JP3800375B2 - Mud disposal method - Google Patents

Mud disposal method Download PDF

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Publication number
JP3800375B2
JP3800375B2 JP26270497A JP26270497A JP3800375B2 JP 3800375 B2 JP3800375 B2 JP 3800375B2 JP 26270497 A JP26270497 A JP 26270497A JP 26270497 A JP26270497 A JP 26270497A JP 3800375 B2 JP3800375 B2 JP 3800375B2
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Japan
Prior art keywords
mud
water
slow
permeable bag
hardening
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JP26270497A
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Japanese (ja)
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JPH1177096A (en
Inventor
正夫 黒岩
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Obayashi Corp
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Obayashi Corp
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  • Treatment Of Sludge (AREA)

Description

【0001】
【発明の属する技術分野】
本発明は、主として海や湖沼あるいは河川の底から浚渫された泥土の処理方法に関する。
【0002】
【従来の技術】
海や湖沼あるいは河川の水質汚染が進行している場合には、かかる水質汚染の進行を阻止して良好な環境を取り戻すことが生態系維持の観点できわめて重要である。
【0003】
水質汚染が進行する原因としては、外部からの有機物流入および底泥からの栄養塩の溶出が挙げられ、したがって、湖沼の水質を改善するには、その底泥を浚渫して除去してやるのが効果的である。
【0004】
ところが、浚渫された泥土は含水比が高くて強度が小さいため、そのままで処分することも再利用することも難しい。そのため、かかる浚渫泥土に固化材を添加して強度増大を図ることが必要不可欠となる。
【0005】
一方、浚渫される泥土は、一般的にはかなりの容量となり、その処分場所を確保するのは容易ではない。したがって、浚渫泥土の減容化を図ることがもう一つの課題となる。
【0006】
【発明が解決しようとする課題】
しかしながら、含水比が高い浚渫泥土の強度を向上させるには大量の固化材が必要となるため、固化材の費用が高くつくとともに、かかる大量の固化材を添加することによって浚渫泥土の容量がさらに増加し、それを処理するために広大な用地を確保しなければならないという問題を生じていた。
【0007】
本発明は、上述した事情を考慮してなされたもので、浚渫泥土の減容化と固化材の節約とを達成可能な浚渫泥土の処理方法を提供することを目的とする。
【0008】
【課題を解決するための手段】
上記目的を達成するため、本発明に係る泥土の処理方法は請求項1に記載したように、泥土に遅硬性固化材を添加攪拌して混合泥土とし、該混合泥土を透水性袋体に充填して所定の間放置する泥土の処理方法であって、前記遅硬性固化材を遅硬性セメントで構成したものである。
また、本発明に係る泥土の処理方法は請求項2に記載したように、泥土に遅硬性固化材を添加攪拌して混合泥土とし、該混合泥土を透水性袋体に充填して所定の間放置する泥土の処理方法であって、前記遅硬性固化材を超遅延剤及びセメントで構成したものである。
【0009】
また、本発明に係る泥土の処理方法は、前記放置中において、前記混合泥土が充填された透水性袋体に所定の荷重を載荷するものである。
【0010】
また、本発明に係る泥土の処理方法は、前記放置中において、前記混合泥土が充填された透水性袋体を積み置きするものである。
【0011】
また、本発明に係る泥土の処理方法は、放置期間が経過した前記透水性袋体を盛土材、堤体材若しくは埋立材として再利用するものである。
【0012】
本発明に係る泥土の処理方法においては、まず、泥土に遅硬性固化材を添加撹拌し、混合泥土とする。次に、該混合泥土を透水性袋体に充填して所定の間放置する。
【0013】
このようにすると、透水性袋体の内部からは泥土に含まれていた水が圧密、毛細管現象等によって外側に浸出し、泥土が固化する頃には、該泥土の含水量は一定のレベルまで低下する。
【0014】
泥土には、海や湖沼あるいは河川の底から浚渫された泥土をはじめ、泥水シールド工法、地中連続壁工法等で生じた泥土が含まれる。
【0015】
