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JPH0633603B2 - Method of injecting sediment composition into water - Google Patents
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JPH0633603B2 - Method of injecting sediment composition into water - Google Patents

Method of injecting sediment composition into water

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Publication number
JPH0633603B2
JPH0633603B2 JP61058175A JP5817586A JPH0633603B2 JP H0633603 B2 JPH0633603 B2 JP H0633603B2 JP 61058175 A JP61058175 A JP 61058175A JP 5817586 A JP5817586 A JP 5817586A JP H0633603 B2 JPH0633603 B2 JP H0633603B2
Authority
JP
Japan
Prior art keywords
water
sand
earth
composition
sediment
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 - Lifetime
Application number
JP61058175A
Other languages
Japanese (ja)
Other versions
JPS62215722A (en
Inventor
大三 喜田
博 久保
知則 漆原
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.)
Obayashi Corp
Original Assignee
Obayashi Corp
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 Obayashi Corp filed Critical Obayashi Corp
Priority to JP61058175A priority Critical patent/JPH0633603B2/en
Publication of JPS62215722A publication Critical patent/JPS62215722A/en
Publication of JPH0633603B2 publication Critical patent/JPH0633603B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Description

【発明の詳細な説明】 《産業上の利用分野》 本発明は、水底の盛土,人工島の造成を行なう際に用い
られる土砂組成物の水中投入方法に関し、特に投入時に
おける水質の汚濁を防止する方法に関する。
TECHNICAL FIELD The present invention relates to a method for injecting earth and sand composition into water, which is used when embankment at the bottom of a water and artificial islands is constructed, and particularly to prevent water pollution during the operation. On how to do.

《発明の背景》 河川,湖沼,海などの水底の盛土,人工島の造成を行な
う場合には、土砂を水中に投入するようにしている。し
かしながら、この一般的な土砂では、土砂粒子が水中で
バラバラに分離して沈降するため、粗粒分が先に沈降し
て堆積し、細粒分は沈降が遅く水中に懸濁し、堆積物の
うちの上層に多く堆積するために、造成された地盤は不
均質で、しかも細粒分を多く含む部分では含水比が高く
非常に軟弱であり、しかも土砂投入時に水質が著しく汚
濁する問題があった。
<< Background of the Invention >> When constructing embankments or artificial islands on the bottom of rivers, lakes, seas, etc., earth and sand are put into water. However, in this general sediment, since the sediment particles are separated and settled in water, the coarse particles settle and deposit first, and the fine particles settle slowly and are suspended in water. Due to the large amount of sedimentation in the upper layer of the soil, the ground that was created is non-homogeneous, and the water content is very high in the part that contains a large amount of fine particles, and it is extremely soft. It was

そこで、本出願人は先に一般的な土砂と粘結剤またはこ
れらと硬化剤とを混合してなる土砂組成物を開発した。
この土砂組成物の粘結剤は土砂粒子間に粘結性を与え、
かつ所定の流動性を確保する材料であり、硬化剤は土砂
を固結させるための材料である。従って、この土砂組成
物は水中に投入した状態でバラバラに分離することな
く、ほぼ一体となって沈降するため、非常に均質な状態
に堆積し、経時後の水中での水の取り込みも少ないので
密度低下が少ない緻密な状態を維持できる利点がある。
Therefore, the present applicant has previously developed a sediment composition which is a mixture of general sediment and a binder or these and a curing agent.
The binder of this earth and sand composition gives a caking property between earth and sand particles,
In addition, it is a material that secures a predetermined fluidity, and the curing agent is a material for solidifying earth and sand. Therefore, this sediment composition does not separate into pieces when it is poured into water, but it settles almost as a unit, so that it deposits in a very homogeneous state, and the uptake of water in water after a while is small. There is an advantage that it is possible to maintain a dense state with little decrease in density.

