JPS638997B2 - - Google Patents
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- Publication number
- JPS638997B2 JPS638997B2 JP15987580A JP15987580A JPS638997B2 JP S638997 B2 JPS638997 B2 JP S638997B2 JP 15987580 A JP15987580 A JP 15987580A JP 15987580 A JP15987580 A JP 15987580A JP S638997 B2 JPS638997 B2 JP S638997B2
- Authority
- JP
- Japan
- Prior art keywords
- copper
- cuprous oxide
- antifouling
- solubility
- antimony
- 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
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- Paints Or Removers (AREA)
- Compositions Of Macromolecular Compounds (AREA)
Description
本発明は船舶、水中構築物等に汚損生物が付着
することを防止し保護することを目的とする防汚
塗料組成物に関する。
海中には動物分類学上脊椎動物の次に位置する
原索動物のホヤから、最も下等な原生動物のプロ
トゾアに至るまでの多種多様な汚損動物が生棲
し、さらに付着珪藻や海藻などの汚損植物が繁殖
している。
防汚塗料に使用される防汚剤は、これら多種多
様な汚損生物全般に対し顕著な防除効果を長期間
にわたつて発揮すると同時に、人体に対する毒性
が低く、環境衛生上の問題点の少ないことが要求
される。近年防汚剤としてトリアルキルすず化合
物、トリフエニルすず化合物、DDT、BHC等の
有機塩素化合物、テトラアルキルチウラムジサル
フアイド、ジンクジアルキルジチオカルバメート
等の有機イオウ化合物が防汚塗料に使用されてい
るが、これら有機防汚剤は一般に特定の汚損生物
のみに選択的に効力を発揮するが、その他の生物
に対しては全く効果を示さず、特に海藻類の付着
防止には多くを期待できない。またすべての汚損
生物全般に対し防汚効果を持たせるようにすれ
ば、人体に対する毒性も強くなるなど未だ実用上
問題点が多い。これに対し銅系防汚剤の代表的な
亜酸化銅を例にとれば、本化合物はすべての汚損
生物に対し顕著な防汚効果を示す一方、人体に対
する毒性は低いので実用性の高い防汚剤として古
くから使用されて来た。しかし亜酸化銅すなわち
酸化第1銅は不安定で、海水中で酸化され次第に
2価の銅塩に変化し、防汚に必要な銅イオンの溶
出速度が10μg/cm2/dayを維持することができ
なくなり、塗膜中には銅化合物が存在するにも
かゝわらずついには防汚効果を失うことが認めら
れる。これは亜酸化銅は1価の銅イオンとして海
水に溶けるが直ちに酸化されて2価の銅イオンに
なり、さらに海水中に多量に存在する水酸イオン
や炭酸イオンを反応し、ついには塩基性炭酸銅に
変化するためであると考えられる。これを溶解度
の変化としてみれば、亜酸化銅の海水に対する溶
解度はPH8.2,温度20℃で5〜3×10-5モル/
であるのに対し、一方塩基性炭酸銅の溶解度は、
同一条件で4〜2×10-6モル/であるから、そ
の間に10倍もの開きがあることになる。
本発明者は、海水中において1価の亜酸化銅が
2価の銅化合物に酸化されることを防止または抑
制する方法について研究し、1価の銅イオンまた
は2価の銅イオンは酸化還元電位が銅より下位に
ある金属、すなわちビスマス、すず、鉛、ニツケ
ル、バナジウム、コバルト、カドミウム、鉄、ガ
リウム、亜鉛、セレン、テルル、マンガン、ジウ
コニウム、ゲルマニウム、チタン、アルミニウ
ム、マグネシウム、ならびに非金属の性質を有す
るが陽イオンを形成するアンチモン、ひ素、リン
等の物質により還元され、より低位のイオンまた
は金属銅にまで還元される性質に着目し、常に微
アルカリ性で酸化物質を多量に含む海水中で上記
の酸化還元反応が長期にわたり進行し、かつ環境
衛生上問題の少ない物質を探索した。これらの物
質は、前記酸化還元反応がアルカリ領域において
長期にわたり安定した速度を保ちながら進行する
必要があり、そのため酸化還元力が強く海水を加
水分解するマグネシウム、ナトリウム、海水中で
急速に消耗し持続性を失うリン、酸化還元反応に
より生成される物質が相互に反応し不溶性の銅化
合物を形成するアルミニウム、コバルト、および
環境衛生上好ましくないカドミウム、ひ素などを
除き、アンチモン、亜鉛、クロム、鉄、ニツケ
ル、鉛、チタンの少なくとも1種を添加すること
により、亜酸化銅のみならず、海水に対する溶解
