JP3311339B1 - Echinoderm exterminator and echinoderm extermination method - Google Patents

Echinoderm exterminator and echinoderm extermination method

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Publication number
JP3311339B1
JP3311339B1 JP2001054155A JP2001054155A JP3311339B1 JP 3311339 B1 JP3311339 B1 JP 3311339B1 JP 2001054155 A JP2001054155 A JP 2001054155A JP 2001054155 A JP2001054155 A JP 2001054155A JP 3311339 B1 JP3311339 B1 JP 3311339B1
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Japan
Prior art keywords
echinoderms
calcium oxide
particles
mass
range
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 - Fee Related
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JP2001054155A
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Japanese (ja)
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JP2002255713A (en
Inventor
伸幸 西野
敏昭 河内
洋 在田
高行 渡辺
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Ube Material Industries Ltd
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Ube Material Industries Ltd
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Abstract

【要約】 【課題】 棘皮動物を除く海洋底生生物に悪影響を与え
ることなく、持続的にその生息領域から棘皮動物を駆除
することができる棘皮動物の駆除剤、及び海洋底生生物
の生息領域から棘皮動物を駆除する方法を提供するこ
と。 【解決手段】 酸化カルシウムを10〜75質量%の範
囲内の量で含む、酸化マグネシウムと酸化カルシウムと
の焼結体粒子からなる棘皮動物駆除剤、及び棘皮動物駆
除剤を海洋底生生物の生息領域(珊瑚礁1)又はその周
囲に配置する、あるいは海洋底生生物の生息領域(珊瑚
礁1)の周囲に配置した後、その生息領域に生息してい
る棘皮動物を駆除する棘皮動物の駆除方法。
Kind Code: A1 Abstract: A pesticidal agent capable of continuously exterminating echinoderms from its habitat without adversely affecting marine benthic organisms other than echinoderms, and a habitat for marine benthic organisms To provide a method for controlling echinoderms from creatures. SOLUTION: An echinoderm exterminator comprising sintered particles of magnesium oxide and calcium oxide containing calcium oxide in an amount in the range of 10 to 75% by mass, and an echinoderm exterminator inhabiting marine benthic organisms. A method for controlling echinoderms, which is arranged at or around an area (coral reef 1) or around an area where marine benthic organisms inhabit (coral reef 1), and then exterminates echinoderms that inhabit the area.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、海洋底生生物の生
息領域から棘皮動物を駆除する方法、及びその駆除に適
した組成物に関するものである。
The present invention relates to a method for controlling echinoderms from the habitat of marine benthic organisms, and to a composition suitable for controlling the same.

【0002】[0002]

【従来の技術】藻場、海洋底生動物(例;アサリやホタ
テ貝)の養殖場あるいは珊瑚礁では、ヒトデやウニなど
の棘皮動物による食害が問題となっている。このため、
棘皮動物を除く海洋底生生物に悪影響を与えることな
く、藻場、海洋底生動物の養殖場あるいは珊瑚礁から棘
皮動物を駆除する方法の研究が行われている。
2. Description of the Related Art In seaweed beds, marine benthic animal (eg, clams and scallops) farms and coral reefs, feeding damage by echinoderms such as starfish and sea urchins has become a problem. For this reason,
Research has been conducted on methods of controlling echinoderms from seagrass beds, marine benthic animal farms or coral reefs without adversely affecting marine benthic organisms other than echinoderms.

【0003】北水試月報第30巻第11号(昭和48年
11月30日発行)には、石灰や消石灰などの強アルカ
リ性の石灰類がヒトデ類やウニ類に対し優れた殺傷効果
を有することが報告されている。この研究報告によれ
ば、消石灰0.4gをヒトデ類に付着させると、高い確
率でヒトデを斃死させることができるとされている。
[0003] In the North Water Trial Monthly Vol. 30, No. 11 (issued on November 30, 1973), strongly alkaline limes such as lime and slaked lime have an excellent killing effect on starfish and sea urchins. It has been reported. According to this research report, if 0.4 g of slaked lime is attached to starfish, the starfish can be killed with a high probability.

【0004】石灰や消石灰などの強アルカリ性の石灰類
は、ヒトデ類やウニ類などの棘皮動物の駆除に有効であ
ると考えられる。しかし、消石灰や生石灰が海底に散布
されるとその周囲は、温度とpHとが急激に高くなる。
従って、消石灰や生石灰を海底に散布する際には、充分
に棘皮動物以外の海洋底生生物への影響を配慮しなけれ
ばならない。また、消石灰や生石灰は海水中で難溶性の
炭酸カルシウムに変化するため、ヒトデ類の殺傷効果が
一時的であるという問題もある。
[0004] Strongly alkaline limes such as lime and slaked lime are considered to be effective in controlling echinoderms such as starfish and sea urchins. However, when slaked lime or quick lime is sprayed on the seabed, the temperature and pH around the lime rapidly increase.
Therefore, when spraying slaked lime or quicklime onto the seabed, it is necessary to sufficiently consider the effects on marine benthic organisms other than echinoderms. Also, slaked lime and quicklime change into calcium carbonate, which is hardly soluble in seawater, so that there is a problem that the effect of killing starfish is temporary.

【0005】[0005]

【発明が解決しようとする課題】本発明の目的は、棘皮
動物を除く海洋底生生物に悪影響を与えることなく、持
続的にその生息領域から棘皮動物を駆除することができ
る棘皮動物の駆除剤、及び海洋底生生物の生息領域から
棘皮動物を駆除する方法を提供することにある。
SUMMARY OF THE INVENTION It is an object of the present invention to control echinoderms which can continuously eradicate echinoderms from their habitat without adversely affecting marine benthic organisms other than echinoderms. And methods of controlling echinoderms from habitats of marine benthic organisms.