《発明が解決しようとする問題点》 しかしながら、このような土砂組成物であっても、水中
投入時に土砂粒子が分離してしまい、吐出部分近傍で水
質が汚濁する場合があった。
<< Problems to be Solved by the Invention >> However, even with such a soil-and-sand composition, the soil-and-sand particles may be separated when being poured into water, and the water quality may be polluted in the vicinity of the discharge portion.

この原因は、(1)土砂組成物中の土砂の粒度が細かい
場合、(2)組成物の混合状態における流動性が大きす
ぎる場合、(3)吐出速度が大きい場合、などである。
従って、前記(1),(2),(3)の要因を除去した
状態で水中投入すれば良いが、実際にはこれらの要因の
全てを除去しきれるものでない。
The causes are (1) the particle size of the sand in the sand composition is fine, (2) the fluidity of the composition in the mixed state is too large, (3) the discharge rate is high, and the like.
Therefore, it may be introduced into the water in a state where the factors (1), (2), and (3) are removed, but in reality, all of these factors cannot be removed.

水中汚濁を防止する対策としては、打設場所を締切り、
締切りの内部の水を打設高さに併せてポンプアップし、
凝集沈澱処理した後に放流することが一般的であるが、
この方法では別途凝集沈澱池が必要となり、特に海上工
事などでは非常にコスト高なものとなる。
As a measure to prevent underwater pollution, the placement site is closed,
Pump up the water inside the deadline according to the casting height,
Although it is common to discharge after coagulating sedimentation treatment,
This method requires a separate coagulation sedimentation basin, which is extremely expensive especially for offshore construction.

この発明は、以上の問題点に鑑みなされたもので、汚濁
の発生源である吐出管の吐出端で集中的に汚濁防止対策
を施すことにより、完全に汚濁の発生を防止できるよう
にすることを目的とする。
The present invention has been made in view of the above problems, and it is possible to completely prevent the occurrence of pollution by intensively taking measures to prevent pollution at the discharge end of the discharge pipe, which is the source of pollution. With the goal.

《問題点を解決するための手段》 前記目的を達成するため、この発明は、土砂と粘結剤と
硬化剤とを混合してなる土砂組成物を吐出管より水中に
吐出するとともに、水中に吐出された土砂のうちの懸濁
状態にある土砂に対して該吐出管の吐出端近傍から凝集
剤を噴出するようにしたことを特徴とする。
<< Means for Solving Problems >> In order to achieve the above-mentioned object, the present invention is to discharge the earth and sand composition obtained by mixing earth and sand, a binder and a hardening agent into water through a discharge pipe, and It is characterized in that the coagulant is jetted from the vicinity of the discharge end of the discharge pipe to the suspended sediment of the discharged sediment.

《作 用》 吐出端近傍で舞い上がる懸濁粒子は直ちに凝集剤に接触
することにより凝集沈積することになる。
<Operation> Suspended particles rising near the discharge end will immediately contact the flocculant and will be aggregated and deposited.

《実施例》 第1図はこの発明方法の第1の実施例を示すものであ
る。
<< Embodiment >> FIG. 1 shows a first embodiment of the method of the present invention.

図において、1は吐出端1aを水底地盤Eに向けた吐出
管、2は該吐出管1の外周部に平行であって、その噴出
端2aを前記吐出端1aの周縁に位置させた凝集剤圧送
パイプである。
In the figure, 1 is a discharge pipe whose discharge end 1a is directed to the submarine ground E, 2 is parallel to the outer peripheral portion of the discharge pipe 1, and the spouting end 2a is located at the periphery of the discharge end 1a. It is a pressure pipe.

吐出管1内には図示しない圧送ポンプにより土砂組成物
が供給され、その吐出端1aより土砂組成物3を吐出
し、水底地盤E上に土砂組成物3の層を沈積させてい
る。
The earth and sand composition is supplied into the discharge pipe 1 by a pressure feed pump (not shown), and the earth and sand composition 3 is discharged from the discharge end 1a to deposit a layer of the earth and sand composition 3 on the water bottom ground E.