度が3×10-6モル/以下の水酸化第2銅や塩基
性炭酸銅などの難溶性銅化合物の溶解を促進させ
ることができ、これを利用して長期間有効に使用
できる防汚塗料組成物を提供できることを知見し
た。
すなわち一般の防汚塗料の銅の溶出機構は1価
の銅イオンが極めて不安定のため明らかではない
が、溶解度の高い1価の銅イオンとして溶出し、
これが酸化されて溶解度の低い2価の銅イオンと
なる際に、過剰の2価の銅イオンが水酸化第2銅
や塩基性炭酸銅となり亜酸化銅の表面に析出する
一方向の反応が進行し、銅イオンの溶出速度が次
第に低下するものと考えられる。これに対し本発
明の防汚塗料組成物においては、亜酸化銅の表面
に析出した水酸化第2銅や塩基性炭酸銅は、添加
したすず、アンチモン、鉄などの還元性物質によ
り溶解度の高い1価の銅化合物に還元される逆方
向の反応がおこり、この二つの正逆反応がある点
で平衡を保つとにより安定した銅イオンの高い溶
出速度が得られるものと信じられる。
本発明の防汚塗料組成物は、難溶性銅化合物
と、該銅化合物より酸化還元電位が低くかつ水に
難溶性である還元性物質とを含む。ここでいう難
溶性銅化合物とは、PH8.2の海水に対する溶解度
が20℃において1×10-4モル/以下の一般には
不溶性といわれる銅化合物で、具体的には銅の酸
化物、硫化物、水酸化物、ロダン化物、フエロシ
アン化物、塩基性炭酸銅、ケイ酸銅、リン酸銅、
および銅イオンに解離する難溶性有機銅化合物が
挙げられる。
本発明に使用するすず、アンチモン、亜鉛、ク
ロム、鉄、ニツケル、鉛、チタンは単体は勿論、
こられ金属の2種以上の合金としても用いること
ができる。またその粒度は還元剤の還元速度や持
続性に影響するため、塗料配合組成、使用目的な
どにより異なるが、塗膜性能および塗装作業性を
考慮して250メツシユより細かいものを使用する。
本発明の防汚塗料組成物において難溶性物質と
還元性物質の組合わせおよびその配合割合は、防
汚塗料の使用方法、目的によつて異なる。例えば
さほど長期の防汚性を必要としない場合は亜酸化
銅の配合量は20〜35重量%と少ないかわりに、強
い還元力を持つアンチモン、鉄、チタンなどを亜
酸化銅の0.1〜30重量%添加すればよく、2年以
上の防汚性を期待する場合は、40〜50重量%の亜
酸化銅に対し還元作用は比較的ゆるやかで持続性
のあるニツケル、亜鉛、鉛などを亜酸化銅の5〜
60重量%加える。亜酸化銅に比較して溶解度の低
いロダン化銅、水酸化第二銅、塩基性炭酸銅等に
対しては、初期の溶出速度を高める強い還元作用
を持つ物質と、持続性のある物質とを組み合わせ
て使用することにより、安定した溶出速度が得ら
れる。しかしながら銅の溶出速度の促進は無制限
に行えばよいのではなく、最小必要溶出速度の
10μg/cm2/dayを大きく上まわることなく保持
すればよい。
本発明の防汚塗料組成物における防汚剤として
は、難溶性銅化合物以外に、公知の有機防汚剤例
えば有機すず化合物、有機イオウ化合物などを併
用してもよい。
また興味あることに本発面により難溶性銅化合
物の溶解促進の結果、従来の銅系防汚塗料組成物
では必須条件とされていたロジンを省くことが可
能になり、防汚塗膜の強度を著きく改善すること
ができた。
以下実施例により本発明を例証する。実施例中
部および%は、特に断らない限り重量による。
実施例 1
亜酸化銅5gと還元性物質としてアンチモン粉
末2gを500ml三角フラスコにとり、海水300mlを
加えかきまぜながら貯蔵する。貯蔵中海水は毎週
1回更新し、一定期間毎に試料の一部を取り出し
PH8.2,温度20℃に調整した海水に対する銅の溶
解度を測定した。
実施例2ないし4
還元性物質の種類を変え、実施例1と同様に処
理し、銅の溶解度を測定した。
実施例 5
亜酸化銅を水酸化第2銅に変え、アンチモン粉
末と組み合わせ、実施例1と同様に処理し、銅の
溶解度を測定した。
実施例 6
アンチモン粉末を8―クロムステンレス粉に変
え、実施例5と同様に処理し、銅の溶解度を測定
した。
比較例 1
実施例5のアンチモン粉末を赤リン粉末に変
え、実施例5と同様に処理し、銅の溶解度を測定
した。これらの結果を表―1に示す。
The present invention relates to an antifouling paint composition for preventing and protecting ships, underwater structures, etc. from adhesion of fouling organisms. A wide variety of fouling animals live in the sea, from ascidians, which are protochordates ranked next to vertebrates in animal taxonomy, to protozoa, the lowest protozoa. Polluted plants are