【0006】[0006]

【課題を解決するための手段】本発明は、酸化カルシウ
ムを10〜75質量%の範囲内の量で含む、酸化マグネ
シウムと酸化カルシウムとの焼結体粒子からなる棘皮動
物駆除剤にある。本発明の棘皮動物駆除剤は、棘皮動物
の中でもヒトデ類及びウニ類、特にヒトデ類に対して有
効である。
SUMMARY OF THE INVENTION The present invention resides in an echinodermic pesticide comprising sintered particles of magnesium oxide and calcium oxide, containing calcium oxide in an amount in the range of 10 to 75% by mass. The echinodermic control agent of the present invention is effective against starfishes and sea urchins, especially starfishes, among echinoderms.

【0007】本発明の棘皮動物駆除剤において、焼結体
粒子の90質量%以上は、0.1〜500mmの範囲内
の大きさにあることが好ましく、また、焼結体粒子の嵩
密度は1.0〜3.5g/cm3の範囲内にあることが
好ましい。また、本発明の棘皮動物駆除剤においては、
焼結体粒子がそれぞれ分離していてもよいし、複数個の
焼結体粒子が結着剤により塊状に結合していてもよい。
In the pesticidal composition of the present invention, 90% by mass or more of the sintered particles are preferably in a size of 0.1 to 500 mm, and the bulk density of the sintered particles is preferably 0.1 to 500 mm. It is preferably in the range of 1.0 to 3.5 g / cm 3 . Further, in the echinoderma pesticide of the present invention,
The sintered body particles may be separated from each other, or a plurality of sintered body particles may be bound in a lump by a binder.

【0008】本発明はまた、下記(1)〜(3)の棘皮
動物の駆除方法にもある。
[0008] The present invention also provides a method for controlling echinoderms of the following (1) to (3).

【0009】(1)海洋底生生物の生息領域に、酸化カ
ルシウムを10〜75質量%の範囲内の量で含む、酸化
マグネシウムと酸化カルシウムとの焼結体粒子を配置す
る棘皮動物の駆除方法。
(1) A method for controlling echinoderms in which sintered particles of magnesium oxide and calcium oxide containing calcium oxide in an amount in the range of 10 to 75% by mass is arranged in the habitat of marine benthic organisms. .

【0010】(2)海洋底生生物の生息領域とその周囲
に、酸化カルシウムを10〜75質量%の範囲内の量で
含む、酸化マグネシウムと酸化カルシウムとの焼結体粒
子を配置する棘皮動物の駆除方法。
(2) Echinoderms in which sintered particles of magnesium oxide and calcium oxide containing calcium oxide in an amount within the range of 10 to 75% by mass are arranged in and around the habitat of marine benthic organisms. How to get rid of.

【0011】(3)海洋底生生物の生息領域の周囲に、
酸化カルシウムを10〜75質量%の範囲内の量で含
む、酸化マグネシウムと酸化カルシウムとの焼結体粒子
を配置し、次いで、該海洋底生生物の生息領域に生息す
る棘皮動物を駆除する棘皮動物の駆除方法。
(3) Around the habitat of marine benthic organisms,
Echinoderm, comprising sintering particles of magnesium oxide and calcium oxide containing calcium oxide in an amount in the range of 10 to 75% by mass, and then exterminating echinoderms living in the habitat of the marine benthic organisms How to get rid of animals.

【0012】上記本発明の棘皮動物の駆除方法におい
て、海洋底生生物の生息領域とは、例えば、藻場、海洋
底生動物(例;アサリやホタテ貝など貝類)の養殖場あ
るいは珊瑚礁をいう。また、配置するとは散布、又は設
置もしくは設置固定することをいう。
In the echinoderm extermination method of the present invention, the habitat of a marine benthic organism means, for example, a seaweed bed, a cultivation ground for marine benthic animals (eg, clams such as clams and scallops) or a coral reef. . In addition, to dispose means to spray, or to install or fix.

【0013】[0013]

【発明の実施の形態】本発明の棘皮動物駆除剤において
は、酸化カルシウムを10〜75質量%の範囲内で含
む、酸化マグネシウムと酸化カルシウムとの焼結体粒子
(以下、MgO−CaO焼結体粒子という)から溶出す
る酸化カルシウム(アルカリ成分)によって棘皮動物の
駆除(忌避)効果が発揮される。このMgO−CaO焼
結体に含まれる酸化カルシウム量は好ましくは20〜6
5質量%の範囲内、より好ましくは35〜65質量%の
範囲内である。
BEST MODE FOR CARRYING OUT THE INVENTION In the echinodermic pesticide of the present invention, sintered particles of magnesium oxide and calcium oxide (hereinafter referred to as MgO-CaO sintered) containing calcium oxide in a range of 10 to 75% by mass. Calcium oxide (alkaline component) eluted from the body particles) exerts an eradication (repellent) effect on echinoderms. The amount of calcium oxide contained in the MgO-CaO sintered body is preferably 20 to 6
It is in the range of 5% by mass, more preferably in the range of 35 to 65% by mass.

