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JP2001181117A - Bottom sediment-improving agent and method for improving bottom sediment - Google Patents

Bottom sediment-improving agent and method for improving bottom sediment

Info

Publication number
JP2001181117A
JP2001181117A JP36626399A JP36626399A JP2001181117A JP 2001181117 A JP2001181117 A JP 2001181117A JP 36626399 A JP36626399 A JP 36626399A JP 36626399 A JP36626399 A JP 36626399A JP 2001181117 A JP2001181117 A JP 2001181117A
Authority
JP
Japan
Prior art keywords
sediment
improving
bottom sediment
improving agent
magnesium hydroxide
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.)
Withdrawn
Application number
JP36626399A
Other languages
Japanese (ja)
Inventor
Ryozo Imai
良三 今井
Shingo Hihara
慎吾 日原
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.)
NAIKAI ENGIYOU KK
Original Assignee
NAIKAI ENGIYOU KK
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 NAIKAI ENGIYOU KK filed Critical NAIKAI ENGIYOU KK
Priority to JP36626399A priority Critical patent/JP2001181117A/en
Publication of JP2001181117A publication Critical patent/JP2001181117A/en
Withdrawn legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/80Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in fisheries management
    • Y02A40/81Aquaculture, e.g. of fish

Landscapes

  • Cultivation Of Seaweed (AREA)
  • Farming Of Fish And Shellfish (AREA)
  • Agricultural Chemicals And Associated Chemicals (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a bottom sediment-improving agent capable of improving habitat environment of algae, living things, etc., by improving the bottom sediment of closed sea bottom, moat bottom, etc., to decrease anaerobic bacteria and provide a method for improving the bottom sediment by using the above agent. SOLUTION: This bottom sediment-improving agent is obtained by forming magnesium hydroxide having 30-97% purity into granular, pellet-like or flake-like magnesium hydroxide having a hardness of 0.3-4.0 kg/granule and 2-9 mm particle diameter. The another objective method for improving the bottom sediment comprises spraying the bottom sediment improving agent on to organic substances-rich bottom sediment at a ratio of 100 to 1,000 g/m2 to carry out decomposing treatment of organic substances.

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、閉鎖性海底や堀底
等の底質を改良して嫌気性細菌を減少させて、藻類や生
物等の生息環境の改善を図ることができる底質改良剤お
よび底質改良方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a bottom sediment improving agent which can improve the habitat of algae, living organisms, etc. by improving sediment such as a closed seabed and a moat bottom to reduce anaerobic bacteria. And a method for improving sediment quality.

【0002】[0002]

【従来の技術】例えば、湾内のような閉鎖性海域の海底
や湖沼、ダム湖、運河、堀等の底には水の流れが少なく
有機物が堆積しやすいため、水温が20℃以上に上昇す
ると、底部に堆積している有機物が酸化分解して乳酸や
プロピオン酸や酢酸等の有機酸を生成し、嫌気性細菌が
増殖して硫黄酸化物を還元するため、毒性のある硫化水
素が浮上し被害をもたらすことになる。これを防止する
方法として、石灰系のアルカリ物質を投入して底質表面
にアルカリ性の被膜を形成し、嫌気性細菌の活性を低く
して硫化水素が発生するのを抑制する方法が知られてお
り、永年にわたって実施されている。
2. Description of the Related Art For example, when water temperature rises to 20 ° C. or more, since the flow of water is small and organic matter is easily deposited on the bottom of a closed sea area such as a bay or at the bottom of a lake, a dam lake, a canal, a moat, etc. The organic matter deposited on the bottom is oxidized and decomposed to produce organic acids such as lactic acid, propionic acid, and acetic acid, and anaerobic bacteria grow to reduce sulfur oxides, causing toxic hydrogen sulfide to emerge. It will cause damage. As a method for preventing this, a method is known in which a lime-based alkaline substance is injected to form an alkaline film on the bottom surface, thereby reducing the activity of anaerobic bacteria and suppressing the generation of hydrogen sulfide. And has been in place for many years.