growing. The antifouling agents used in antifouling paints have a remarkable long-term control effect against a wide variety of fouling organisms in general, and at the same time, they have low toxicity to the human body and have few environmental health problems. is required. In recent years, trialkyltin compounds, triphenyltin compounds, organic chlorine compounds such as DDT and BHC, and organic sulfur compounds such as tetraalkylthiuram disulfides and zinc dialkyldithiocarbamates have been used in antifouling paints as antifouling agents. Generally, these organic antifouling agents are selectively effective only against specific fouling organisms, but are completely ineffective against other organisms, and cannot be expected to be particularly effective in preventing the adhesion of seaweed. Furthermore, there are still many problems in practical use, such as the fact that if it were to have an antifouling effect against all fouling organisms in general, it would become more toxic to the human body. On the other hand, taking cuprous oxide, a typical copper-based antifouling agent, as an example, this compound shows a remarkable antifouling effect against all fouling organisms, while its toxicity to the human body is low, making it a highly practical antifouling agent. It has been used since ancient times as a staining agent. However, cuprous oxide, or cuprous oxide, is unstable and gradually changes to divalent copper salt when oxidized in seawater, and the elution rate of copper ions necessary for antifouling is maintained at 10 μg/cm 2 /day. It is observed that the coating film eventually loses its antifouling effect despite the presence of copper compounds in the coating. This is because cuprous oxide dissolves in seawater as monovalent copper ions, but is immediately oxidized to divalent copper ions, which then react with hydroxide ions and carbonate ions, which are present in large quantities in seawater, and finally become basic. This is thought to be due to the change to copper carbonate. If we look at this as a change in solubility, the solubility of cuprous oxide in seawater is 5 to 3 x 10 -5 mol/at a pH of 8.2 and a temperature of 20°C.
