JPS62215722A - Charging of soil and sand composition into water - Google Patents

Charging of soil and sand composition into water

Info

Publication number
JPS62215722A
JPS62215722A JP5817586A JP5817586A JPS62215722A JP S62215722 A JPS62215722 A JP S62215722A JP 5817586 A JP5817586 A JP 5817586A JP 5817586 A JP5817586 A JP 5817586A JP S62215722 A JPS62215722 A JP S62215722A
Authority
JP
Japan
Prior art keywords
soil
water
composition
binder
discharge
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.)
Granted
Application number
JP5817586A
Other languages
Japanese (ja)
Other versions
JPH0633603B2 (en
Inventor
Daizo Kida
喜田 大三
Hiroshi Kubo
博 久保
Tomonori Urushibara
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.)
Ohbayashi Gumi Ltd
Obayashi Corp
Original Assignee
Ohbayashi Gumi Ltd
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 Ohbayashi Gumi Ltd, Obayashi Corp filed Critical Ohbayashi Gumi Ltd
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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Abstract

PURPOSE:To completely prevent the occurrence of muddling of water by a method in which a soil composition formed by mixing soil with a binder with or without a hardener is discharged from a tube into water and also a coagulant is jetted to near the end of the discharge tube. CONSTITUTION:A soil composition 3 containing a binder giving caking power to soil particles and sand grains and also to ensure a given fluidity or a hardener to harden and solidify the soil particles with the binder is supplied by a pump into a discharge tube 1 and discharged from the discharge end 1a to deposit the layer of the composition 3 on the bottom ground (l) under water. Although a suspension layer 4 is formed on the periphery of the discharged position when the grain size of soil is smaller or the discharge speed is high, the suspension layer 4 is coagulated by a coagulant jetted from the end 2a of a coagulant sending pipe 2 and sedimented on the soil composition 3 so deposited to prevent the occurrence of muddling. The prevention measure against muddling when charging the soil composition can be taken at low cost.

Description

【発明の詳細な説明】 (産業上の利用分野)′ 本発明は、水底の覆土、盛土1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。
Detailed Description of the Invention (Industrial Field of Application) The present invention relates to a method of injecting a soil composition into water, which is used when covering the water bottom with soil and creating an embankment and an artificial island. Concerning methods of preventing pollution.

(発明の背景) 河川、湖沼、海などの水底の覆土、盛土1人工島の造成
を行なう場合には、土砂を水中に投入するJ: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 an artificial island by covering the bottom of a river, lake, marsh, sea, etc. with earth and embankment, earth and sand are poured into the water. However, with this general sediment, the sediment particles separate and settle in the water, so the coarse particles settle and accumulate first, while the fine particles settle slowly and become suspended in the water.
Because much of the sediment is deposited in the upper layer, the created ground is heterogeneous, and the areas containing many fine particles have a high water content and are extremely soft, and the water quality becomes extremely polluted when soil is added. There was a problem.

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。
Therefore, the present applicant has previously developed a sand and sand composition made by mixing general sand and a binder, or a mixture of these and a hardening agent.

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
、は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。
The binder in this sediment composition provides caking properties between the sediment particles,
The curing agent is a material for solidifying earth and sand. Therefore, when this sediment composition is put into water, it does not separate into pieces and settles as a whole, so it is deposited in a very homogeneous state, and there is little water uptake in the water after time. Therefore, it has the advantage of being able to maintain a dense state with little density loss.

(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、吐山部分近傍で水
質が汚濁する場合があった。
(Problems to be Solved by the Invention) However, even with such a sediment composition, the sediment particles may separate when put into water, resulting in water pollution in the vicinity of the crest portion.

この原因は、(1)土砂組成物中の土砂の校庭が細かい
場合、(2)組成物の混合状態における流動性が大きす
きるざる場合、(3)吐出速度が大ぎい場合、 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 of this are (1) when the soil in the sediment composition is fine, (2) when the fluidity of the composition is too low in the mixed state, (3) when the discharge speed is too high, etc. . Therefore, it is sufficient to remove the factors (1), (2), and (3) before putting the product into water, but in reality, it is not possible to completely eliminate all of these factors.

水中汚濁を防止覆る対策としては、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。
Measures to prevent and cover water pollution include closing off the pouring area;
Pump up the water inside the cofferdam according to the pouring height,
Generally, it is discharged after coagulation and sedimentation treatment, but
This method requires a separate coagulation and sedimentation tank, which is extremely costly, especially in offshore construction.