【0003】ところが、本発明者らの研究によると、石
灰系の材料を使ってpHをアルカリサイドへ引き上げる
方法は、海水中において石灰(CaO)が水酸化カルシ
ウム(Ca(OH)2 )に変わり、更に二水石膏(Ca
SO4 ・2H2 O)と炭酸石灰(CaCO3 )に変わ
る。二水石膏(CaSO4 ・2H2 O)は溶解度が大き
いので硫酸分離して栄養源となり、嫌気性細菌が活発に
働きだすというマイナス効果が生じることが判明した。
また、石灰の大半が炭酸石灰(CaCO3 )となって底
質表層を覆い、酸素が遮断される状態となり、その下に
は生物、藻類、草類の繁殖がみられないことも判明し
た。
However, according to the study of the present inventors, the method of raising the pH to the alkaline side using a lime-based material is that lime (CaO) is replaced with calcium hydroxide (Ca (OH) 2 ) in seawater. , And gypsum (Ca)
(SO 4 2H 2 O) and lime carbonate (CaCO 3 ). Gypsum dihydrate (CaSO 4 .2H 2 O) was found to have a negative effect that sulfuric acid was separated as a nutrient source due to its high solubility, and anaerobic bacteria began to work actively.
In addition, it was also found that most of the lime became carbonated lime (CaCO 3 ), covering the surface of the sediment, and oxygen was cut off, and no organisms, algae, and grasses were bred below it.

【0004】[0004]

【発明が解決しようとする課題】本発明は上記のような
従来の問題点を解決して、閉鎖性海底や堀底等の底質を
効率よく改良して嫌気性細菌の増殖を防止し、藻類や生
物等の生息環境の改善を図ることができる底質改良剤お
よび底質改良方法を提供することを目的として完成され
たものである。
DISCLOSURE OF THE INVENTION The present invention solves the above-mentioned conventional problems and efficiently improves sediment such as a closed seabed and a moat floor to prevent the growth of anaerobic bacteria and to prevent the growth of algae. The present invention has been completed for the purpose of providing a sediment improving agent and a method for improving a sediment capable of improving a habitat of a living thing or the like.

【0005】[0005]

【課題を解決するための手段】上記の課題を解決するた
めになされた本発明は、純度30〜97%の水酸化マグ
ネシウムを、硬度が0.3〜4.0kg/粒で粒径が2〜
9mmの粒状あるいはペレット状のものとし、またはフレ
ーク状のものとしたことを特徴とする底質改良剤と、こ
の底質改良剤を、有機物の多い底質に100〜1000
g/m2の割合で散布して有機物を分解処理させるようにし
たことを特徴とする底質改良方法である。
SUMMARY OF THE INVENTION To solve the above-mentioned problems, the present invention provides magnesium hydroxide having a purity of 30 to 97%, a hardness of 0.3 to 4.0 kg / grain and a particle size of 2 kg. ~
9 mm granular or pellet-like or flake-like bottom sediment improver, and this sediment improver is added to an organic matter-rich sediment by 100-1000.
This is a method for improving bottom quality, characterized in that organic substances are decomposed by spraying at a rate of g / m 2 .

【0006】[0006]

【発明の実施の形態】以下に、本発明の好ましい実施の
形態を示す。本発明では、人間の生活環境を良好に改善
することに主眼をおいて材料の選択し、自然破壊や環境
破壊を誘因する物質でないことを前提に研究した結果、
水酸化マグネシウムを用いることで問題を解決した。水
酸化マグネシウムは、海水中に含有されているミネラル
の一つであるマグネシウムをMg(OH)2 の形で採取
したアルカリ性剤である。そして、Mg(OH)2 は海
水ではほとんど溶解せず、酸性物と反応して溶解する物
質であるため、施用量のロスがないという利点を有する
ものであり、また硫酸塩と反応して硫酸マグネシウム
(MgSO4 )と水に分解するので海底に残渣を残さな
いという利点を有する。更に、長期的にみればMg(O
H)2 は徐々に溶け出し、この溶け出したアルカリ分が
近辺をアルカリ性に保つという利点もある。この結果、
海底泥のような場所に適用すれば、泥をアルカリ性に維
持し底質を改良して嫌気性細菌の増殖を有効に防止する
こととなる。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Preferred embodiments of the present invention will be described below. In the present invention, the selection of materials with a focus on improving the human living environment satisfactorily, as a result of research on the premise that they are not substances that induce natural destruction or environmental destruction,
The problem was solved by using magnesium hydroxide. Magnesium hydroxide is an alkaline agent obtained by collecting magnesium, which is one of the minerals contained in seawater, in the form of Mg (OH) 2 . Since Mg (OH) 2 is a substance that hardly dissolves in seawater and reacts and dissolves with an acidic substance, it has the advantage that there is no loss in application rate. Since it is decomposed into magnesium (MgSO 4 ) and water, there is an advantage that no residue is left on the sea floor. Furthermore, in the long term, Mg (O
H) 2 gradually dissolves, and there is also an advantage that the dissolved alkali keeps the vicinity alkaline. As a result,
If applied to places such as seabed mud, the mud will be kept alkaline and the sediment will be improved to effectively prevent the growth of anaerobic bacteria.