On the other hand, the solubility of basic copper carbonate is
Under the same conditions, it is 4 to 2 x 10 -6 mol/, so there is a difference of 10 times between them. The present inventor researched a method for preventing or suppressing the oxidation of monovalent cuprous oxide into divalent copper compounds in seawater, and found that monovalent copper ions or divalent copper ions have a redox potential. Properties of metals that are subordinate to copper, namely bismuth, tin, lead, nickel, vanadium, cobalt, cadmium, iron, gallium, zinc, selenium, tellurium, manganese, diumconium, germanium, titanium, aluminum, and magnesium, as well as nonmetallic properties. However, we focused on the property that it is reduced by substances such as antimony, arsenic, and phosphorus that form cations, and is reduced to lower ions or metallic copper. We searched for substances that allow the above redox reaction to proceed over a long period of time and pose fewer environmental health problems. The redox reaction of these substances needs to proceed at a stable rate over a long period of time in an alkaline region. Therefore, magnesium and sodium, which have strong redox power and hydrolyze seawater, are quickly depleted in seawater and do not last long. Antimony, zinc, chromium, iron, By adding at least one of nickel, lead, and titanium, not only cuprous oxide but also poorly soluble copper such as cupric hydroxide and basic copper carbonate, which have a solubility in seawater of 3 x 10 -6 mol/or less, can be used. It has been found that the dissolution of compounds can be promoted, and by utilizing this, it is possible to provide an antifouling paint composition that can be effectively used for a long period of time. In other words, the elution mechanism of copper from general antifouling paints is not clear because monovalent copper ions are extremely unstable, but it elutes as monovalent copper ions with high solubility.
When this is oxidized to become divalent copper ions with low solubility, a unidirectional reaction progresses in which excess divalent copper ions become cupric hydroxide and basic copper carbonate and precipitate on the surface of cuprous oxide. However, it is thought that the elution rate of copper ions gradually decreases. In contrast, in the antifouling paint composition of the present invention, cupric hydroxide and basic copper carbonate deposited on the surface of cuprous oxide have high solubility due to added reducing substances such as tin, antimony, and iron. It is believed that a reaction in the opposite direction of reduction to a monovalent copper compound occurs, and that by maintaining an equilibrium between these two forward and reverse reactions at a certain point, a more stable and high elution rate of copper ions can be obtained. The antifouling paint composition of the present invention includes a sparingly soluble copper compound and a reducing substance that has a lower redox potential than the copper compound and is sparingly soluble in water. The poorly soluble copper compound referred to here refers to a copper compound that is generally said to be insoluble, with a solubility in seawater of PH8.2 of 1 x 10 -4 mol/or less at 20°C, and specifically copper oxides and sulfides. , hydroxide, rhodanide, ferrocyanide, basic copper carbonate, copper silicate, copper phosphate,
and sparingly soluble organic copper compounds that dissociate into copper ions. Tin, antimony, zinc, chromium, iron, nickel, lead, and titanium used in the present invention can be used alone, of course;
It can also be used as an alloy of two or more of these metals. In addition, the particle size affects the reduction rate and sustainability of the reducing agent, so it varies depending on the paint composition, purpose of use, etc., but in consideration of coating film performance and painting workability, particles finer than 250 mesh are used. In the antifouling paint composition of the present invention, the combination of a poorly soluble substance and a reducing substance and their blending ratio vary depending on the method and purpose of using the antifouling paint. For example, if long-term antifouling properties are not required, the amount of cuprous oxide mixed is as low as 20 to 35% by weight, but antimony, iron, titanium, etc., which have strong reducing power, are added at 0.1 to 30% by weight of cuprous oxide. %, and if you expect stain resistance for more than 2 years, add 40 to 50% by weight of cuprous oxide to nickel, zinc, lead, etc. whose reducing action is relatively slow and long-lasting. Copper 5~
Add 60% by weight. For copper rhodanide, cupric hydroxide, basic copper carbonate, etc., which have lower solubility than cuprous oxide, there are substances that have a strong reducing effect that increases the initial dissolution rate, and substances that are persistent. By using these in combination, a stable elution rate can be obtained. However, it is not enough to accelerate the elution rate of copper without limit;
It is sufficient to maintain the amount without significantly exceeding 10 μg/cm 2 /day. As the antifouling agent in the antifouling paint composition of the present invention, in addition to the sparingly soluble copper compound, known organic antifouling agents such as organic tin compounds and organic sulfur compounds may be used in combination. It is also interesting to note that this discovery promotes the dissolution of poorly soluble copper compounds, making it possible to omit rosin, which was considered an essential condition in conventional copper-based antifouling paint compositions, thereby increasing the strength of the antifouling paint film. could be significantly improved. The invention is illustrated by the following examples. Examples and percentages are by weight unless otherwise specified. Example 1 5 g of cuprous oxide and 2 g of antimony powder as a reducing substance are placed in a 500 ml Erlenmeyer flask, 300 ml of seawater is added, and the flask is stored while stirring. During storage, seawater is refreshed once a week, and a portion of the sample is taken out at regular intervals.