前記土砂組成物3は、一般的な土砂と、該土砂粒子間に
粘結性を与え、かつ所定の流動性を確保する粘結剤と、
土砂粒子間で硬化し、該土砂を固結させる硬化剤とを含
んでいる。
The earth and sand composition 3 is a general earth and sand, and a caking agent that gives a caking property between the earth and sand particles and secures a predetermined fluidity,
It contains a hardening agent which hardens between the earth and sand particles and solidifies the earth and sand.

前記粘結剤は水溶性天然,半合成または合成高分子から
なるもので、一種の糊状物質によって各粒子の分離、並
びに水の取り込みを防ぐ機能を備えている。
The binder is composed of a water-soluble natural, semi-synthetic or synthetic polymer, and has a function of separating each particle by a kind of pasty substance and preventing water from being taken in.

該粘結剤を具体的に説明すると、水溶性天然高分子とし
ては、各種澱粉,こんにゃくふのり,寒天,アルギン酸
ソーダ,トロロアオイ,トラゴントガム,アラビアゴ
ム,デキストリン,レバン、にかわ,ゼラチン,カゼイ
ン,コラーゲンなどを用いる。
Explaining the binder specifically, examples of water-soluble natural polymers include various starches, konjac fukin, agar, sodium alginate, trourooi, tragone gum, gum arabic, dextrin, levan, glue, gelatin, casein, collagen and the like. To use.

水溶性半合成高分子の例としては、ビスコース,メチル
セルロース,エチルセルロース,ヒドロキシエチルセル
ロース,ヒドロキシプロピルメチルセルロース,カルボ
キシメチルセルロース,可溶性澱粉,カルボキシメチル
澱粉,ジアルデヒド澱粉などを用いる。
Examples of water-soluble semi-synthetic polymers include viscose, methyl cellulose, ethyl cellulose, hydroxyethyl cellulose, hydroxypropyl methyl cellulose, carboxymethyl cellulose, soluble starch, carboxymethyl starch, dialdehyde starch and the like.

水溶性合成分子としては、ポリビニルアルコール,ポリ
アクリル酸ナトリウム,ポリアクリルアミド,ポリエチ
レンオキシドなどを用いる。
As the water-soluble synthetic molecule, polyvinyl alcohol, sodium polyacrylate, polyacrylamide, polyethylene oxide or the like is used.

前記硬化剤は、普通ポルトランドセメント,高炉セメン
ト,フライアッシュセメント,その他のセメント材料あ
るいは消石灰などの石灰系材料またはアスファルト系材
料,高炉スラグ系材料の中から選ばれた一種またはその
組合せとなっている。そして、この種の硬化剤は投入後
の土砂の土質を固化し、安定させ、その強度を向上させ
る機能を備えている。
The curing agent is one or a combination selected from ordinary Portland cement, blast furnace cement, fly ash cement, other cement materials, lime-based materials such as slaked lime, asphalt-based materials, and blast-furnace slag-based materials. . Then, this type of hardening agent has a function of solidifying and stabilizing the soil quality of the earth and sand after charging, and improving its strength.

また、各粘結剤および硬化剤の土砂に対する配合割合
は、経済性および硬化の達成度合いを勘案して、土砂10
00重量部に対し粘結剤 1〜 5重量部、および硬化剤50〜
300重量部が最も好ましい値となっている。
In addition, the mixing ratio of each binder and hardening agent to the earth and sand is 10 in consideration of the economic efficiency and the degree of achievement of hardening.
1 to 5 parts by weight of binder and 50 to 50 parts by weight of hardener
300 parts by weight is the most preferable value.