【0014】本発明のMgO−CaO焼結体粒子では、
酸化カルシウムが主に酸化マグネシウム結晶(ペリクレ
ース結晶)粒間に存在する。このため、MgO−CaO
焼結体粒子は、生石灰や消石灰と比較して酸化カルシウ
ムの溶出量が少なくなる。従って、MgO−CaO焼結
体粒子を海底に散布しても、生石灰や消石灰の場合と比
較して、その周囲の環境の変化(温度やpHの上昇)が
小さくなる。また、酸化マグネシウム結晶粒間に存在す
る酸化カルシウムは、炭酸カルシウムに変化しにくい。
従って、MgO−CaO焼結体粒子は、持続的に酸化カ
ルシウムを溶出する。
In the MgO-CaO sintered particles of the present invention,
Calcium oxide mainly exists between magnesium oxide crystal (periclase crystal) grains. For this reason, MgO-CaO
The amount of calcium oxide eluted from the sintered particles is smaller than that of quicklime or slaked lime. Therefore, even if the MgO-CaO sintered particles are sprayed on the seabed, changes in the surrounding environment (temperature and pH rise) are smaller than in the case of quick lime or slaked lime. In addition, calcium oxide existing between magnesium oxide crystal grains is not easily changed to calcium carbonate.
Therefore, the MgO—CaO sintered body particles continuously elute calcium oxide.

【0015】本発明のMgO−CaO焼結体粒子として
は、天然のドロマイトを焼成して得られる天然ドロマイ
トクリンカ、あるいは酸化マグネシウム原料(例、水酸
化マグネシウム)と酸化カルシウム原料(例、水酸化カ
ルシウム)とを混合し、焼成して得たマグネシア・カル
シアクリンカ(マグライムクリンカともいう)を有利に
用いることができる。また、鉄成分(Fe23)を酸化
マグネシウム結晶中に固溶させた鉄成分含有マグネシア
・カルシアクリンカも好ましく用いることができる。鉄
成分含有マグネシア・カルシアクリンカーは、酸化カル
シウムの溶出量は少ないが、その分長期間にわたって酸
化カルシウムを溶出するので、棘皮動物の駆除効果が長
期間持続する。鉄成分含有マグネシア・カルシアクリン
カを用いる場合、鉄成分量が0.2〜5質量%の範囲内
にあることが好ましい。鉄成分含有マグネシア・カルシ
アクリンカは、鉄成分を含む水酸化マグネシウムと水酸
化カルシウムとを混合し、焼成することにより製造する
ことができる(特公平1−38072号参照)。
The MgO—CaO sintered particles of the present invention include natural dolomite clinker obtained by calcining natural dolomite, or a raw material of magnesium oxide (eg, magnesium hydroxide) and a raw material of calcium oxide (eg, calcium hydroxide). And magnesia calcia clinker (also referred to as maglime clinker) obtained by mixing and calcining can be advantageously used. Further, magnesia calcia clinker containing an iron component in which an iron component (Fe 2 O 3 ) is dissolved in magnesium oxide crystals can also be preferably used. Magnesia calcia clinker containing an iron component elutes a small amount of calcium oxide, but elutes calcium oxide over a long period of time, so that the eradication effect of echinoderms is maintained for a long time. When using a magnesia calcia clinker containing an iron component, the amount of the iron component is preferably in the range of 0.2 to 5% by mass. Magnesia calcia clinker containing an iron component can be produced by mixing magnesium hydroxide containing an iron component and calcium hydroxide and firing the mixture (see Japanese Patent Publication No. 1-38072).

【0016】本発明のMgO−CaO焼結体粒子は、篩
などの通常の分級装置にて、その90質量%以上が、
0.1〜500mmの範囲内(好ましくは1〜100m
mの範囲内)となるようにすることが好ましい。
The sintered particles of the MgO-CaO of the present invention have 90% by mass or more in a usual classifier such as a sieve.
Within the range of 0.1 to 500 mm (preferably 1 to 100 m
m).

【0017】本発明のMgO−CaO焼結体粒子の嵩密
度は、1〜3.5g/cm3の範囲内にあることが好ま
しく、より好ましくは2〜3.5g/cm3の範囲内で
ある。
The bulk density of the MgO-CaO sintered particles [0017] The present invention is preferably in the range of 1~3.5g / cm 3, more preferably in the range of 2~3.5g / cm 3 is there.

【0018】本発明の棘皮動物駆除剤は、複数個のMg
O−CaO焼結体粒子を結着剤にて結合させて塊状にし
て用いても良い。このMgO−CaO焼結体粒子塊状物
の形状としては、例えば、球形状、アーモンド形状、立
方形状、四脚ブロック形状を挙げることができる。ま
た、軽量化を目的として、MgO−CaO焼結体粒子塊
状物の内部を中空にしたり、生分解性の樹脂を内部に充
填することもできる。
The echinodermic pesticide of the present invention comprises a plurality of Mg
O-CaO sintered particles may be combined with a binder and used as a lump. Examples of the shape of the MgO-CaO sintered body particle aggregate include a spherical shape, an almond shape, a cubic shape, and a quadruped block shape. In addition, for the purpose of weight reduction, the inside of the MgO—CaO sintered body particle aggregate can be made hollow or a biodegradable resin can be filled inside.

【0019】MgO−CaO焼結体粒子塊状物に用いる
結着剤の例としては、セメント(例;マグネシアセメン
ト)などの無機物、及び生分解性樹脂などの樹脂を挙げ
ることができる。MgO−CaO焼結体粒子と結着剤と
の配合割合は、通常、MgO−CaO焼結体粒子が70
〜90質量%(好ましくは75〜85質量%)、結着剤
が30〜10質量%(好ましくは25〜15質量%)で
ある。
Examples of the binder used for the MgO-CaO sintered body particle aggregate include inorganic substances such as cement (eg, magnesia cement) and resins such as biodegradable resins. The mixing ratio of the MgO-CaO sintered particles and the binder is usually 70% for the MgO-CaO sintered particles.
90 to 90% by mass (preferably 75 to 85% by mass), and the binder is 30 to 10% by mass (preferably 25 to 15% by mass).