遅硬性固化材としては、例えば遅硬性セメントを使用することが可能であり、特に数日程度以降に強度が発現するように配合しておくと、その間、十分な脱水作用が期待できる。具体的には、例えば、コンクリート打継部においてコールドジョイントを生じることなく新旧コンクリートを一体化するために使用される、いわゆる超遅延剤と呼ばれる添加剤を使用すればよい。
【0016】
なお、脱水によって泥土の含水量が低下するので、遅硬性固化材の添加量は、従来の場合よりも少なくて済む。
【0017】
透水性袋体は、泥土の重量に耐えられるものであればどのような材質かは問わないが、例えば織布、不織布を使用することができる。
【0018】
放置中、透水性袋体をどのように配置しておくかは任意であり、単に置いておくだけでも混合泥土の自重によってある程度の脱水が可能であるが、かかる透水性袋体に所定の荷重を載荷しておけば、上述の脱水作用が促進され、透水性袋体内に充填された混合泥土の含水量をより効率よく低下させることができる。
【0019】
混合泥土が充填された透水性袋体にどのようにして荷重を載荷するかは任意であり、例えば、重ならないように配置された透水性袋体の上に土を盛るといった方法が考えられるが、透水性袋体を数段に積み置きするようにすれば、比較的狭いスペースであっても、透水性袋体に十分な荷重を載荷することが可能となる。
【0020】
放置が終了した透水性袋体をどのように処分するかは任意であり、そのまま所定の廃棄物処分場に運搬して処分してもよいが、所定の脱水が行われているので内部から化学物質が溶出するおそれは少なく、しかも所定の強度も出ているので、これを、盛土材、堤体材若しくは埋立材として再利用すれば、廃棄物処分場を確保する必要がなくなるとともに資源の再利用にもなるので、環境保護に大いに寄与する。
【0021】
なお、本発明でいうところの放置とは、主として静置を指すが、振動を加えたり揺動させたりといった操作をも含むものとする。
【0022】
【発明の実施の形態】
以下、本発明に係る泥土の処理方法の実施の形態について、添付図面を参照して説明する。なお、従来技術と実質的に同一の部品等については同一の符号を付してその説明を省略する。
【0023】
図1は、本実施形態に係る泥土の処理方法の手順を示したフローチャート、図2は、各設備の配置図である。
【0024】
これらの図でわかるように、本実施形態に係る泥土の処理方法においては、まず、海や湖沼あるいは河川の底から泥土1を浚渫する(ステップ101)。浚渫にあたっては、例えば高濃度浚渫船を使用するのがよい。
【0025】
次に、浚渫された泥土1を圧送管2を介して沈殿池3にいったん投入し、しかる後に沈殿した浚渫泥土4をサンドポンプ5で吸引して撹拌槽6に投入する(ステップ102)。
【0026】
次に、撹拌槽6に遅硬性固化材としての遅硬性セメント7を添加撹拌し、混合泥土8とする(ステップ103)。遅硬性セメント7は、2〜7日程度以降に強度が発現するように配合しておくと、その間、十分な脱水作用が期待できる。具体的には、例えば、コンクリート打継部においてコールドジョイントを生じることなく新旧コンクリートを一体化するために使用される、いわゆる超遅延剤と呼ばれる添加剤を使用すればよい。
【0027】
次に、撹拌槽6内の混合泥土8をサンドポンプ9及び送泥管10を介して透水性袋体11を配置した箇所まで送り、該混合泥土を透水性袋体11に充填して、所定の期間放置する(ステップ104)。
【0028】
図3は、透水性袋体11を二段積みするとともに、それらのうち、下段に配置されたものから順次充填している様子を示したものである。
【0029】
透水性袋体11は、混合泥土8が充填されても破れない程度の引張強度、例えば50kgf/cm2程度の引張強度を有する織布や不織布で構成するのがよい。なお、ここでいう透水性とは、例えば10-2cm/sオーダーの透水性を有するものが好ましい。
【0030】
このように混合泥土8が充填された透水性袋体11を二段積みにして放置しておくと、該透水性袋体の内部から浚渫泥土4に含まれていた水が外側に浸出し、浚渫泥土4が遅硬性セメント7によって固化する頃には、該浚渫泥土の含水量は一定のレベルまで低下する。
【0031】
なお、透水性袋体11からの浸出水については、これを排水溝12に集めた上、シルト分を多量に含んでいるのであれば、凝集剤を添加して凝集沈下処理を行った後、河川に放流すればよい。
【0032】
次に、放置が終了した透水性袋体11を搬出し、盛土材、堤体材若しくは埋立材として再利用する(ステップ105)。
【0033】
以上説明したように、本実施形態に係る泥土の処理方法によれば、浚渫泥土4に遅硬性セメント7を添加撹拌して混合泥土8とし、これを透水性袋体11に充填して放置するようにしたので、浚渫泥土4が遅硬性セメント7によって固化する前に該泥土に含まれていた水分が透水性袋体11から浸出する。すなわち、含水比が高い浚渫泥土4は、遅硬性セメント7による水和反応が開始する前に、一定のレベルまで脱水が行われることとなり、かくして、一定の減容化がなされた状態で浚渫泥土4の強度を改善することが可能となる。また、浚渫泥土4の含水量が脱水によって低下するので、遅硬性セメント7の所要量は、従来の場合よりも少なくて済む。
【0034】
図4は、浚渫泥土を透水性袋体に充填することによって含水比がどのように低下するかを調べた実験であり、当初400%であった含水比が60日経過後は、100%に低下している様子がわかる。
