JPH0337483B2 - - Google Patents

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Publication number
JPH0337483B2
JPH0337483B2 JP16016983A JP16016983A JPH0337483B2 JP H0337483 B2 JPH0337483 B2 JP H0337483B2 JP 16016983 A JP16016983 A JP 16016983A JP 16016983 A JP16016983 A JP 16016983A JP H0337483 B2 JPH0337483 B2 JP H0337483B2
Authority
JP
Japan
Prior art keywords
water
biocidal
substance
diluted
wood
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
Application number
JP16016983A
Other languages
Japanese (ja)
Other versions
JPS60155403A (en
Inventor
Toshikazu Minami
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.)
Shinto Paint Co Ltd
Original Assignee
Shinto Paint Co 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 Shinto Paint Co Ltd filed Critical Shinto Paint Co Ltd
Priority to JP16016983A priority Critical patent/JPS60155403A/en
Publication of JPS60155403A publication Critical patent/JPS60155403A/en
Publication of JPH0337483B2 publication Critical patent/JPH0337483B2/ja
Granted legal-status Critical Current

Links

Description

【発明の詳細な説明】[Detailed description of the invention]

本発明は微粒化した固形の殺生原体を安定に分
散せしめてなる水性懸濁状木材保護組成物に関
し、水に希釈した場合でも長期間殺生原体が沈降
せず良好な木材保護効果を持続する組成物に関す
るものである。 製材された木材表面におけるかびの発生を防止
する方法として一般的に行なわれているのは、防
かび剤を20〜200倍の水に希釈した水溶液に木材
を数分〜数十分間浸漬処理する方法である。従つ
て木材防かび剤に要求される特性としては、大量
の水で希釈した状態で殺生原体が長期間に亘り安
定な分散状態に維持されること、即ち殺生原体が
分離、沈降或は結晶析出等を起こさないこと、が
挙げられる。 ところで現在市販されている木材防かび剤の殆
んどは、殺生原体として2,4,6−トリクロロ
フエノール、ペンタクロロフエノール、2,4,
6−トリブロモフエノール、2,4−ジクロロ−
5−ブロムフエノール等のハロゲン化フエノール
をアルカリ水溶液に溶解した水性製剤であり、こ
の水性製剤は優れた防かび効果を有すると共に、
界面活性剤を使用する必要がないのでコスト的に
も有利であるといつた特長を有している。 一方、ハロゲン化フエノール以外にも木材防か
び剤として有効な殺生原体も種々知られている
が、その殆んどは水に不溶性の固体である為、こ
れを製剤化するにはまず有機溶剤に溶解した後、
水希釈性を与える為の界面活性剤を添加しなけれ
ばならず、製剤としての高濃度化が困難であ
る、水希釈時に殺生原体の結晶が析出する恐れ
がある、有機溶剤を使用する為高価で且つ火災
の危険や人畜に対する吸入毒性を有している、等
の欠点があるので、現在のところ殆んど実用化さ
れていない。こうした欠点を解決する方策とし
て、農薬分野等で広く利用されている様な水性懸
濁製剤とする方法が考えられる。即ち水性懸濁製
剤とは、水に不溶性の固形原体を界面活性剤、増
粘剤、保護コロイド剤等の力を借りて水中に安定
に分散させた製剤であり、木材防かび剤として使
用可能な水不溶性の固形殺生原体も農薬原体と同
様に水性懸濁製剤とすることが可能である。しか
し農薬用の水性懸濁製剤は流通商品としての安定
性が問題となるだけであつて、これを水に希釈し
たときの安定性はそれほど重要でなく、水への分
散が可能で且つ数時間沈降しない程度の分散性が
あれば十分である。しかしながら木材防かび剤の
場合は水希釈後長期間に亘つて固形殺生原体が分
散状態で安定に維持されなければならず、農薬用
途の水性懸濁製剤の技術をそのまま転用しただけ
では木材保護の目的を果すことができない。 本発明者等はこうした事情に着目し、常温にお
いて固体で実質的に水不溶性の木材保護用殺生原
体を使用し、大量の水に希釈した場合でも該殺生
原体を分散状態で長期間安定に保持し得る様な水
性懸濁状木材保護組成物を開発しようとして種々
研究を進めてきた。本発明はかかる研究の結果完
成されたものであつて、その構成は、水系分散媒
中に木材保護用殺生原体を有効成分として懸濁状
に分散させてなる水性懸濁状木材保護組成物であ
つて、前記木材保護用殺生原体は、常温において
固体で前記水系分散媒に対する溶解度が50ppm以
下であり、且つ真比重と平均粒子径(単位:μ
m)の積が0.8(μm)以下であるところに要旨を
有するものである。 固形状で水に不溶性の殺生原体を水中に安定に
分散させる為には、界面活性剤を用いて固体粒子
の濡れ及び分散を良くするのが有効と考えられる
が、それ以外の根本的な問題として殺生原体の真
比重及び粒子径並びに分散媒の比重及び粘度が関
与することも確認されている。これらのうち殺生
原体の比重及び分散媒の比重は通常変えることが
できないが、殺生原体の粒子径及び分散媒の粘度
を変えることは可能である。その為従来の水性懸
濁製剤では固形原体の粒子径を極力小さくすると
共に分散媒の粘度を大きくして殺生原体粒子の沈
降防止を図つている。しかしこの水性懸濁製剤を
大量の水に希釈すると分散媒(水)の粘度は約
1cpで一定となり、製剤の状態では安定であつた
殺生原体の粒子が速やかに沈降してしまう。この
場合の沈降防止対策としては上記諸条件のうち殺
生原体の粒子径を小さくする方法が考えられる。
小さくする度合は殺生原体の真比重によつて異な
るが、通常0.2〜0.5μm程度であれば製剤調製直
後に水希釈しても長期間安定なものが得られる。
しかしながら殺生原体の種類によつては、長期間
保存した後の製剤を水に希釈したときの安定性が
極端に悪くなることがある。これは製剤保存時に
殺生原体の経時的な肥大化が起こる為と考えられ
る。そしてこうした傾向は殺生原体の水に対する
溶解度が大きい程強くなることが確認された。こ
の様に殺生原体の水性懸濁製剤を大量の水に希釈
したときの安定性は、殺生原体の真比重及び粒子
径並びに分散媒への溶解度に著しく依存してい
る。本発明ではこうした殺生原体の水分散性に及
ぼす前記各要素の相互関係を詳細に検討した結
果、分散媒に対する溶解度が50ppm以下で且つ真
比重と粒子径(単位:μm)の積が0.8以下とい
う要件を満たす殺生原体を使用すれば、製剤自体
はもとよりこれを大量の水に希釈した場合でも極
めて優れた安定性を示すという事実を見出し、本
発明に到達したものである。 本発明で使用する分散媒の主成分は水である
が、この他殺生原体の分散を促進させる為の界面
活性剤或は凍結防止用のアルコールやダライコー
ル類等の様に、水よりも殺生原体をよく溶解する
添加剤を配合することが多いが、本発明では殺生
原体の溶解度が50ppmを越えないという条件を満
たす範囲で界面活性剤その他の添加剤の種類や添
加量を考慮しなければならない。その理由は、上
記溶解度が50ppmを越えると前述の如く製剤保存