【0007】そして本発明では、前記水酸化マグネシウ
ムとして、硬度が0.3〜4.0kg/粒で粒径が2〜9
mmの粒状あるいはペレット状のものとし、またはフレー
ク状のものとして使用する。これは水酸化マグネシウム
の真比重が2.39と大きなものであり、一方、底質泥
の表層は軟らかいため、粒度が大きくて硬いものは反応
前に泥中へ自然に潜り込むという物理性と、細かく分散
して沈降するほど菌や硫黄酸化物との接触面積を増加さ
せるという化学的根拠を基本として硬度と形状を特定し
ている。
In the present invention, the magnesium hydroxide has a hardness of 0.3 to 4.0 kg / particle and a particle size of 2 to 9 kg.
Use as granules or pellets of mm or flakes. This is because the true specific gravity of magnesium hydroxide is as large as 2.39, while the surface layer of the sediment is soft, and the large and hard particles have the physical property of sneaking into the mud naturally before the reaction, The hardness and shape are specified based on the chemical basis that the finer the particles are, the more they disperse and settle.

【0008】また水酸化マグネシウムに対し、貝化石を
体積比で20%以上の割合で混合することもできる。こ
の場合、予め混合しておく他、施工現地において別々の
袋に入っている水酸化マグネシウムと貝化石の各袋を一
定の比率で使用することもできる。貝化石は、有史以前
の地殻変動によって生じた天然物であり飼料添加物とし
て公認されて久しく、特に養殖用の餌に配合して使用さ
れている安全性の高いものである。この貝化石は、Ca
CO3 を主成分とする中性化合物であり、溶出して近辺
をアルカリ性に保つという機能はないが、有機物の分解
過程で生じる窒素や燐を減少させて富栄養化を抑制する
作用を発揮し、間接的に嫌気性細菌の増殖を防止するも
のである。そして、水酸化マグネシウムと貝化石を同時
に用いることで、水酸化マグネシウムの性能である酸と
の反応を促進し、貝化石の特性である多孔質形状によっ
て、水酸化マグネシウムの持続性を高める相乗効果が得
られるので併用することがより好ましい。
[0008] Further, shell fossils can be mixed with magnesium hydroxide at a ratio of 20% or more by volume. In this case, besides mixing in advance, each bag of magnesium hydroxide and shell fossil contained in separate bags at the construction site can be used at a fixed ratio. Shell fossils are natural products produced by prehistoric crustal deformation, have long been officially recognized as feed additives, and have high safety especially when used in feed for aquaculture. This shell fossil is Ca
It is a neutral compound mainly composed of CO 3 and has no function of eluting and keeping the surrounding area alkaline, but exerts the effect of reducing nitrogen and phosphorus generated in the decomposition process of organic substances and suppressing eutrophication. And indirectly prevent the growth of anaerobic bacteria. By using magnesium hydroxide and shell fossils at the same time, synergistic effect of promoting the reaction with acid, which is the performance of magnesium hydroxide, and increasing the sustainability of magnesium hydroxide by the porous shape which is the characteristic of shell fossils Are more preferably used in combination.

【0009】なお以上のような底質改良剤は、水面上よ
り直接に散布することもできるが、風や波や現場の状況
によって散布し難い場合もあり、このような場合には生
分解性樹脂からなる袋体に5〜20kg/袋を詰めて用い
るようにすれば、取扱性に優れまた均一な散布が可能と
なり好ましい。
Although the above sediment improving agent can be sprayed directly on the water surface, it may be difficult to spray it due to wind, waves, or on-site conditions. It is preferable to pack 5 to 20 kg / bag in a resin bag because excellent handling properties and uniform spraying are possible.