【0020】MgO−CaO焼結体粒子塊状物は、さら
に所望により、水酸化マグネシウム、水酸化カルシウム
などのアルカリ剤を含んでいてもよい。
The MgO—CaO sintered body particle aggregate may further contain an alkali agent such as magnesium hydroxide or calcium hydroxide, if desired.

【0021】次に、ヒトデによる食害が問題となってい
る珊瑚礁を例に取り、本発明の棘皮動物駆除剤を用いた
棘皮動物の駆除方法について、添付図面を参照しながら
説明する。
Next, a method for controlling echinoderms using the echinoderma pesticide of the present invention will be described with reference to the accompanying drawings, taking, as an example, a coral reef, which is a problem of starvation by starfish.

【0022】図1は、珊瑚礁が形成されている海域を海
上から見た概念図である。この図1の海域3では、珊瑚
礁1が陸地4から離れた沖合に形成されている。
FIG. 1 is a conceptual diagram of a sea area where a coral reef is formed as viewed from the sea. In the sea area 3 of FIG. 1, the coral reef 1 is formed offshore away from the land 4.

【0023】珊瑚礁1からヒトデを駆除する方法として
は、まず、本発明の棘皮動物駆除剤を珊瑚礁1に直接散
布する方法がある。珊瑚礁1に散布する駆除剤の量は、
珊瑚や棘皮動物を除く海洋底生生物に対して悪影響を与
えない範囲であれば特に制限はない。通常は、海底の面
積1m2当たり10〜1000gの範囲内とする。駆除
剤の散布方法に特には制限はなく、例えば、海面に散布
してもよい。駆除剤は、珊瑚礁1の中央から外側方向に
向かって順に散布し、ヒトデを珊瑚礁1から追い出すよ
うにするのがよい。
As a method for controlling starfish from the coral reef 1, there is a method in which the echinoderma pesticide of the present invention is directly sprayed on the coral reef 1. The amount of pesticide sprayed on coral reef 1
There is no particular limitation as long as it has no adverse effect on marine benthic organisms other than corals and echinoderms. Usually, it is in the range of 10 to 1000 g per 1 m 2 of seabed area. There is no particular limitation on the method of spraying the pesticide, and for example, it may be sprayed on the sea surface. The pesticide is preferably sprayed in order from the center of coral reef 1 toward the outside so that the starfish is expelled from coral reef 1.

【0024】駆除剤の散布により珊瑚礁1に生息してい
るヒトデを駆除した後、さらに、珊瑚礁1の周囲(以
下、境界区域という)2にも駆除剤を散布し、珊瑚礁1
に外部からヒトデが侵入しないようにすることが好まし
い。境界区域2には、駆除剤を珊瑚礁1よりも多量に散
布しておくことが好ましい。境界区域2に散布する駆除
剤の量は、境界区域2の海底の面積1m2当たり100
g以上、好ましくは1000g〜5000gの範囲内で
ある。境界区域2の幅に特別な制限はないが、ヒトデの
侵入防止効果と散布のための手間とを考えると、通常は
1〜10mの範囲内である。
After the starfish inhabiting the coral reef 1 has been exterminated by spraying the pesticide, the pesticide is further sprayed around the coral reef 1 (hereinafter referred to as a boundary area) 2 to thereby remove the coral reef 1.
It is preferable to prevent starfish from entering the outside. It is preferable that the pesticide is applied to the boundary area 2 in a larger amount than the coral reef 1. The amount of the pesticide applied to the boundary area 2 is 100 per m 2 of the seabed area of the boundary area 2.
g or more, preferably in the range of 1000 g to 5000 g. The width of the boundary area 2 is not particularly limited, but is usually in the range of 1 to 10 m in consideration of the effect of preventing starfish invasion and the time required for spraying.

【0025】珊瑚礁1からヒトデを駆除する別の方法と
して、まず境界区域(珊瑚礁1の周囲)2の海底に駆除
剤を設置し、珊瑚礁1に外部からヒトデが侵入しないよ
うにした後、珊瑚礁1に生息する棘皮動物を捕獲する方
法がある。この方法は、特に珊瑚礁1の水深が深い又は
海水の流れが速いなどの理由により、駆除剤を散布する
のが困難な場合に有効である。この駆除剤を海底に設置
する場合の好ましい配置の例を、添付図面の図2〜図4
に示す。
As another method for controlling starfish from the coral reef 1, a pesticide is first installed on the seabed in the boundary area (around the coral reef 1) 2 so that the starfish does not enter the coral reef 1 from the outside. There is a method to capture echinoderms that live in Japan. This method is effective particularly when it is difficult to spray the pesticide due to the fact that the coral reef 1 has a deep water depth or the seawater flows fast. An example of a preferred arrangement when this pesticide is installed on the sea floor is shown in FIGS.
Shown in

【0026】図2は、駆除剤(図示せず)を入れた網袋
5がアンカー6にて設置固定された海底7を示す図であ
る。網袋5の大きさには特別な制限はない。例えば、海
底に設置した時の網袋の長さ方向(珊瑚礁を囲む方向)
の長さが100m以上であってもよい。
FIG. 2 is a view showing a seabed 7 on which a mesh bag 5 containing a pesticide (not shown) is installed and fixed by an anchor 6. There is no particular limitation on the size of the mesh bag 5. For example, the length direction of the net bag when installed on the sea floor (the direction surrounding the coral reef)
May be 100 m or longer.

【0027】図3及び図4に、塊状に形成された駆除剤
を海底に設置した例を示す。
FIG. 3 and FIG. 4 show examples in which a massively formed pesticide is installed on the sea floor.