【0035】
なお、フィルタプレス等の機械脱水を行ってから固化材を添加する方法を採用すれば、本実施形態と同様、浚渫泥土の減容化並びに固化材の節約を達成することができるが、機械脱水を行うための設備は大がかりであり、そのために別途設置費用や維持費用がかかることを考えれば、本実施形態に係る浚渫泥土の処理方法は、きわめて安価でなおかつ浚渫泥土の減容化と固化材の節約を同時に達成することができる有用な方法であると言える。
【0036】
また、本実施形態によれば、放置中、混合泥土8が充填された透水性袋体11を積み置きするようにしたので、脱水作用が促進され、浚渫泥土4の含水量をより効率よく低下させることができるとともに、比較的狭いスペースであっても、透水性袋体11に十分な荷重を載荷して脱水を効率的に行うことが可能となる。これは、天日乾燥に要する面積に比べれば大幅な面積縮小となる。
【0037】
また、本実施形態によれば、脱水固化が進行した透水性袋体11の内部からは化学物質が溶出するおそれが少なく、しかも所定の強度も出ているので、これを盛土材、堤体材若しくは埋立材として再利用することによって、廃棄物処分場を確保する必要がなくなるとともに資源の再利用にもなるので、環境保護に大いに寄与する。
【0038】
本実施形態では、放置期間が経過して脱水固化が終了した透水性袋体11を搬出し、これを堤体材等に再利用するようにしたが、これに代えてそのまま廃棄物処分場に廃棄処分するようにしてもよい。かかる構成においては、浚渫泥土が所定のレベルまで減容化された状態となっているので、廃棄物処分場での必要容量が少なくて済む。また、透水性袋体11を搬出せずにそのまま残し、その上に盛土等を施して緑化を行えば、適度な起伏のある公園を造成することも可能となる。
【0039】
【発明の効果】
以上述べたように、本発明に係る泥土の処理方法によれば、泥土が遅硬性固化材によって固化する前に該泥土に含まれていた水分が透水性袋体から浸出する。すなわち、含水比が高い泥土は、遅硬性固化材による固化反応が開始する前に、一定のレベルまで脱水が行われることとなり、一定の減容化がなされた状態で泥土の強度を改善することが可能となる。また、泥土の含水量が脱水によって低下するので、遅硬性固化材の所要量は、従来の場合よりも少なくて済む。
【0040】
また、請求項3に係る本発明の泥土の処理方法によれば、脱水作用が促進され、泥土の含水量をより効率よく低下させることができるという効果も奏する。
【0041】
また、請求項4に係る本発明の泥土の処理方法によれば、透水性袋体を数段に積み置きするようにすれば、比較的狭いスペースであっても、透水性袋体に十分な荷重を載荷することが可能となるという効果も奏する。
【0042】
また、請求項5に係る本発明の泥土の処理方法によれば、廃棄物処分場を確保する必要がなくなるとともに資源の再利用にもなるので、環境保護に大いに寄与するという効果も奏する。
【0043】
【図面の簡単な説明】
【図1】本実施形態に係る泥土の処理方法の手順を示したフローチャート。
【図2】本実施形態に係る泥土の処理方法を行う設備の配置図。
【図3】図2のA―A線方向に沿う詳細断面図。
【図4】本実施形態に係る泥土の処理方法の作用を示したグラフ。
【符号の説明】
4 浚渫泥土(泥土)
7 遅硬性セメント(遅硬性固化材)
8 混合泥土
11 透水性袋体
[0001]
BACKGROUND OF THE INVENTION
The present invention mainly relates to a method for treating mud soil dredged from the bottom of a sea, lake, or river.
[0002]
[Prior art]
When water pollution of the sea, lakes, or rivers is progressing, it is extremely important from the viewpoint of maintaining the ecosystem to prevent such water pollution from progressing and restore a good environment.
[0003]
The cause of water pollution is the inflow of organic substances from the outside and the elution of nutrients from the bottom mud. Therefore, it is effective to remove and remove the bottom mud to improve the water quality of the lake. Is.
[0004]
However, dredged mud has a high water content and low strength, so it is difficult to dispose of it as it is or to reuse it. Therefore, it is essential to increase the strength by adding a solidifying material to the dredged clay.