時に殺生原体粒子が肥大化し、大量の水で希釈し
たときの分散安定性が低下するからである。尚分
散剤の主体は水であるから、好適な殺生原体を選
択するにあたつては目安として水に対する溶解度
が50ppm以下のものであれば好ましいものと判断
してよく、この様な殺生原体としては例えば2−
ベンズイミダゾールカルバミン酸メチル、2−
(4′−チアゾリル)ベンゾイミダゾール、N−1,
1,2,2,−テトラクロルエチルチオテトラヒ
ドロフタルイミド、テトラクロルイソフタロニト
リル等が挙げられ、これらは単独で或は必要によ
り2種以上を組合せて使用することができる。 また本発明に係る他の特徴的構成である 〔殺生原体の真比重×同粒子径(μm)〕<0.8(μ
m) という構成は、製剤自体の放置安定性及びこれを
水に希釈したときの安定性を良好に保つうえで不
可欠の要件であり、例えば殺生原体の真比重が2
であれば平均粒径を0.4μm以下に粉砕し、又真比
重が1.5であれば平均粒径を0.53μm以下に粉砕し
て使用しなければならない。しかして上記積が
0.8(μm)を越えると製剤を水に希釈したときの
分散安定性が低下し、木材保護組成物としての性
能を長期間維持することができなくなる。 上記の様な諸要件を満たす木材保護組成物を製
造する為の具体的な方法は格別特殊なものではな
く、一般的な水性懸濁製剤の製法に準じた方法を
採用することができ、例えば常温で固体の木材
用殺生原体を予めエアミルやハンマーミル等の乾
式粉砕機で微粉砕した後、界面活性剤を用いて水
中に分散させる方法、木材殺生原体を界面活性
剤及び水と共に混合し、振動ミルやサンドミル等
の湿式粉砕機で微粉砕すると共に水中に分散させ
る方法、等が一般的な方法として推奨される。ま
た上記製剤製造工程で適量の増粘剤や消泡剤、凍
結防止剤等を添加し、分散安定性等の向上を図る
ことも有効である。更に本発明に係る上記水性懸
濁製剤には必要により、ハロゲン化フエノールの
様な水溶性殺生原体或は界面活性剤で乳化・可溶
化した液状の疎水性殺生原体を少量配合すること
もできる。 界面活性剤は前述の如く製剤及び水希釈時の分
散安定性を高めるのに有効であるが、ノニオン界
面活性剤(例えばポリオキシエチレンアルキルフ
エニルエーテル、ポリオキシエチレンアルキルエ
ーテル、ポリオキシエチレンフエノールエーテル
等)とアニオン界面活性剤(例えばジアルキルス
ルホサクシネート、ナフタリンスルホン酸とホル
マリンの縮合物、ポリオキシエチレンアルキルア
リルエーテルサルフエート等)を混合使用したと
きに最良の結果が得られる。又特に製剤保存時の
分散安定性を高めるのに有効な増粘剤としては、
例えばグアーガム、アラビアガム等の天然物やカ
ルボキシメチルセルロースナトリウムやアルギン
酸アルカリ塩等の加工天然物、ポリビニルアルコ
ールやポリビニルピロリドン等の合成物が賞用さ
れる。 本発明は以上の様に構成されるが、要は木材用
殺生原体の分散媒に対する溶解度及び真比重と平
均粒子径の積を適正に調整することによつて、製
剤自体の保存安定性はもとより水希釈時における
分散安定性を飛躍的に高めることができ、木材保
存剤としての性能を長期間高レベルに維持し得る
ことになつた。 次に実施例及び比較例を挙げて本発明の効果を
一層明確にする。尚下記実験例及び比較例で使用
する殺生原体は何れも1〜10μmに乾式粉砕した
ものを用いた。 実施例 1〜3 水にポリオキシエチレン(20モル)スチリルフ
エニルエーテルとジオクチルスルホサクシネート
を溶解し、これに木材用殺生原体を加えて混合す
る。混合比率は下記の通りとした。 殺生原体 30重量% ポリオキシエチレン(20モル)−スチリルフエニ
ルエーテル 4 〃 ジオクチルスルホサクシネート 〃 水 残部 この混合物350gと粉砕メデイア(ガラスビー
ズ1mmφ)1000gとを内容量1のパールミル
(90mmφ×160mmh)に入れ、周速4m/secで所
定時間粉砕・混合した。用いた殺生原体及び粉砕
時間は下記の通りとした。
The present invention relates to an aqueous wood-suspended wood protection composition in which a micronized solid biocidal active substance is stably dispersed, and even when diluted with water, the biocidal active substance does not settle for a long period of time and maintains a good wood protection effect. The present invention relates to a composition for carrying out. A commonly used method to prevent mold from forming on the surface of sawn wood is to immerse the wood in an aqueous solution containing a fungicide diluted 20 to 200 times as much water for several minutes to several tens of minutes. This is the way to do it. Therefore, the characteristics required of a wood fungicide are that the biocidal active substance is maintained in a stable dispersion state for a long period of time when diluted with a large amount of water; that is, the biocidal active substance does not separate, settle, or One example is that crystal precipitation does not occur. By the way, most of the wood fungicides currently on the market contain 2,4,6-trichlorophenol, pentachlorophenol, 2,4,
6-tribromophenol, 2,4-dichloro-
It is an aqueous preparation in which a halogenated phenol such as 5-bromophenol is dissolved in an alkaline aqueous solution, and this aqueous preparation has an excellent antifungal effect, and
It has the advantage of being cost-effective as it does not require the use of surfactants. On the other hand, in addition to halogenated phenols, there are various biocide active substances that are effective as wood fungicides, but most of them are solids that are insoluble in water, so in order to formulate them, organic solvents are first used. After dissolving in