The solubility of copper in seawater adjusted to pH 8.2 and temperature 20℃ was measured. Examples 2 to 4 The solubility of copper was measured in the same manner as in Example 1 except that the type of reducing substance was changed. Example 5 Cuprous oxide was replaced with cupric hydroxide, combined with antimony powder, treated in the same manner as in Example 1, and the solubility of copper was measured. Example 6 The antimony powder was replaced with 8-chromium stainless steel powder, treated in the same manner as in Example 5, and the solubility of copper was measured. Comparative Example 1 The antimony powder in Example 5 was replaced with red phosphorus powder, the same treatment as in Example 5 was carried out, and the solubility of copper was measured. These results are shown in Table-1.
【表】
表―1から明らかなように、本発明による還元
性物質の添加は難溶性銅化合物の溶解度を著しく
高めることができた。
実施例7ないし9
表―2の実施例7ないし9,比較例2および3
の成分を均一に混合して塗料を調製し、80ないし
100ミクロンの厚さに塗装した試験板を岡山県玉
野海域のいかだに吊り下げ、一定期間毎に引き上
げ、塗膜から溶出する銅イオンの溶出速度を測定
した。結果を表―3に示す。[Table] As is clear from Table 1, the addition of the reducing substance according to the present invention was able to significantly increase the solubility of the poorly soluble copper compound. Examples 7 to 9 Examples 7 to 9 and Comparative Examples 2 and 3 in Table 2
Prepare the paint by uniformly mixing the ingredients of
A test plate coated with a thickness of 100 microns was suspended on a raft in the Tamano Sea area in Okayama Prefecture, and lifted out at regular intervals to measure the elution rate of copper ions eluted from the paint film. The results are shown in Table-3.
【表】【table】
【表】
註 * 塩化ビニル〓 ビニルブチルエーテル
共重合樹脂 西独ヘキスト社製
[Table] Note * Vinyl chloride = Vinyl butyl ether Copolymer resin Manufactured by Hoechst, West Germany
【表】
本発明組成物を塗布したものは比較塗料を塗布
したものに比べて銅イオンの溶出速度において顕
著な効果を示した。なお防汚に必要な最少溶出速
度は10μg/cm2/dayである。
実施例 10
チタン粉 2.0
亜酸化銅 20.0
トリフエニール錫ハイドロオキサイド 10.0
ベンガラ 13.0
タルク 10.0
ロジン 10.0
塩化ゴム 10.0
T.C.P. 5.0
キシレン 20.0
計 100.0
実施例 11
アンチモン粉 5.0
亜酸化銅 20.0
ベンガラ 15.0
タルク 15.0
ロジン 10.0
塩化ゴム 10.0
T.C.P. 5.0
キシレン 20.0
計 100.0
実施例 12
ニツケル粉 10.0
亜酸化銅 50.0
ロジン 8.0
ポリ塩化ビニル(UCC製VYHH) 6.0
T.C.P. 2.0
メチルイソブチルケトン 12.0
トルエン 12.0
計 100.0
実施例 13
亜鉛粉 10.0
亜酸化銅 50.0
ポリ塩化ビニル(UCC製VYHH) 10.0
T.C.P. 2.0
メチルイソブチルケトン 14.0
トルエン 14.0
計 100.0
実施例 14
ステンレス粉(8クロム鋼) 20.0
水酸化第二銅 40.0
ロジン 8.0
ポリ塩化ビニル(UCC製VYHH) 6.0
T.C.P. 2.0
メチルイソブチルケトン 12.0
トルエン 12.0
計 100.0
実施例 15
鉛粉 15.0
亜酸化銅 40.0
ロジン 15.0
アマニボイル油 10.0
ナフサ 20.0
計 100.0
比較例 4
亜酸化銅 20.0
トリフエニール錫ハイドロオキサイド 10.0
亜鉛華 10.0
ベンガラ 10.0
タルク 5.0
ロジン 10.0
塩化ゴム 10.0
T.C.P. 5.0
キシレン 20.0
計 100.0
比較例 5
亜酸化銅 50.0
亜鉛華 5.0
ベンガラ 5.0
ロジン 8.0
ポリ塩化ビニル(UCC製VYHH) 6.0
T.C.P. 2.0
メチルイソブチルケトン 12.0
トルエン 12.0
計 100.0