[0005]
On the other hand, dredged mud generally has a considerable capacity, and it is not easy to secure a disposal site. Therefore, another challenge is to reduce the volume of dredged mud.
[0006]
[Problems to be solved by the invention]
However, in order to improve the strength of dredged mud with a high water content, a large amount of solidifying material is required, so the cost of the solidifying material is high, and adding such a large amount of solidifying material further increases the capacity of dredged mud soil. Increasingly, there was a problem that a vast land had to be secured to handle it.
[0007]
The present invention has been made in consideration of the above-described circumstances, and an object of the present invention is to provide a method for treating dredged mud that can achieve volume reduction of dredged mud and saving of solidified material.
[0008]
[Means for Solving the Problems]
In order to achieve the above object, the method for treating mud according to the present invention, as described in claim 1, adds a slow-hardening solidifying material to the mud and stirs to form mixed mud, and the mixed mud is filled in a water-permeable bag. Then, a method for treating mud that is allowed to stand for a predetermined period of time, wherein the slow-hardening solidified material is composed of slow-hardening cement.
Further, according to the method for treating mud according to the present invention, as described in claim 2, a slow-hardening solidifying material is added to the mud and stirred to form mixed mud, and the mixed mud is filled in a permeable bag body for a predetermined period. A method for treating mud to be left, wherein the slow-hardening solidifying material is composed of a super-retarding agent and cement.
[0009]
In the mud treatment method according to the present invention, a predetermined load is loaded on the water-permeable bag filled with the mixed mud during the standing.
[0010]
In the mud treatment method according to the present invention, the water-permeable bag filled with the mixed mud is stacked during the standing.
[0011]
Moreover, the processing method of the mud according to the present invention is to reuse the water-permeable bag body after the leaving period has passed as a banking material, a bank body material or a landfill material.