It is necessary to add a surfactant to provide water dilutability, making it difficult to achieve high concentrations as a formulation; there is a risk that crystals of the biocidal drug substance may precipitate when diluted with water; organic solvents are used; At present, it is hardly put into practical use because it has drawbacks such as being expensive, causing fire danger, and being inhaled toxic to humans and animals. One possible solution to these drawbacks is to formulate an aqueous suspension preparation, which is widely used in the field of agrochemicals and the like. In other words, an aqueous suspension preparation is a preparation in which a water-insoluble solid substance is stably dispersed in water with the help of surfactants, thickeners, protective colloids, etc., and is used as a wood fungicide. Possible water-insoluble solid biocidal drug substances can also be made into aqueous suspension formulations, similar to pesticide drug substances. However, the only problem with aqueous suspension preparations for agricultural chemicals is their stability as a distributed product, and the stability when diluted in water is not so important. It is sufficient that it has enough dispersibility to prevent sedimentation. However, in the case of wood fungicides, the solid biocidal active substance must be stably maintained in a dispersed state for a long period of time after being diluted with water. cannot fulfill its purpose. The present inventors focused on these circumstances and used a biocidal active ingredient for wood protection that is solid at room temperature and substantially water-insoluble, and the biocidal active ingredient remains stable for a long period of time in a dispersed state even when diluted in a large amount of water. Various studies have been carried out in an attempt to develop an aqueous suspension wood protection composition that can maintain the properties of wood. The present invention was completed as a result of such research, and consists of an aqueous suspension wood protection composition in which a biocidal active ingredient for wood protection is dispersed as an active ingredient in an aqueous dispersion medium. The biocide active substance for wood protection is solid at room temperature, has a solubility in the aqueous dispersion medium of 50 ppm or less, and has a true specific gravity and an average particle diameter (unit: μ
The gist is that the product of m) is 0.8 (μm) or less. In order to stably disperse a solid, water-insoluble biocidal substance in water, it is thought to be effective to improve the wetting and dispersion of solid particles using a surfactant, but there are other fundamental problems. It has also been confirmed that the true specific gravity and particle size of the biocidal substance and the specific gravity and viscosity of the dispersion medium are involved as problems. Among these, the specific gravity of the biocide active substance and the specific gravity of the dispersion medium cannot usually be changed, but it is possible to change the particle size of the biocide active substance and the viscosity of the dispersion medium. Therefore, in conventional aqueous suspension preparations, the particle size of the solid drug substance is made as small as possible and the viscosity of the dispersion medium is increased to prevent the biocidal drug particles from settling. However, when this aqueous suspension preparation is diluted with a large amount of water, the viscosity of the dispersion medium (water) becomes approx.
It becomes constant at 1 cp, and the biocidal drug particles, which were stable in the formulation state, quickly settle out. As a countermeasure to prevent sedimentation in this case, a method of reducing the particle size of the biocidal active substance under the above conditions can be considered.