比較例 6
亜酸化銅 40.0
ベンガラ 10.0
タルク 5.0
ロジン 15.0
アマニボイル油 10.0
ナフサ 20.0
計 100.0
比較例 7
ベンガラ 25.0
亜鉛華 20.0
タルク 5.0
ロジン 20.0
塩化ゴム 7.0
T.C.P. 3.0
キシレン 20.0
計 100.0
実施例16ないし19[Table] The coatings coated with the composition of the present invention showed a remarkable effect on the elution rate of copper ions compared to the coatings coated with the comparative paint. The minimum elution rate required for antifouling is 10 μg/cm 2 /day. Example 10 Titanium powder 2.0 Cuprous oxide 20.0 Triphenyltin hydroxide 10.0 Red iron 13.0 Talc 10.0 Rosin 10.0 Chlorinated rubber 10.0 TCP 5.0 Xylene 20.0 Total 100.0 Example 11 Antimony powder 5.0 Cuprous oxide 20.0 Red iron 15 .0 Talc 15.0 Rosin 10.0 Chlorinated Rubber 10.0 TCP 5.0 Xylene 20.0 Total 100.0 Example 12 Nickel powder 10.0 Cuprous oxide 50.0 Rosin 8.0 Polyvinyl chloride (UCC VYHH) 6.0 TCP 2.0 Methyl isobutyl ketone 12.0 Toluene 12.0 Total 100.0 Example 13 Zinc powder 10.0 Cuprous oxide 50 .0 Polyvinyl chloride ( VYHH manufactured by UCC) 10.0 TCP 2.0 Methyl isobutyl ketone 14.0 Toluene 14.0 Total 100.0 Example 14 Stainless steel powder (8 chromium steel) 20.0 Cupric hydroxide 40.0 Rosin 8.0 Polyvinyl chloride (VYHH manufactured by UCC) 6.0 TCP 2.0 Methyl isobutyl ketone 12.0 Toluene 12.0 Total 100.0 Example 15 Lead powder 15.0 Cuprous oxide 40.0 Rosin 15.0 Linseed boil oil 10.0 Naphtha 20.0 Total 100.0 Comparative example 4 Cuprous oxide 20.0 Triphenyltin hydroxide 10.0 Zinc white 10.0 Red iron 10.0 Talc 5.0 Rosin 10.0 Chlorinated rubber 10.0 TCP 5.0 Xylene 20.0 Total 100.0 Comparative Example 5 Cuprous oxide 50.0 Zinc white 5.0 Red iron 5.0 Rosin 8.0 Polyvinyl chloride (VYHH manufactured by UCC) 6.0 TCP 2.0 Methyl isobutyl ketone 12.0 Toluene 12.0 Total 100.0 Comparative example 6 Cuprous oxide 40.0 Red iron 10.0 Talc 5.0 Gin 15.0 Linseed boil oil 10.0 Naphtha 20.0 Total 100.0 Comparative Example 7 Red iron 25.0 Zinc white 20.0 Talc 5.0 Rosin 20.0 Chlorinated rubber 7.0 TCP 3.0 Xylene 20.0 Total 100.0 Examples 16 to 19
【表】【table】
【表】
高分子有機錫化合物の合成例
26部のトリブチル錫メタクリレートおよび14部
のメチルメタクリレートを60部のキシレン中に溶
かし、そして0.4部の過酸化ベンゾイルを加えた。
温度を8時間にわたつて徐々に上昇させ、発熱を
制御するために必要に応じて冷却し、最終温度は
110℃になつた。この結果高分子有機錫化合物40
%溶液を得た。
比較例 8
高分子有機錫化合物の40%溶液 55
亜酸化銅 30
チタン白 10
ベントナイト 1
ハイドロキノン 0.1
キシレン 4
計 100.1
以上の各実施例および比較例に記載の配合組成
物を常法に従つて塗料化した防汚塗料をあらかじ
め防錆塗料を塗布した鋼板に塗布した後、岡山県
玉野市宇野港内において1ケ年の海中浸漬試験を
行つた。
その結果を表―4に示す。試験結果は生物の付
着百分率により次の6段階に分けて表示した。
5:80%以上付着
4:40―80%付着
3:20―40%付着
2:10―20%付着
1:10%以下付着
0:生物付着なしTable: Synthesis Example of Polymeric Organotin Compounds 26 parts of tributyltin methacrylate and 14 parts of methyl methacrylate were dissolved in 60 parts of xylene, and 0.4 parts of benzoyl peroxide were added.