【0028】図3は、立方形状に形成された駆除剤8が
二段に積み上げられて設置されている海底7を示す図で
ある。立方形状の駆除剤8を海底7に設置することによ
り、駆除剤同士の隙間を少なくすることができる。
FIG. 3 is a view showing the seabed 7 on which the pesticides 8 formed in a cubic shape are stacked and installed in two stages. By installing the cubic pesticide 8 on the seabed 7, the gap between the pesticides can be reduced.

【0029】図4は、直径が相対的に大きい球形状の駆
除剤9と直径が相対的に小さい球形状の駆除剤10とが
交互に設置されている海底7を示す図である。直径の異
なる球形状の駆除剤を海底7に設置することにより、駆
除剤同士の隙間を小さくすることができる。
FIG. 4 is a diagram showing the seabed 7 in which spherical pesticides 9 having a relatively large diameter and spherical pesticides 10 having a relatively small diameter are alternately provided. By installing spherical pesticides having different diameters on the seabed 7, the gap between the pesticides can be reduced.

【0030】なお、図1においては沖合に形成された珊
瑚礁を例に取り説明したが、沿岸に生成された珊瑚礁の
場合には、図5に示すように、陸地4の形状を利用する
ことも可能である。
Although FIG. 1 has been described taking coral reefs formed offshore as an example, in the case of coral reefs generated along the coast, as shown in FIG. 5, the shape of land 4 may be used. It is possible.

【0031】本発明の棘皮動物駆除剤は、公知である他
の湖底もしくは海底の化学的環境の改質剤(以下、底質
改質剤という)と併用することができる。本発明の棘皮
動物駆除剤と併用できる公知の底質改質剤の例として
は、宇部マテリアルズ(株)から販売されているクリア
ウォーター(水酸化マグネシウムを主成分とする底質改
善剤)、クリアウォーターH(酸化マグネシウムを主成
分とする底質改善剤)、及びカルサンマリン(酸化カル
シウムを主成分とする底質改善剤)などの湖底もしくは
海底の土壌をアルカリ性にし、土壌中の堆積有機物の分
解を促進するものを挙げることができる。
The echinoderma pesticide of the present invention can be used in combination with other known chemical modifiers of lake or sea bottom chemical environment (hereinafter referred to as sediment modifiers). Examples of known sediment modifying agents that can be used in combination with the echinoderma pesticide of the present invention include clear water (a sediment improving agent mainly composed of magnesium hydroxide) sold by Ube Materials Co., Ltd. Lake bottom or sea bottom soil such as Clearwater H (a bottom sediment improver mainly composed of magnesium oxide) and calsanmarine (a bottom sediment improver mainly composed of calcium oxide) is made alkaline to remove sedimentary organic matter in the soil. Those that promote decomposition can be mentioned.

【0032】[0032]

【実施例】以下、本発明を実施例に基づいて具体的に説
明するが、これらは本発明を限定するものではない。な
お、実施例に記載の嵩密度は次のようにして測定した値
である。
EXAMPLES Hereinafter, the present invention will be described specifically with reference to Examples, but these do not limit the present invention. The bulk density described in the examples is a value measured as follows.

【0033】日本学術振興会第124委員会試験法分科
会において決定された「学振法2.マグネシアクリンカ
の見掛け気孔率、見掛け密度及び嵩比重の測定方法」
(1981年版耐火物手帳、耐火物技術協会発行)に準
じて行い、下記の計算式を用いて算出した。
"JSPS 2. Measuring method of apparent porosity, apparent density and bulk density of magnesia clinker" determined by the 124th Committee of the Japan Society for the Promotion of Science
(Refractory Handbook, 1981 Edition, published by The Japan Refractory Technical Association) and calculated using the following formula.

【0034】 嵩密度(g/cm3)=W1/(W3−W2)×S W1:試料の乾燥重量 W2:ケロシンで飽和した試料のケロシン中での重量
(g) W3:ケロシンで飽和した試料の重量(g) S:測定温度におけるケロシンの密度(g/cm3
Bulk density (g / cm 3 ) = W 1 / (W 3 −W 2 ) × S W 1 : dry weight of sample W 2 : weight of sample saturated with kerosene in kerosene (g) W 3 : Weight of sample saturated with kerosene (g) S: Density of kerosene at measurement temperature (g / cm 3 )

【0035】[実施例1]脱炭酸処理した海水に、Mg
イオンとFeイオンの比率がFe23/MgO質量換算
で1.2/100となるようにFeSO4水溶液を添加
した。この海水にCa(OH)2スラリを加えてMg
(OH)2を生成させ、これを沈降濃縮し、工業用水に
より洗浄してMg(OH)2スラリを得た。得られたM
g(OH)2スラリとCa(OH)2スラリとを、MgO
/CaO質量換算で40/60となるように混合した。
この混合スラリをろ過、乾燥し固形物を得た。この固形
物を1900℃、30分間の条件で焼成しMgO−Ca
O焼結体粒子とした。このMgO−CaO焼結体粒子を
目開き3mmと10mmの篩を用いて分級し、粒子径3
〜10mmのMgO−CaO焼結体粒子を得た。得られ
たMgO−CaO焼結体粒子の嵩密度及び化学組成を表
1に示す。
Example 1 Decarbonated seawater was mixed with Mg
An aqueous solution of FeSO 4 was added so that the ratio of ions to Fe ions was 1.2 / 100 in terms of the mass of Fe 2 O 3 / MgO. Add Ca (OH) 2 slurry to this seawater and add Mg
(OH) 2 was produced, which was precipitated and concentrated, and washed with industrial water to obtain a Mg (OH) 2 slurry. M obtained
g (OH) 2 slurry and Ca (OH) 2 slurry
/ 40/60 in terms of CaO mass.
The mixed slurry was filtered and dried to obtain a solid. This solid is fired at 1900 ° C. for 30 minutes to obtain MgO—Ca.
O sintered compact particles were obtained. The MgO—CaO sintered particles were classified using a sieve having an opening of 3 mm and a sieve having a diameter of 10 mm.
MgO-CaO sintered particles of 10 mm to 10 mm were obtained. Table 1 shows the bulk density and chemical composition of the obtained MgO-CaO sintered particles.