The degree of reduction varies depending on the true specific gravity of the biocidal drug substance, but if it is generally about 0.2 to 0.5 μm, a product that is stable for a long period of time can be obtained even if diluted with water immediately after preparation.
However, depending on the type of biocidal drug substance, the stability of the preparation after long-term storage may be extremely poor when diluted with water. This is thought to be because the biocidal drug substance enlarges over time during storage of the preparation. It was confirmed that this tendency becomes stronger as the solubility of the biocidal substance in water increases. As described above, the stability of an aqueous suspension preparation of a biocidal drug substance when diluted in a large amount of water is significantly dependent on the true specific gravity and particle size of the biocidal drug substance, as well as its solubility in a dispersion medium. In the present invention, as a result of a detailed study of the interrelationship of the above-mentioned factors on the water dispersibility of the biocidal active substance, we found that the solubility in the dispersion medium is 50 ppm or less, and the product of true specific gravity and particle diameter (unit: μm) is 0.8 or less. The present invention was achieved based on the discovery that if a biocidal drug substance that satisfies the above requirements is used, the formulation itself exhibits extremely excellent stability not only when it is diluted with a large amount of water. The main component of the dispersion medium used in the present invention is water, but in addition, surfactants to promote the dispersion of the biocidal substance, alcohols for anti-freezing, Dalaicol, etc. Additives that dissolve the active biocidal substance well are often added, but in the present invention, the type and amount of surfactants and other additives are taken into consideration as long as the solubility of the active biocidal substance does not exceed 50 ppm. Must. The reason for this is that if the above-mentioned solubility exceeds 50 ppm, the biocidal drug substance particles will enlarge during storage of the preparation as described above, and the dispersion stability will decrease when diluted with a large amount of water. Furthermore, since the main component of the dispersant is water, when selecting a suitable biocidal substance, it can be judged that it is preferable if the solubility in water is 50 ppm or less. For example, the body is 2-
Benzimidazole methyl carbamate, 2-
(4'-thiazolyl)benzimidazole, N-1,
Examples include 1,2,2-tetrachloroethylthiotetrahydrophthalimide, tetrachloroisophthalonitrile, and the like, and these can be used alone or in combination of two or more types if necessary. In addition, another characteristic configuration of the present invention is [true specific gravity of biocidal substance x particle diameter (μm)] < 0.8 (μm)
m) is an essential requirement for maintaining good storage stability of the formulation itself and stability when diluted with water; for example, if the true specific gravity of the biocidal drug substance is 2.
If so, then the average particle size must be pulverized to 0.4 μm or less, and if the true specific gravity is 1.5, the average particle size must be pulverized to 0.53 μm or less before use. However, the above product is