この発明は、以上の問題点に息みなされたもので、汚濁
の発生源である吐出菅の吐出端で集中的に汚濁防止対策
を論ずことにより、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。
This invention has been made in view of the above problems, and makes it possible to completely prevent the occurrence of pollution by intensively discussing pollution prevention measures at the discharge end of the discharge tube, which is the source of pollution. The purpose is to

(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、
または土砂と粘結剤と硬化剤とを混合してなる土砂組成
物を吐出菅より水中に吐出するとともに、該吐出端近傍
に凝集剤を噴出するうよにしたことを特徴とする。
(Means for Solving the Problems) In order to achieve the above object, the present invention provides soil and sand, a binder,
Alternatively, it is characterized in that a sand and sand composition formed by mixing earth and sand, a binder, and a hardening agent is discharged into water from a discharge tube, and a flocculant is spouted near the discharge end.

(作 用) 吐出端近傍で舞い上がる懸濁粒子は直らに凝集剤に接触
することにより凝集沈積することになる。
(Function) The suspended particles flying up near the discharge end will be flocculated and deposited by coming into direct contact with the flocculant.

(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 this invention.

図において、1は吐出端1aを水底地!3Fに向けた吐
出菅、2は該吐出菅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
送バイブである。
In the figure, 1 indicates that the discharge end 1a is at the bottom of the water! The discharge pipe 2 facing 3F is a flocculant pressure-feeding vibrator which is parallel to the outer circumference of the discharge pipe 1 and whose ejection end 2a is located at the periphery of the ejection end 1a.

吐出菅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 tube 1 by a pressure 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、ま
たは土砂と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 includes general earth and sand and a binder that imparts caking properties between the earth and sand particles and ensures a predetermined fluidity, or hardens between the earth and sand, the binder, and the earth and sand particles, It contains a hardening agent that 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 made of a water-soluble natural, semi-synthetic or synthetic polymer, and has the function of preventing the separation of particles and the incorporation of water through a kind of glue-like substance.

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lνにやく、ふのり。
To explain the binder specifically, water-soluble natural polymers include various starches, starches, and funori.

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、fキストリン、レバン。
Agar, sodium alginate, molasses, tragonth gum, gum arabic, f-kistrin, levan.

にかわ、ゼラヂン、カゼイン、コラーゲンなどを用いる
Glue, geladin, casein, collagen, etc. are used.

水溶性半合成高分子の例としては、ヒスコース。An example of a water-soluble semi-synthetic polymer is hiscose.

メチルセルロース、エチルセルロース、ヒトOキシエヂ
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。
Methylcellulose, ethylcellulose, human oxyedylcellulose, hydroxypropylmethylcellulose,
Carboxymethyl cellulose, soluble starch, carboxymethyl starch, dialdehyde starch, etc. are used.

水溶性合成高分子としては、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 polymer, polyvinyl alcohol, sodium polyacrylate, polyacrylamide, polyethylene oxide, etc. are used.

前記硬化剤は、普通ポルトランドセメン1−2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クアル1−
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。
The hardening agent may be ordinary Portland cement 1-2 blast furnace cement, fly ash cement, other cement materials, lime-based materials such as slaked lime, or Asqual 1-2.
The material is selected from the group consisting of blast furnace slag type materials and blast furnace slag type materials, or a combination thereof.

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。
This type of curing agent has the function of solidifying and stabilizing the soil quality of the earth and sand after being added, 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rtt部、および硬化
剤50〜300重堡部が最も好ましい値となっている。
In addition, the blending ratio of each binder and hardening agent to the soil and sand is determined by taking into account economic efficiency and degree of hardening.
The most preferable values are 1 to 5 parts by weight of the binder and 50 to 300 parts by weight of the curing agent per 00 parts by weight.

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菅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tl!3JiM4を生ずる。ここで、この懸濁層4は
凝集剤圧送バイブ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 fed into the discharge end 1a of the discharge pipe 1 in a slurry state, and there is almost no risk of suspension compared to general earth and sand. When the particle size of the material is fine or the discharge speed is high, there is a tl! 3JiM4 is generated. Here, this suspended layer 4 comes into contact with the flocculant spouted from the spouting end 2a of the flocculant-feeding vibrator 2, immediately coagulates, and settles on the sediment composition, thereby preventing pollution. Become.