【0010】このような底質改良剤は、有機物の多い底
質に対し100〜1000g/m2、好ましくは250〜5
00g/m2の割合で水面上より散布して前記有機物を分解
処理させるようにする。底質改良剤は粒径が2〜9mmの
粒状やペレット状のもの、またはフレーク状のものであ
るため広範囲に拡がりつつ沈降し、目的とする底質層を
完全にカバーすることとなる。なお底質改良剤の散布
は、水温が20℃以上になると有機物が酸化分解を開始
するので、その直前に散布処理するが好ましい。
Such a sediment improver is used in an amount of 100 to 1000 g / m 2 , preferably 250 to 5
The organic matter is decomposed by spraying from the surface of the water at a rate of 00 g / m 2 . Since the sediment improver is in the form of granules, pellets, or flakes having a particle size of 2 to 9 mm, it spreads over a wide area and sediments, completely covering the intended sediment layer. In addition, since the organic matter starts oxidative decomposition when the water temperature becomes 20 ° C. or more, it is preferable to spray the bottom quality improving agent immediately before the spraying.

【0011】また底質改良剤は、真比重が2.39と大
きな水酸化マグネシウムからなり、硬度が0.3〜4.
0kg/粒で粒径が2〜9mmの粒状あるいはペレット状の
ものとし、またはフレーク状のものであるため、水面上
から散布すると速やかに沈降して底質の表面から1〜1
0cmの深さの位置に留まることとなる。これは、底質表
層はヘドロ化した有機物が堆積して軟質泥土で覆われて
いるためであり、底質改良剤が改質を最も必要とする場
所に丁度留まるよう形状等が選択されているからであ
る。
The sediment improving agent is composed of magnesium hydroxide having a true specific gravity of 2.39 and a hardness of 0.3 to 4.
Since it is in the form of granules or pellets having a particle size of 2 to 9 mm at 0 kg / particle, or in the form of flakes, it spreads quickly from the surface of the water and sediments quickly and is 1 to 1 from the surface of the sediment.
It will remain at a depth of 0 cm. This is because the sediment surface layer is covered with soft mud by depositing organic matter converted into sludge, and the shape and the like are selected so that the sediment improver just stays in the place where the reforming is most needed. Because.

【0012】[0012]

【実施例】(実施例1、2)三重県度会郡南勢町五ケ所
湾内の赤潮発生頻度の多い地内である礫浦地内の船舶工
区内において、養殖漁場の底質改善を目的として、硬度
が0.5kg/粒で粒径が3〜7mmの粒状の水酸化マグネ
シウムからなる底質改良剤を、散布量200〜400g/
m2の割合で散布し、施工後約2ケ月、および3ケ月後に
その海域における底質層の酸素量、PH値、硫化物量な
どを調査した(実施例1)。また、水酸化マグネシウム
と貝化石を体積比で50%ずつ混合した底質改良剤を、
同様に散布した場合を実施例2として調査した。各種デ
ータの測定結果は表1に示すとおりであり、底質層から
採取した泥の中に底質改良剤が点々と混在しているのが
認められ、施工前は生物(貝やゴカイ等)や藻類の生息
がなかったが、施工後にはいずれも繁殖していることが
確認でき、環境の改善が図れたことが確認できた。一
方、底質改良剤を散布しなかった海域(比較例1)の底
質層の泥は硫化物の強い臭いがし、また生物も藻も存在
しないものであった。なお、以上の実験は出願人が三重
県漁業協同組合連合会の協力のもとに行ったものであ
る。
[Examples] (Examples 1 and 2) Hardness was improved to improve the sediment quality of aquaculture fishing grounds in the shipyard in the Gravel Pond, which is a land with high red tide frequency, in Gogasho Bay, Minamisei-cho, Dokai-gun, Mie Prefecture. A sediment improver consisting of granular magnesium hydroxide having a particle size of 3 to 7 mm at 0.5 kg / particle was sprayed at a rate of 200 to 400 g / g.
Spraying was performed at a rate of m 2 , and about 2 months and 3 months after the construction, the oxygen content, PH value, sulfide content, etc. of the sediment layer in the sea area were investigated (Example 1). In addition, a bottom quality improver in which magnesium hydroxide and shell fossils are mixed by 50% by volume ratio,
In the same manner, the case of spraying was examined as Example 2. The measurement results of various data are as shown in Table 1, and it was recognized that the sediment improving agent was mixed in the mud collected from the sediment layer in various places. No algae or inhabitants were found, but it was confirmed that they were all breeding after construction, and that the environment was improved. On the other hand, the mud in the sediment layer in the sea area where the sediment improver was not sprayed (Comparative Example 1) had a strong smell of sulfide, and was free of organisms and algae. The above experiments were performed by the applicant in cooperation with the Mie Prefecture Fisheries Cooperative Association.