さらに、これらの組成物3は水とともに混合し、スラリ
ー状の状態で前記吐出管1の吐出端1aより投入される
ものであり、一般土砂に比べて懸濁の惧れは殆どない
が、土砂そのものの粒度が細かい場合や吐出速度が大き
い場合などでは吐出した部分の周縁に図中点の集合で示
す懸濁層4を生ずる。ここで、この懸濁層4は凝集剤圧
送パイプ2の噴出端2aから噴出する凝集剤に接触し、
直ちに凝集し、沈積した土砂組成物上に沈降し、これに
より汚濁が防止されることになる。
Furthermore, these compositions 3 are mixed with water and are introduced in the state of a slurry from the discharge end 1a of the discharge pipe 1, and there is almost no possibility of suspension as compared with general earth and sand. In the case where the particle size is small or the discharge speed is high, the suspension layer 4 shown by a set of dots in the figure is formed at the periphery of the discharged portion. Here, the suspension layer 4 contacts the coagulant ejected from the ejection end 2a of the coagulant pressure-feeding pipe 2,
It immediately aggregates and settles on the deposited sediment composition, which prevents pollution.

なお、噴出端2aの形状としては、細かい多数のノズル
部を設けることにより懸濁層4との接触確立を高め、ほ
ぼ完全に汚濁を防止することができる。
As for the shape of the ejection end 2a, by providing a large number of fine nozzle portions, the contact establishment with the suspension layer 4 can be enhanced, and the contamination can be almost completely prevented.

なお、前記凝集剤としてはPAC,硫酸バンドなどの無
機凝集剤あるいは高分子凝集剤の単独または混合物を併
用して用いる。
As the aggregating agent, inorganic aggregating agents such as PAC and sulfuric acid band or polymer aggregating agents may be used alone or in combination.

この場合、海中など塩分を含む水域での工事では、通常
高分子凝集剤のみで十分である。
In this case, the polymer flocculant alone is usually sufficient for construction in a sea area containing salt.

一方、併用する場合には、これらの凝集剤を別々のパイ
プで圧送し、無機凝集剤が先に接触するようにパイプを
配置することが望ましい。
On the other hand, when they are used in combination, it is desirable that these aggregating agents are pressure-fed by separate pipes and the pipes are arranged so that the inorganic aggregating agent comes into contact with them first.

また、その使用量としては、前記懸濁層4の1m2に対し
1〜5gの高分子凝集剤でほぼ水中汚濁を完全に防止す
ることが確認されている。
It has been confirmed that 1 to 5 g of the polymer flocculant per 1 m 2 of the suspension layer 4 can be used to completely prevent water contamination.

次に第2図はこの発明方法の第2実施例を示すものであ
る。
Next, FIG. 2 shows a second embodiment of the method of the present invention.

図において、吐出管1の吐出端1aの周縁には水中ポン
プ10の吸込み端10aが位置している。また、凝集剤
圧送パイプ2の噴出端2bは水中ポンプ10の吸込端1
0aに位置させている。
In the figure, the suction end 10 a of the submersible pump 10 is located on the periphery of the discharge end 1 a of the discharge pipe 1. Further, the ejection end 2b of the coagulant pressure-feeding pipe 2 is the suction end 1 of the submersible pump 10.
It is located at 0a.

以上の構成において、吐出管1より土砂組成物3を吐出
した状態で、水中ポンプ10を駆動することにより、吐
出端1aの周縁に舞い上がる懸濁層4は水中ポンプの吸
込み端側にすべて吸引され、同時に凝集剤圧送パイプ2
の噴出端2bから噴出する凝集剤も吸込み端10aより
水中ポンプ10内にい取り込まれる。水中ポンプ10内
で懸濁層4と凝集剤とは接触混合し、その状態で水中ポ
ンプ10の吐出し端10bより吐き出される。
In the above configuration, by driving the submersible pump 10 in a state where the sediment composition 3 is discharged from the discharge pipe 1, the suspension layer 4 rising to the periphery of the discharge end 1a is all sucked to the suction end side of the submersible pump. At the same time, coagulant pressure feed pipe 2
The aggregating agent ejected from the ejection end 2b of the above is also taken into the submersible pump 10 from the suction end 10a. The suspension layer 4 and the coagulant are contact-mixed in the submersible pump 10, and in this state, the suspension layer 4 and the coagulant are discharged from the discharge end 10b of the submersible pump 10.