The temperature was gradually increased over 8 hours, cooling as necessary to control exotherm, and the final temperature was
The temperature reached 110℃. The resulting polymeric organotin compound 40
% solution was obtained. Comparative Example 8 40% solution of polymeric organotin compound 55 Cuprous oxide 30 Titanium white 10 Bentonite 1 Hydroquinone 0.1 Xylene 4 Total 100.1 The compositions described in the above Examples and Comparative Examples were made into a paint according to a conventional method. After applying the antifouling paint to a steel plate that had been previously coated with antirust paint, a one-year underwater immersion test was conducted in Uno Port, Tamano City, Okayama Prefecture. The results are shown in Table 4. The test results were divided into the following six levels and displayed according to the percentage of attachment of organisms. 5: 80% or more adhesion 4: 40-80% adhesion 3: 20-40% adhesion 2: 10-20% adhesion 1: 10% or less adhesion 0: No biofouling
【表】
表―4に示されるように本発明に係る防汚塗料
組成物は海中浸漬試験で評価を行なつた結果、12
ケ月の浸漬によつても海藻の付着を完全に阻止す
ることができた。[Table] As shown in Table 4, the antifouling paint composition according to the present invention was evaluated in an underwater immersion test, and as a result, 12
It was also possible to completely prevent the adhesion of seaweed by soaking the shells.
Claims (1)
電位が低くかつ水に難溶性である還元性物質を含
むことを特徴とする防汚塗料組成物。 2 還元性物質が、すず、アンチモン、亜鉛、ク
ロム、鉄、ニツケル、鉛またはチタンの少なくと
も1種である特許請求の範囲第1項の防汚塗料組
成物。 3 還元性物質が、すず、アンチモン、亜鉛、ク
ロム、鉄、ニツケル、鉛またはチタンを含む合金
の少なくとも1種である特許請求の範囲第1項の
防汚塗料組成物。[Scope of Claims] 1. An antifouling paint composition comprising a sparingly soluble copper compound and a reducing substance that has a lower redox potential than the copper compound and is sparingly soluble in water. 2. The antifouling paint composition according to claim 1, wherein the reducing substance is at least one of tin, antimony, zinc, chromium, iron, nickel, lead, or titanium. 3. The antifouling paint composition according to claim 1, wherein the reducing substance is at least one kind of alloy containing tin, antimony, zinc, chromium, iron, nickel, lead, or titanium.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP15987580A JPS5783566A (en) | 1980-11-12 | 1980-11-12 | Antifouling coating composition |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP15987580A JPS5783566A (en) | 1980-11-12 | 1980-11-12 | Antifouling coating composition |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5783566A JPS5783566A (en) | 1982-05-25 |
| JPS638997B2 true JPS638997B2 (en) | 1988-02-25 |
Family
ID=15703106
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP15987580A Granted JPS5783566A (en) | 1980-11-12 | 1980-11-12 | Antifouling coating composition |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5783566A (en) |
-
1980
- 1980-11-12 JP JP15987580A patent/JPS5783566A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5783566A (en) | 1982-05-25 |
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