【0036】[0036]

【表1】 表1 ────────────────────────────── 嵩密度(g/cm3) 3.40 ────────────────────────────── 化学組成(%) MgO 38.49 CaO 60.31 Fe23 0.39 SiO2 0.10 Al23 0.076 B23 0.024 ──────────────────────────────Table 1 {Bulk density (g / cm 3 ) 3.40} ─────────────────────────── Chemical composition (%) MgO 38.49 CaO 60.31 Fe 2 O 3 0.39 SiO 20 .10 Al 2 O 3 0.076 B 2 O 3 0.024 °

【0037】[評価及び結果]下記の評価モデルを使用
した。 (1)MgO−CaO焼結体粒子に接触したヒトデの挙
動の観察 水槽(幅52cm、奥行き32cm、高さ12cm)に
海水を入れ、水槽の底部四隅に実施例1で製造したMg
O−CaO焼結体粒子を1個ずつ設置した。次いで、水
槽にヒトデを3個体入れた。MgO−CaO焼結体粒子
に接触した後のヒトデの挙動の観察結果を表2に示す。
[Evaluation and Results] The following evaluation model was used. (1) Observation of behavior of starfish in contact with MgO-CaO sintered particles Particles of seawater were placed in a water tank (width 52 cm, depth 32 cm, height 12 cm), and Mg produced in Example 1 was placed at the bottom four corners of the water tank.
O-CaO sintered particles were placed one by one. Next, three starfish were placed in the water tank. Table 2 shows the observation results of the behavior of the starfish after coming into contact with the MgO-CaO sintered body particles.

【0038】参考例として、実施例1で製造したMgO
−CaO焼結体粒子の代わりに、下記(1)〜(3)に
示す市販の底質改善剤を用いた以外は同様の操作を行っ
て、これらに接触した後のヒトデの挙動の観察した。そ
の結果を表2に併せて示す。
As a reference example, the MgO prepared in Example 1 was used.
-The same operation was performed except that the commercially available sediment improving agents shown in the following (1) to (3) were used instead of the CaO sintered body particles, and the behavior of the starfish after contacting them was observed. . The results are also shown in Table 2.

【0039】(1)クリアウォーター(水酸化マグネシ
ウムを主成分とする底質改善剤、宇部マテリアルズ
(株)製) (2)クリアウォーターH(酸化マグネシウムを主成分
とする底質改善剤、宇部マテリアルズ(株)製) (3)カルサンマリン(酸化カルシウムを主成分とする
底質改善剤、宇部マテリアルズ(株)製)
(1) Clearwater (a sediment improving agent containing magnesium hydroxide as a main component, manufactured by Ube Materials Co., Ltd.) (2) Clearwater H (a sediment improving agent containing magnesium oxide as a main component, Ube (3) Calsan marine (a bottom sediment improver containing calcium oxide as a main component, manufactured by Ube Materials Co., Ltd.)

【0040】[0040]

【表2】 表2 ──────────────────────────────────── 試 料 試料に接触した後のヒトデの挙動 ──────────────────────────────────── 実施例1で製造した 直ちに試料から離れ、その後、試料に近づかな MgO−CaO焼結体 かった(試料はヒトデが接触しても崩壊せず) ──────────────────────────────────── 参考例 (1)クリアウォーター 試料の上を歩行するヒトデと、直ちに試料から (水酸化マグネシウムを 離れるヒトデとがあった 主成分とする底質改善剤) (2)クリアウォーターH 試料に接触した状態で留まっていた (酸化マグネシウムを 主成分とする底質改善剤) (3)カルサンマリン 直ちに試料から離れ、その後、試料に近づかな (酸化カルシウムを かった(試料はヒトデが接触した後崩壊した) 主成分とする底質改善剤) ────────────────────────────────────[Table 2] Table 2 ──────────────────────────────────── Sample After contact with sample Starfish behavior 離 れ Immediately separated from the sample produced in Example 1, After that, it was a MgO-CaO sintered body that did not approach the sample (the sample did not collapse even if it came in contact with starfish). ───────────── Reference example (1) Clear water Starfish walking on the sample and starfish immediately leaving the sample (2) Clearwater H stayed in contact with the sample (magnesium oxide-based sediment improving agent) (3) Calsanmarin Away from the sample and then approach the sample (calcium oxide was applied (the sample collapsed after contact with the starfish)). ─────────────────────

【0041】(2)餌(アサリ)を用いたヒトデ忌避効
果の評価 図6に示すように、縦100cm、横200cm、深さ
100cmの水槽11を、仕切板12によって区画Aと
区画Bの二つに区分けした。仕切板12には4cm×4
cmの角材を用いた。区画Aに実施例1で製造したMg
O−CaO焼結体粒子を敷き詰め(図示せず)その上に
アサリ16を20個体置いて、区画Bにはヒトデ17を
7個体とイトマキヒトデ18を3個体入れた。評価中
は、常時海水を区画Aに供給した。区画Aに供給された
海水は、区画Aをオバーフローして区画Bに流れ込み、
区画Bに設けられている排水口15から外部に排出され
る。なお、区画Aにはバケツ14を設置し、ポンプ13
から供給された海水が、バケツ14をオーバーフロして
区画Aに流れ込むようにした。
(2) Evaluation of Starfish Repellent Effect Using Bait (Clam) As shown in FIG. 6, a water tank 11 having a length of 100 cm, a width of 200 cm and a depth of 100 cm is divided into two sections A and B by a partition plate 12. Divided into two. 4 cm x 4 for partition plate 12
cm square wood was used. Mg produced in Example 1 in Section A
Twenty clams 16 were placed on the O-CaO sintered particles (not shown), and seven starfish 17 and three starfish 18 were placed in section B. During the evaluation, seawater was constantly supplied to section A. The seawater supplied to the section A overflows the section A and flows into the section B,
The water is discharged to the outside from the drain port 15 provided in the section B. A bucket 14 is installed in section A, and a pump 13
Was overflowed from the bucket 14 and flowed into the section A.