吐き出された懸濁層4は凝集剤の凝集作用により早期に
沈降、水底地盤E上に沈積することになる。
The discharged suspension layer 4 is settled early by the coagulating action of the coagulant and deposited on the water bottom ground E.

この実施例では、吐出端1aより舞い上がる懸濁層を強
制的に吸込みつつ凝集剤に接触させるために、より一層
確実な汚濁防止効果を得ることになる。
In this embodiment, since the suspension layer rising from the discharge end 1a is forcibly sucked and brought into contact with the coagulant, a more reliable pollution prevention effect can be obtained.

《発明の効果》 以上各実施例によ詳細に説明したように、この発明方法
によれば、土砂組成物の水中投入時において汚濁を完全
に防止できるために、従来のように別途凝集沈澱池を設
けたり、汚濁水を別な場所に搬送する必要がなくなるた
めに、水中投入時における汚濁防止対策を極めて安価に
実施できる。
<Effects of the Invention> As described in detail in each of the above examples, according to the method of the present invention, since it is possible to completely prevent pollution when the earth and sand composition is poured into water, a separate coagulating sedimentation pond as in the conventional case is used. Since it is not necessary to provide an air conditioner or to transport the polluted water to another place, it is possible to implement the pollution prevention measures at the time of the submersion at an extremely low cost.

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

第1図はこの発明の第1の実施例による水中投入方法を
示す説明図、第2図はこの発明の第2実施例による水中
投入方法を示す説明図である。 1……吐出管、1a……吐出端 2……凝集剤圧送パイプ、2a,2b……噴出端 3……土砂組成物
FIG. 1 is an explanatory view showing an underwater charging method according to a first embodiment of the present invention, and FIG. 2 is an explanatory view showing an underwater charging method according to a second embodiment of the present invention. 1 ... Discharge pipe, 1a ... Discharge end 2 ... Coagulant pressure feed pipe, 2a, 2b ... Jet end 3 ... Sediment composition

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】土砂と粘結剤と硬化剤とを混合してなる土
砂組成物を吐出管より水中に吐出するとともに、水中に
吐出された土砂のうちの懸濁状態にある土砂に対して該
吐出管の吐出端近傍から凝集剤を噴出するようにしたこ
とを特徴とする土砂組成物の水中投入方法。
1. A sediment composition obtained by mixing sediment, a binder, and a hardening agent is discharged into water through a discharge pipe, and the suspended sediment of the sand discharged into the water is discharged. A method for injecting a sediment composition into water, characterized in that a coagulant is ejected from the vicinity of the ejection end of the ejection pipe.
JP61058175A 1986-03-18 1986-03-18 Method of injecting sediment composition into water Expired - Lifetime JPH0633603B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61058175A JPH0633603B2 (en) 1986-03-18 1986-03-18 Method of injecting sediment composition into water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61058175A JPH0633603B2 (en) 1986-03-18 1986-03-18 Method of injecting sediment composition into water

Publications (2)

Publication Number Publication Date
JPS62215722A JPS62215722A (en) 1987-09-22
JPH0633603B2 true JPH0633603B2 (en) 1994-05-02

Family

ID=13076660

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61058175A Expired - Lifetime JPH0633603B2 (en) 1986-03-18 1986-03-18 Method of injecting sediment composition into water

Country Status (1)

Country Link
JP (1) JPH0633603B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH04194218A (en) * 1990-11-28 1992-07-14 Mitsui Fudousan Kensetsu Kk Underwater banking method

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5187324A (en) * 1975-01-29 1976-07-30 Motooka Tsusho Kk Umetateyodeido doshanoshorihooho

Also Published As

Publication number Publication date
JPS62215722A (en) 1987-09-22

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