If it exceeds 0.8 (μm), the dispersion stability of the preparation when diluted with water decreases, making it impossible to maintain its performance as a wood protection composition for a long period of time. The specific method for producing a wood protection composition that meets the above requirements is not particularly special, and a method similar to the production method for general aqueous suspension preparations can be adopted, for example. A method in which the wood biocidal active substance, which is solid at room temperature, is finely pulverized using a dry grinder such as an air mill or a hammer mill, and then dispersed in water using a surfactant, and the wood biocidal active substance is mixed with the surfactant and water. However, as a general method, it is recommended to finely pulverize the material using a wet pulverizer such as a vibration mill or a sand mill, and then disperse it in water. It is also effective to add an appropriate amount of a thickener, antifoaming agent, antifreeze agent, etc. in the above-mentioned preparation manufacturing process to improve dispersion stability and the like. Furthermore, if necessary, the aqueous suspension preparation according to the present invention may contain a small amount of a water-soluble biocide drug substance such as a halogenated phenol, or a liquid hydrophobic biocide drug substance emulsified and solubilized with a surfactant. can. As mentioned above, surfactants are effective in improving the dispersion stability of formulations and water dilution, but nonionic surfactants (e.g., polyoxyethylene alkyl phenyl ether, polyoxyethylene alkyl ether, polyoxyethylene phenol ether) The best results are obtained when a mixture of anionic surfactants (such as dialkyl sulfosuccinates, condensates of naphthalene sulfonic acid and formalin, polyoxyethylene alkyl allyl ether sulfates, etc.) is used. In addition, thickeners that are particularly effective for increasing dispersion stability during storage of formulations include:
For example, natural products such as guar gum and gum arabic, processed natural products such as sodium carboxymethylcellulose and alkali alginate, and synthetic products such as polyvinyl alcohol and polyvinylpyrrolidone are used. The present invention is constructed as described above, but the key point is that the storage stability of the formulation itself can be improved by appropriately adjusting the solubility of the biocidal raw material for wood in the dispersion medium and the product of true specific gravity and average particle diameter. In addition, the dispersion stability when diluted with water can be dramatically improved, and the performance as a wood preservative can be maintained at a high level for a long period of time. Next, Examples and Comparative Examples will be given to further clarify the effects of the present invention. The biocidal raw materials used in the following experimental examples and comparative examples were all dry-pulverized to 1 to 10 μm. Examples 1 to 3 Polyoxyethylene (20 mol) styryl phenyl ether and dioctyl sulfosuccinate are dissolved in water, and a biocide for wood is added and mixed. The mixing ratio was as follows. Biocidal active substance 30% by weight Polyoxyethylene (20 mol) - styryl phenyl ether 4 Dioctylsulfosuccinate Water Remainder 350 g of this mixture and 1000 g of crushed media (glass beads 1 mm φ) were milled in a pearl mill (90 mm φ x 160 mmh) with an inner capacity of 1. ) and pulverized and mixed at a circumferential speed of 4 m/sec for a predetermined period of time. The biocidal drug substance used and the grinding time were as follows.