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どの接触確率を高め、は
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 parts, the probability of contact with the suspended layer 4 can be increased and contamination can be almost completely prevented.

なJ3、前記凝集剤としてはPAC,硫酸バンドなどの
無償凝集剤あるいは高分子凝集剤の単独または混合物を
01用して用いる。
J3, as the flocculant, a free flocculant such as PAC or sulfuric acid, or a polymer flocculant alone or in a mixture is used.

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, for construction work in waters containing salt such as the sea, it is usually sufficient to use only a polymer flocculant.

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、71[機凝集剤が先に接触するようにバイ
ブを配置することが望ましい。
On the other hand, when used together, it is desirable to pump these flocculants through separate pipes and arrange the vibrator so that the flocculants come into contact first.

また、その使用量としては、前記懸iiB層4の1d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。
Furthermore, it has been confirmed that 1 to 5 g of the polymer flocculant per 1 d of the suspension iiB layer 4 can almost completely prevent water pollution.

次に第2図はこの発明方法の第2実施例を示1ちのであ
る。
Next, FIG. 2 shows a second embodiment of the method of this invention.

図において、吐出菅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。
In the figure, a suction end 10a of a submersible pump 10 is located at the periphery of a discharge end 1a of a discharge tube 1.

また、凝集剤圧送バイブ2の噴出端2bは水中ポンプ1
0の吸込み端10aに位置させている。
Further, the ejection end 2b of the flocculant pressure-feeding vibrator 2 is connected to the submersible pump 1.
It is located at the suction end 10a of 0.

以上の構成において、吐出菅1より土砂組成物3を吐出
した状態で、水中ポンプ1o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、同時に凝集剤圧送バイブ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 1o while discharging the earth and sand composition 3 from the discharge tube 1, the suspended layer 4 that flies up around the periphery of the discharge end 1a is all sucked into the suction end side of the submersible pump. , At the same time, flocculant pumping vibe 2
The flocculant spouted from the spouting end 2b is also taken into the submersible pump 10 from the suction end 10a. The suspended layer 4 and the flocculant are contacted and mixed in the submersible pump 10, and in this state is 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!lIE上に沈積することになる。
The discharged suspended layer 4 settles quickly due to the flocculating action of the flocculant, and becomes the bottom of the water! It will be deposited on the IIE.

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眩るために、より−・
層確実な汚濁防止効果を得ることになる。
In this embodiment, since the suspended layer flying up from the discharge end 1a is forcibly sucked in and comes into contact with the flocculant, the
This results in a reliable pollution prevention effect.

(発明の効果) 以上各実施例により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 explained in detail in each of the Examples above, according to the method of the present invention, a separate flocculation and sedimentation tank is required unlike the conventional method in order to completely prevent pollution when the sediment composition is put into water. Since there is no need to install or transport contaminated water to another location, it is possible to implement pollution prevention measures at an extremely low cost when the water is put into the water.

【図面の簡単な説明】[Brief explanation 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・・・・・・吐出菅      1a・・・吐出端2
・・・・・・凝集剤圧送バイブ 2a、2b・・・噴出
端3・・・・・・土砂組成物 第1図 第2図
FIG. 1 is an explanatory diagram showing a method of putting the device into water according to the first embodiment of the present invention, and FIG. 2 is an explanatory diagram showing the method of putting the product into water according to the second embodiment of the invention. 1...Discharge pipe 1a...Discharge end 2
...Flocculant pressure-feeding vibrator 2a, 2b...Ejection end 3...Sediment composition Fig. 1 Fig. 2

Claims (1)

【特許請求の範囲】[Claims] (1)土砂と粘結剤、また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菅より水中に吐出すると
ともに、該吐出端近傍に凝集剤を噴出するうよにしたこ
とを特徴とする土砂組成物の水中投入方法。
(1) Discharge a sediment composition formed by mixing soil and a binder, or a soil, a binder, and a hardening agent into water from a discharge tube, and spout a flocculant near the discharge end. A method for introducing a sediment composition into water, characterized by:
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 true JPS62215722A (en) 1987-09-22
JPH0633603B2 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)

Cited By (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

Citations (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

Patent Citations (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

Cited By (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

Also Published As

Publication number Publication date
JPH0633603B2 (en) 1994-05-02

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