【0013】[0013]

【表1】 [Table 1]

【0014】(実施例3〜6)三重県度会郡南勢町五ケ
所湾内の赤潮発生頻度の多い地内である礫浦地内の船舶
外工区内(実施例3、4)、および榊原地内の水汲み谷
区(実施例5、6)において、養殖漁場の底質改善を目
的として、水酸化マグネシウムからなる底質改良剤、お
よび水酸化マグネシウムと貝化石を体積比で50%ずつ
混合した底質改良剤を、実施例1、2と同様に散布し
て、各種データの測定した結果は表2、3に示すとおり
であった。また、実施例3〜6では底質層から採取した
泥の中に底質改良剤が点々と混在しているのが認めら
れ、施工前は生物(貝やゴカイ等)や藻類の生息がなか
ったが、施工後にはいずれも繁殖していることが確認で
き、環境の改善が図れたことが確認できた。一方、底質
改良剤を散布しなかった海域(比較例2、3)の底質層
の泥は硫化物の強い臭いがし、また生物も藻も存在しな
いものであった。なお、以上の実験は出願人が三重県漁
業協同組合連合会の協力のもとに行ったものである。
(Examples 3 to 6) Water pumping in a ship-excavation area in a gravel basin, which is a frequent occurrence of red tide, in Gogasho Bay, Minase-cho, Dokai-gun, Mie Prefecture (Examples 3 and 4) and in Sakakibara area In the valleys (Examples 5 and 6), for the purpose of improving the bottom quality of aquaculture and fishing grounds, a bottom quality improving agent composed of magnesium hydroxide and a bottom quality improvement mixture of 50% by volume of magnesium hydroxide and shell fossils were mixed. The agent was sprayed in the same manner as in Examples 1 and 2, and the results of measurement of various data were as shown in Tables 2 and 3. Further, in Examples 3 to 6, it was recognized that the sediment improving agent was mixed in the mud collected from the sediment layer, and there was no inhabitation of living organisms (eg, shellfish and creatures) and algae before construction. However, after the construction, it was confirmed that the breeding was in all cases, and it was confirmed that the environment was improved. On the other hand, the mud in the sediment layer in the sea area where the sediment improver was not sprayed (Comparative Examples 2 and 3) had a strong smell of sulfide, and was free of organisms and algae. The above experiments were performed by the applicant in cooperation with the Mie Prefecture Fisheries Cooperative Association.

【0015】[0015]

【表2】 [Table 2]

【0016】[0016]

【表3】 [Table 3]

【0017】(実施例7)三重県志摩郡志摩町和具浦地
内において、真珠養殖漁場の底質改善を目的として、水
酸化マグネシウムからなる底質改良剤を、散布量約25
0g/m2の割合で散布し、施工後約3ケ月、6ケ月、およ
び9ケ月後にその海域における底質層の酸素量、PH
値、硫化物量などを調査した。各種データの測定結果は
表4に示すとおりであった。一方、底質改良剤を散布し
なかった海域(比較例4)の底質層の泥は硫化物の強い
臭いがし、また生物も藻も存在しないものであった。な
お、以上の実験は出願人が三重県志摩町水産農林課の協
力のもとに行ったものである。
(Example 7) In the Wagoura area of Shima-cho, Shima-gun, Mie Prefecture, a sediment improver composed of magnesium hydroxide was sprayed in an amount of about 25 for the purpose of improving the sediment quality of a pearl culture fishing ground.
0 g / m 2 at about 3 months, 6 months, and 9 months after construction,
Values, sulfide content, etc. were investigated. The measurement results of the various data were as shown in Table 4. On the other hand, the mud in the sediment layer in the sea area where the sediment improver was not sprayed (Comparative Example 4) had a strong smell of sulfide, and was free from living things and algae. The above experiments were performed by the applicant in cooperation with the Fisheries Agriculture and Forestry Division, Shima Town, Mie Prefecture.