【表】 得られた各水性懸濁物の調製直後のもの、及び
45℃で30日間保存したものを水に希釈し、殺生原
体粒子の沈降度を測定した。 比較例 1〜3 上記実施例における混合物の粉砕時間を、
BCMは0.5時間(比較例1)、TBZは1時間(比
較例2)、TPNは3時間(比較例3)とした他は
実施例1〜3と同様にして水性懸濁組成物を調製
し、同様に殺生原体の沈降度を測定した。 比較例 4〜6 実施例1〜3の配合において水を5%減らし、
その代りにエチレングリコールモノメチルエーテ
ルを加えた他は全く同様にして粉砕・混合を行な
つた。 殺生原体 30重量% ポリオキシエチレン(20モル)−スチリルフエニ
ルエーテル 4 〃 ジオクチルスルホサクシネート 1 〃 エチレングリコールモノメチルエーチル5 〃 水 残部 殺生原体としてBCMを用いたものを比較例4、
TBZを用いたものを比較例5、TPNを用いたも
のを比較例6とし、同様に水希釈後の殺生原体の
沈降度を調べた。 比較例 7、8 実施例1〜3の配合に準じ、下記の殺生原体及
び粉砕時間を採用した他は同様にして水性懸濁物
を調製し、同様にして殺生原体の沈降度を調べ
た。
[Table] Immediately after preparation of each obtained aqueous suspension, and
The samples stored at 45°C for 30 days were diluted with water, and the degree of sedimentation of the biocidal drug particles was measured. Comparative Examples 1 to 3 The grinding time of the mixture in the above examples was
Aqueous suspension compositions were prepared in the same manner as in Examples 1 to 3, except that BCM was used for 0.5 hours (Comparative Example 1), TBZ was used for 1 hour (Comparative Example 2), and TPN was used for 3 hours (Comparative Example 3). Similarly, the degree of sedimentation of the biocidal drug substance was measured. Comparative Examples 4 to 6 In the formulations of Examples 1 to 3, water was reduced by 5%,
Grinding and mixing were carried out in exactly the same manner except that ethylene glycol monomethyl ether was added instead. Biocidal drug substance 30% by weight Polyoxyethylene (20 mol) - styryl phenyl ether 4 〃 Dioctylsulfosuccinate 1 〃 Ethylene glycol monomethyl ethyl 5 〃 Water Balance Comparative example 4 using BCM as biocidal drug substance
Comparative Example 5 used TBZ and Comparative Example 6 used TPN, and the degree of sedimentation of the biocidal drug substance after dilution with water was similarly examined. Comparative Examples 7 and 8 Aqueous suspensions were prepared in the same manner as in Examples 1 to 3, except that the following biocide drug substance and grinding time were used, and the degree of sedimentation of the biocide drug substance was examined in the same manner. Ta.