【0042】ヒトデ及びイトマキヒトデの挙動を三週間
観察したところ、ヒトデ及びイトマキヒトデは区画Aに
は移動できずに、共食いした。この間区画Aに入れたア
サリは全て正常であった。
When the behaviors of the starfish and the starfish were observed for three weeks, the starfish and the starfish could not move to the section A, and ate each other. During this time, all clams placed in section A were normal.

【0043】参考例として、実施例1で製造したMgO
−CaO焼結体粒子の代わりに、クリアウォーター(水
酸化マグネシウムを主成分とする底質改善剤)を用いた
以外は同様の操作を行った。評価開始3日後には、ヒト
デ及びイトマキヒトデが区画Aに移動し、アサリを食し
ていた。
As a reference example, the MgO prepared in Example 1 was used.
-The same operation was performed except that clear water (a bottom quality improving agent containing magnesium hydroxide as a main component) was used instead of the CaO sintered body particles. Three days after the start of the evaluation, the starfish and the starfish moved to the section A and ate clams.

【0044】[実施例2]実施例1で製造したMgO−
CaO焼結体粒子80質量部、マグネシアセメント20
質量部、及びマグネシアセメント100gに対して50
ミリリットルとなる量の塩化マグネシウム溶液(ボーメ
度:25)を混合した。この組成物を型に入れて、5時
間養生し、立方形状のMgO−CaO焼結体粒子塊状物
を得た。得られた塊状物について実施例1と同様に、海
水中でヒトデと接触させた結果、ヒトデは直ちに塊状物
から離れ、その後、試料に近づかなかなった。
Example 2 The MgO— produced in Example 1
80 parts by mass of CaO sintered body particles, magnesia cement 20
50 parts by mass and 100 g of magnesia cement
A milliliter amount of a magnesium chloride solution (degree of Baume: 25) was mixed. This composition was put in a mold and cured for 5 hours to obtain a cubic MgO—CaO sintered body particle aggregate. As a result of contacting the obtained lump with a starfish in seawater in the same manner as in Example 1, the starfish immediately separated from the lump and did not approach the sample.

【0045】[0045]

【発明の効果】本発明の棘皮動物駆除剤は、海水中にお
いて持続的に酸化カルシウム(アルカリ成分)が溶出す
る。従って、本発明の棘皮動物駆除剤を用いることによ
り、棘皮動物から藻場、アサリやホタテ貝などの養殖場
あるいは珊瑚礁を長期間にわたって保護することができ
る。また、本発明の棘皮動物駆除剤は、主成分が海水に
含まれているカルシウムとマグネシウムであるので、海
藻、アサリやホタテ貝などの有用生物及び珊瑚に悪影響
を与えにくい。
EFFECTS OF THE INVENTION The echinoderma pesticide of the present invention elutes calcium oxide (alkaline component) continuously in seawater. Therefore, by using the echinodermic control agent of the present invention, seaweed beds, cultivation sites such as clams and scallops or coral reefs can be protected from echinoderms for a long period of time. In addition, since the echinoderma pesticide of the present invention is mainly composed of calcium and magnesium contained in seawater, it does not easily adversely affect useful organisms such as seaweed, clams and scallops and corals.

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

【図1】珊瑚礁が沖合に形成されている海域を海上から
見た概念図である。
FIG. 1 is a conceptual diagram of a sea area where a coral reef is formed offshore as viewed from the sea.

【図2】本発明の棘皮動物駆除剤が設置されている海底
の一例を示す概念図である。
FIG. 2 is a conceptual diagram showing an example of the seabed on which the echinoderma pesticide of the present invention is installed.

【図3】本発明の棘皮動物駆除剤が設置されている海底
の別の一例を示す概念図である。
FIG. 3 is a conceptual diagram showing another example of the seabed on which the echinoderma pesticide of the present invention is installed.

【図4】本発明の棘皮動物駆除剤が設置されている海底
のさらに別の一例を示す概念図である。
FIG. 4 is a conceptual diagram showing still another example of the seabed on which the echinoderma pesticide of the present invention is installed.

【図5】珊瑚礁が沿岸に形成されている海域を海上から
見た概念図である。
FIG. 5 is a conceptual diagram of a sea area where a coral reef is formed along the coast as viewed from the sea.

【図6】実施例1の評価試験で用いた水槽の平面図であ
る。
FIG. 6 is a plan view of a water tank used in the evaluation test of Example 1.