【0018】[0018]

【表4】 [Table 4]

【0019】[0019]

【発明の効果】以上の説明からも明らかなように、本発
明は閉鎖性海底や堀底等の底質を効率よく改良して嫌気
性細菌の増殖を防止し、藻類や生物等の生息環境の改善
を図ることができるものである。よって本発明は従来の
問題点を一掃した底質改良剤および底質改良方法とし
て、産業の発展に寄与するところは極めて大である。
As is apparent from the above description, the present invention efficiently improves sediment such as a closed seabed and a moat floor, prevents the growth of anaerobic bacteria, and reduces the habitat of algae and living organisms. It can be improved. Therefore, the present invention greatly contributes to industrial development as a sediment improving agent and a sediment improving method that have eliminated the conventional problems.

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 純度30〜97%の水酸化マグネシウム
を、硬度が0.3〜4.0kg/粒で粒径が2〜9mmの粒
状あるいはペレット状のものとし、またはフレーク状の
ものとしたことを特徴とする底質改良剤。
1. Magnesium hydroxide having a purity of 30 to 97%, in the form of granules or pellets having a hardness of 0.3 to 4.0 kg / particle and a particle size of 2 to 9 mm, or flakes. A bottom quality improving agent, characterized in that:
【請求項2】 請求項1に記載の水酸化マグネシウムに
対し貝化石を体積比20%以上の割合で混合したことを
特徴とする底質改良剤。
2. A bottom sediment improving agent comprising the fossil shell fossil mixed with the magnesium hydroxide according to claim 1 at a volume ratio of 20% or more.
【請求項3】 請求項1または2に記載の底質改良剤が
生分解性樹脂からなる袋体に詰められていることを特徴
とする底質改良剤。
3. A bottom sediment improving agent characterized in that the sediment improving agent according to claim 1 or 2 is packed in a bag made of a biodegradable resin.
【請求項4】 請求項1〜3のいずれかに記載の底質改
良剤を、有機物の多い底質に100〜1000g/m2の割
合で散布して有機物を分解処理させるようにしたことを
特徴とする底質改良方法。
4. The method according to claim 1, wherein the sediment improving agent according to any one of claims 1 to 3 is applied to the sediment rich in organic matter at a rate of 100 to 1000 g / m 2 to decompose the organic matter. Characteristic method of improving bottom quality.
【請求項5】 底質改良剤を、底質の表面から1〜10
cmの深さの位置に留まらせるようにした請求項4に記載
の底質改良方法。
5. A sediment improving agent is added from 1 to 10 from the surface of sediment.
5. The method for improving bottom sediment according to claim 4, wherein the method is adapted to remain at a depth of cm.
JP36626399A 1999-12-24 1999-12-24 Bottom sediment-improving agent and method for improving bottom sediment Withdrawn JP2001181117A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP36626399A JP2001181117A (en) 1999-12-24 1999-12-24 Bottom sediment-improving agent and method for improving bottom sediment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP36626399A JP2001181117A (en) 1999-12-24 1999-12-24 Bottom sediment-improving agent and method for improving bottom sediment

Publications (1)

Publication Number Publication Date
JP2001181117A true JP2001181117A (en) 2001-07-03

Family

ID=18486342

Family Applications (1)

Application Number Title Priority Date Filing Date
JP36626399A Withdrawn JP2001181117A (en) 1999-12-24 1999-12-24 Bottom sediment-improving agent and method for improving bottom sediment

Country Status (1)

Country Link
JP (1) JP2001181117A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008239516A (en) * 2007-03-26 2008-10-09 Hiroto Maeda Prevention of red tide
JP2016068021A (en) * 2014-09-30 2016-05-09 宇部マテリアルズ株式会社 Modifier for bottom sediment of habitat of bivalve digging into sand, and improvement method
JP2022076111A (en) * 2020-11-09 2022-05-19 アクアインテック株式会社 Pump facility

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008239516A (en) * 2007-03-26 2008-10-09 Hiroto Maeda Prevention of red tide
JP2016068021A (en) * 2014-09-30 2016-05-09 宇部マテリアルズ株式会社 Modifier for bottom sediment of habitat of bivalve digging into sand, and improvement method
JP2022076111A (en) * 2020-11-09 2022-05-19 アクアインテック株式会社 Pump facility
JP7551105B2 (en) 2020-11-09 2024-09-17 アクアインテック株式会社 Pumping Station

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