〔殺生原体の平均粒径〕[Average particle size of biocidal drug substance]

粒度分布測定器SA−CP2型(島津製作所製)
で測定。 〔殺生原体の真比重〕 JIS K 0061−78(化学製品の比重測定法)に
準じて測定。 〔分散媒に対する殺生原体の溶解度〕 各分散媒(100重量部)に平均粒径1〜10μm
の各殺生原体(1重量部)を加え、25℃で24時間
撹拌した後更に24時間静置する。この一部を遠心
分離器(10000RPM、1時間)にかけて上澄液の
殺生原体濃度を測定し、これを分散媒に対する殺
生原体の溶解度とする。 〔水希釈時の殺生原体の沈降度〕 得られた各水性懸濁組成物1重量部を300重量
部の水に希釈し、200mlの栓付メスシリンダーに
200ml入れて7日間放置した後、希釈液層の間位
置(メスシリンダーの100mlの位置)の希釈液を
採取して殺生原体の濃度を測定し、次式により沈
降度を求める。 沈降度(%)=100−{7日間放置後の希釈液中間
部の殺生原体濃度/水希釈直後の殺生原体濃度×100}
Particle size distribution analyzer model SA-CP2 (manufactured by Shimadzu Corporation)
Measured in. [True specific gravity of biocidal substance] Measured according to JIS K 0061-78 (Method for measuring specific gravity of chemical products). [Solubility of biocidal drug substance in dispersion medium] Average particle size of 1 to 10 μm in each dispersion medium (100 parts by weight)
Each biocidal active substance (1 part by weight) was added thereto, stirred at 25°C for 24 hours, and then allowed to stand for an additional 24 hours. A portion of this is centrifuged (10,000 RPM, 1 hour), and the concentration of the biocide drug substance in the supernatant is measured, and this is taken as the solubility of the biocide drug substance in the dispersion medium. [Sedimentation degree of biocidal drug substance when diluted with water] 1 part by weight of each of the obtained aqueous suspension compositions was diluted with 300 parts by weight of water, and poured into a 200 ml graduated cylinder with a stopper.
After adding 200 ml and leaving it for 7 days, collect the diluted liquid between the diluted liquid layers (the 100 ml position of the measuring cylinder), measure the concentration of the biocidal substance, and calculate the degree of sedimentation using the following formula. Sedimentation degree (%) = 100 - {Concentration of the biocidal drug substance in the middle part of the diluted solution after standing for 7 days / Concentration of the biocidal drug substance immediately after dilution with water x 100}