【符号の説明】[Explanation of symbols]

1 珊瑚礁 2 境界区域 3 海域 4 陸地 5 網袋 6 アンカー 7 海底 8 立方形状の棘皮動物駆除剤 9、10 球形状の棘皮動物駆除剤 11 水槽 12 仕切板 13 ポンプ 14 バケツ 15 排水口 16 アサリ 17 ヒトデ 18 イトマキヒトデ DESCRIPTION OF SYMBOLS 1 Coral reef 2 Boundary area 3 Sea area 4 Land 5 Landing net 6 Anchor 7 Ocean floor 8 Cubic-shaped echinoderm 9,10 Spherical echinoderm 11 Aquarium 12 Partition plate 13 Pump 14 Bucket 15 Drainage port 16 Clam 17 Starfish 18 Starfish

───────────────────────────────────────────────────── フロントページの続き (72)発明者 渡辺 高行 山口県宇部市大字小串1985番地 宇部マ テリアルズ株式会社内 (56)参考文献 特開 昭60−112666(JP,A) 特開 昭58−23608(JP,A) SHUMWAY,S.E.,et.a l.,Effects of calc ium oxide on non−t aeget organismsin mussel beds,Bull.E nviron.Contam.Toxi cal.,1988年,Vol.40,No. 4,pp.503−509 西村昭史・関政夫,養殖漁場改良にお ける石灰の作用,日本水産学会誌,日 本,1983年,Vol.49,No.3,p p.353−358 (58)調査した分野(Int.Cl.7,DB名) A01N 59/06 A01N 25/00 A01N 25/12 CA(STN) REGISTRY(STN) JICSTファイル(JOIS)──────────────────────────────────────────────────続 き Continuation of the front page (72) Inventor Takayuki Watanabe 1985 Kogushi, Oji, Ube City, Yamaguchi Prefecture Inside Ube Materials Co., Ltd. (56) References JP-A-60-112666 (JP, A) JP-A-58- 23608 (JP, A) SHUMWAY, S.M. E. FIG. , Et. a l. , Effects of calcium oxide on non-taeget organismsin musclesel beds, Bull. Environ. Contam. Toxi cal. 1988, Vol. 40, No. 4 pp. 503-509 Akishi Nishimura and Masao Seki, Effects of Lime on Improvement of Aquaculture and Fishing Grounds, Journal of the Fisheries Society of Japan, Japan, 1983, Vol. 49, no. 3, pp. 353-358 (58) Field surveyed (Int. Cl. 7 , DB name) A01N 59/06 A01N 25/00 A01N 25/12 CA (STN) REGISTRY (STN) JICST file (JOIS)

Claims (7)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 酸化カルシウムを10〜75質量%の範
囲内の量で含む、酸化マグネシウムと酸化カルシウムと
の焼結体粒子からなる棘皮動物駆除剤。
1. An ectodermal control agent comprising sintered particles of magnesium oxide and calcium oxide, comprising calcium oxide in an amount in the range of 10 to 75% by mass.
【請求項2】 上記焼結体粒子の90質量%以上が、
0.1〜500mmの範囲内の大きさにあることを特徴
とする請求項1に記載の棘皮動物駆除剤。
2. 90% by mass or more of the sintered body particles are
2. The echinodermic control agent according to claim 1, wherein the size is in the range of 0.1 to 500 mm.
【請求項3】 上記焼結体粒子の嵩密度が1.0〜3.
5g/cm3の範囲内にあることを特徴とする請求項1
に記載の棘皮動物駆除剤。
3. The sintered body particles have a bulk density of 1.0 to 3.
2. The method according to claim 1, wherein the amount is within a range of 5 g / cm 3.
2. The echinoderma pesticide according to item 1.
【請求項4】 複数個の焼結体粒子が、結着剤により塊
状に結合していることを特徴とする請求項1に記載の棘
皮動物駆除剤。
4. The echinodermic control agent according to claim 1, wherein the plurality of sintered body particles are bound in a lump by a binder.
【請求項5】 海洋底生生物の生息領域に、酸化カルシ
ウムを10〜75質量%の範囲内の量で含む、酸化マグ
ネシウムと酸化カルシウムとの焼結体粒子を配置する棘
皮動物の駆除方法。
5. A method for controlling echinoderms, comprising sintering particles of magnesium oxide and calcium oxide containing calcium oxide in an amount in the range of 10 to 75% by mass in a habitat of a marine benthic organism.
【請求項6】 海洋底生生物の生息領域とその周囲に、
酸化カルシウムを10〜75質量%の範囲内の量で含
む、酸化マグネシウムと酸化カルシウムとの焼結体粒子
を配置する棘皮動物の駆除方法。
6. A habitat for marine benthic organisms and its surroundings,
A method for controlling echinoderms comprising sintering particles of magnesium oxide and calcium oxide, comprising calcium oxide in an amount within the range of 10 to 75% by mass.
【請求項7】 海洋底生生物の生息領域の周囲に、酸化
カルシウムを10〜75質量%の範囲内の量で含む、酸
化マグネシウムと酸化カルシウムとの焼結体粒子を配置
し、次いで、該海洋底生生物の生息領域に生息する棘皮
動物を駆除する棘皮動物の駆除方法。
7. Sintered particles of magnesium oxide and calcium oxide containing calcium oxide in an amount in the range of 10 to 75% by mass are arranged around a habitat of a marine benthic organism, A method for controlling echinoderms that exterminates echinoderms that inhabit marine benthic areas.
JP2001054155A 2001-02-28 2001-02-28 Echinoderm exterminator and echinoderm extermination method Expired - Fee Related JP3311339B1 (en)

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JP5535518B2 (en) * 2008-05-01 2014-07-02 宇部マテリアルズ株式会社 Removal method of slime and aqueous slime remover preparation kit
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Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
SHUMWAY,S.E.,et.al.,Effects of calcium oxide on non−taeget organismsin mussel beds,Bull.Environ.Contam.Toxical.,1988年,Vol.40,No.4,pp.503−509
西村昭史・関政夫,養殖漁場改良における石灰の作用,日本水産学会誌,日本,1983年,Vol.49,No.3,pp.353−358

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