one-month water flow test was conducted in the spring, when the mussels are attached, in a temporary model waterway installed at a steel factory in the coastal area. The model waterway is 5
It consists of rows of waterways, and the seawater flow rate of each waterway is 10m 2 /
hr, average flow velocity is 0.3 m/s. In this test, a 35w/w% aqueous solution of hydrogen peroxide was used, and a 20w/w% aqueous solution of polyhexamethylene biguanide hydrochloride with an average molecular weight of 900 was used as polyhexamethylene biguanide or its water-soluble salt. Injected. 4th result
Shown in the table.
【表】
(注) 試験区No.3及び4において過酸化水素とポリ
ヘキサメチレンビグアニド塩酸塩の注入は同一時
間帯に注入した。
比較例 1
実施例4と同様にして、過酸化水素もしくはポ
リヘキサメチレンビグアニド塩酸塩を単独で用い
た場合の効果について試験した。結果を第5表に
示す。[Table] (Note) In test areas No. 3 and 4, hydrogen peroxide and polyhexamethylene biguanide hydrochloride were injected at the same time.
It was injected into the interstitial zone.
Comparative Example 1 In the same manner as in Example 4, the effect of using hydrogen peroxide or polyhexamethylene biguanide hydrochloride alone was tested. The results are shown in Table 5.
【表】
実施例 5
実施例4と同様のモデル水路で、フジツボの付
着期である夏季に1ケ月間の通水試験を実施し
た。使用した薬剤は実施例4に同じであるが、こ
の試験では両薬剤を予め混合後、添加した。混合
割合は以下の如くとした。
35w/w%過酸化水素 90部
20w/w%ポリヘキサメチレンビグアニド塩
酸塩 10部
結果を第6表に示す。[Table] Example 5 A one-month water flow test was conducted in the same model waterway as in Example 4 during the summer season when barnacles are attached. The drugs used were the same as in Example 4, but in this test both drugs were mixed in advance and then added. The mixing ratio was as follows. 35w/w% hydrogen peroxide 90 parts 20w/w% polyhexamethylene biguanide hydrochloride 10 parts The results are shown in Table 6.
【表】
比較例 2
実施例5と同様にして、過酸化水素もしくはポ
リヘキサメチレンビグアニド塩酸塩を単独で用い
た場合の効果について試験した。結果を第7表に
示す。[Table] Comparative Example 2 In the same manner as in Example 5, the effect of using hydrogen peroxide or polyhexamethylene biguanide hydrochloride alone was tested. The results are shown in Table 7.
【表】【table】
Claims (1)
及びYはそれぞれ炭素数3〜12個のアルキレン基
を示す。)の繰り返し単位からなるビグアニド重
合物、もしくはその水溶性塩とを有効成分として
含有することを特徴とする用水系付着物の防除
剤。[Claims] 1. Hydrogen peroxide and general formula (In the formula, R represents a hydrogen atom or a hydrocarbon group, and
and Y each represents an alkylene group having 3 to 12 carbon atoms. ), or a water-soluble salt thereof, as an active ingredient.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP46380A JPS5697598A (en) | 1980-01-07 | 1980-01-07 | Antifouling agent for protection of water system from contamination |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP46380A JPS5697598A (en) | 1980-01-07 | 1980-01-07 | Antifouling agent for protection of water system from contamination |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5697598A JPS5697598A (en) | 1981-08-06 |
| JPS6316197B2 true JPS6316197B2 (en) | 1988-04-07 |
Family
ID=11474481
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP46380A Granted JPS5697598A (en) | 1980-01-07 | 1980-01-07 | Antifouling agent for protection of water system from contamination |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5697598A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107522304A (en) * | 2017-08-01 | 2017-12-29 | 西安工程大学 | A kind of dirt dispersion agent and preparation method thereof |
Families Citing this family (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO1997033092A1 (en) | 1996-03-06 | 1997-09-12 | Hitachi, Ltd. | Centrifugal compressor and diffuser for the centrifugal compressor |
| DE19856071A1 (en) * | 1998-12-04 | 2000-06-15 | Degussa | Process for avoiding water contamination with non-resident organisms |
| JP2001172783A (en) * | 1999-12-13 | 2001-06-26 | Aquas Corp | Copper corrosion preventive and copper corrosion preventing method |
| JP4856811B2 (en) * | 2001-02-26 | 2012-01-18 | 三菱瓦斯化学株式会社 | Oberias adhesion control method |
| JP4521460B2 (en) * | 2008-02-20 | 2010-08-11 | メック株式会社 | Etching solution and method of forming copper wiring using the same |
| US11085010B2 (en) | 2017-08-18 | 2021-08-10 | Ecolab Usa Inc. | Method for off-line cleaning of cooling towers |
| JP7326083B2 (en) * | 2019-09-18 | 2023-08-15 | アクアス株式会社 | Algae control composition and algae control method |
| JP7326084B2 (en) * | 2019-09-18 | 2023-08-15 | アクアス株式会社 | Slime inhibitor composition and method for inhibiting slime |
-
1980
- 1980-01-07 JP JP46380A patent/JPS5697598A/en active Granted
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107522304A (en) * | 2017-08-01 | 2017-12-29 | 西安工程大学 | A kind of dirt dispersion agent and preparation method thereof |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5697598A (en) | 1981-08-06 |
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