【表】【table】

【表】 (A):調製直後品
(B):45℃、30日間保存品
第1表の結果より次の様に考察することができ
る。 実施例1〜3は何れも本発明で規定する要件を
すべて満たしているので、調製直後のものはもと
より、45℃で30日間保存した後のものであつても
水希釈液の沈降度は5%以下と極めて低く、優れ
た分散安定性が得られている。 比較例1〜3は何れも殺生原体の粉砕が不十分
であつて、(平均粒径×真比重)の値が0.8を越え
ている為、調製直後のものでも水希釈液の沈降度
が高く分散安定性が悪い。 比較例4〜8は分散媒に対する殺生原体の溶解
度が50ppmを越える比較例であり、調製直後品の
水希釈液の分散安定性は良好であるが、製剤後の
保存時に殺生原体粒子が肥大化し、これを水希釈
した場合の分散安定性は極端に悪くなつている。
[Table] (A): Immediately prepared product
(B): Product stored at 45℃ for 30 days From the results in Table 1, the following can be considered. Since Examples 1 to 3 all meet all the requirements stipulated by the present invention, the sedimentation degree of the water diluted solution is 5 even when it is immediately prepared or after being stored at 45°C for 30 days. % or less, and excellent dispersion stability has been obtained. In all of Comparative Examples 1 to 3, the biocidal active substance was insufficiently pulverized, and the value of (average particle size x true specific gravity) exceeded 0.8, so the degree of sedimentation of the water diluted solution was low even immediately after preparation. high and poor dispersion stability. Comparative Examples 4 to 8 are comparative examples in which the solubility of the biocide drug substance in the dispersion medium exceeds 50 ppm, and the dispersion stability of the water diluted solution of the product immediately after preparation is good, but the biocide drug substance particles are removed during storage after formulation. It becomes enlarged, and when diluted with water, the dispersion stability becomes extremely poor.

Claims (1)

【特許請求の範囲】[Claims] 1 水系分散媒中に木材保護用殺生原体を有効成
分として懸濁状に分散させてなる水性懸濁状木材
保護組成物であつて、前記木材保護用殺生原体
は、常温において固体で前記水系分散媒に対する
溶解度が50ppm以下であり、且つ真比重と平均粒
子径(単位:μm)の積が0.8(μm)以下である
ことを特徴とする水性懸濁状木材保護組成物。
1 An aqueous suspended wood protection composition comprising a biocide active ingredient for wood protection dispersed as an active ingredient in an aqueous dispersion medium, wherein the biocide active ingredient for wood protection is solid at room temperature and An aqueous suspension wood protection composition having a solubility in an aqueous dispersion medium of 50 ppm or less, and a product of true specific gravity and average particle diameter (unit: μm) of 0.8 (μm) or less.
JP16016983A 1983-08-30 1983-08-30 Aqueous suspending wood protective composition Granted JPS60155403A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP16016983A JPS60155403A (en) 1983-08-30 1983-08-30 Aqueous suspending wood protective composition

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP16016983A JPS60155403A (en) 1983-08-30 1983-08-30 Aqueous suspending wood protective composition

Publications (2)

Publication Number Publication Date
JPS60155403A JPS60155403A (en) 1985-08-15
JPH0337483B2 true JPH0337483B2 (en) 1991-06-05

Family

ID=15709343

Family Applications (1)

Application Number Title Priority Date Filing Date
JP16016983A Granted JPS60155403A (en) 1983-08-30 1983-08-30 Aqueous suspending wood protective composition

Country Status (1)

Country Link
JP (1) JPS60155403A (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6163601A (en) * 1984-09-05 1986-04-01 Kao Corp Finely granulated destroying substance, its production, and suspended agricultural chemical preparation containing same
JPH02279611A (en) * 1989-04-20 1990-11-15 Nippon Oil & Fats Co Ltd Preparation of bordeaux mixture
CA2521872C (en) 2003-04-09 2010-11-30 Osmose, Inc. Micronized wood preservative formulations
DE602004022171D1 (en) 2003-06-17 2009-09-03 Phibrowood Llc PARTICULATE WOOD PROTECTION AGENT AND METHOD OF MANUFACTURE THEREOF
US20050252408A1 (en) 2004-05-17 2005-11-17 Richardson H W Particulate wood preservative and method for producing same
US20060112850A1 (en) 2004-10-14 2006-06-01 Jun Zhang Micronized wood preservative formulations in organic carriers

Also Published As

Publication number Publication date
JPS60155403A (en) 1985-08-15

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