[0012]
In the method for treating mud according to the present invention, first, a slow-hardening solidifying material is added to the mud and stirred to obtain mixed mud. Next, the mixed mud is filled in a water-permeable bag and left for a predetermined period.
[0013]
In this way, the water contained in the mud is squeezed out from the inside of the water-permeable bag body by compaction, capillary action, etc., and when the mud is solidified, the water content of the mud reaches a certain level. descend.
[0014]
The mud includes mud mud drowned from the bottom of the sea, lakes, or rivers, as well as mud produced by the mud shield method, the underground continuous wall method, and the like.
[0015]
For example, a slow-hardening cement can be used as the slow-hardening solidified material, and if it is formulated so that strength develops especially after several days, sufficient dehydrating action can be expected during that time. Specifically, for example, an additive called a so-called super-retarding agent that is used to integrate old and new concrete without producing a cold joint in the concrete joint portion may be used.
[0016]
In addition, since the water content of the mud is reduced by dehydration, the amount of the slow-hardening solidifying material added can be smaller than in the conventional case.
[0017]
The material of the water-permeable bag is not limited as long as it can withstand the weight of the mud. For example, a woven fabric or a non-woven fabric can be used.
[0018]
It is arbitrary how the permeable bag body is arranged during the standing, and even if it is left alone, it can be dehydrated to some extent by the weight of the mixed mud, but a predetermined load is applied to the permeable bag body. Is loaded, the above-mentioned dehydration action is promoted, and the water content of the mixed mud filled in the water-permeable bag can be reduced more efficiently.
[0019]
How to load a water-permeable bag filled with mixed mud is arbitrary. For example, a method of placing soil on a water-permeable bag arranged so as not to overlap is conceivable. If the water-permeable bags are stacked in several stages, a sufficient load can be loaded on the water-permeable bags even in a relatively narrow space.
[0020]
It is arbitrary how to dispose of the permeable bag after it has been left unattended, and it may be transported to a predetermined waste disposal site and disposed of as it is. There is little risk of the substance leaching out, and it also has a predetermined strength. If this is reused as embankment material, embankment material or landfill material, it will not be necessary to secure a waste disposal site and resources will be re-used. Since it is also used, it contributes greatly to environmental protection.
[0021]
The term “leaving” as used in the present invention mainly refers to standing, but also includes operations such as applying vibration and swinging.
[0022]
DETAILED DESCRIPTION OF THE INVENTION
Embodiments of a mud treatment method according to the present invention will be described below with reference to the accompanying drawings. Note that components that are substantially the same as those of the prior art are assigned the same reference numerals, and descriptions thereof are omitted.
[0023]
FIG. 1 is a flowchart showing a procedure of a mud treatment method according to the present embodiment, and FIG. 2 is a layout diagram of each facility.
[0024]
As can be seen from these drawings, in the mud processing method according to the present embodiment, the mud 1 is first dredged from the bottom of the sea, lake, or river (step 101). For dredging, for example, a high concentration dredger should be used.
[0025]
Next, the dredged mud 1 is once put into the settling basin 3 via the pressure feed pipe 2, and then the dredged mud 4 is sucked by the sand pump 5 and put into the stirring tank 6 (step 102).
[0026]
Next, a slow-hardening cement 7 as a slow-hardening solidifying material is added to the stirring tank 6 and stirred to form a mixed mud 8 (step 103). When the slow-hardening cement 7 is blended so that strength develops after about 2 to 7 days, a sufficient dehydrating action can be expected during that time. Specifically, for example, an additive called a so-called super-retarding agent that is used to integrate old and new concrete without producing a cold joint in the concrete joint portion may be used.
[0027]
Next, the mixed mud 8 in the agitation tank 6 is sent to the place where the water permeable bag 11 is disposed via the sand pump 9 and the mud pipe 10, and the mixed mud is filled into the water permeable bag 11, (Step 104).
[0028]
FIG. 3 shows a state in which the water-permeable bag bodies 11 are stacked in two stages and are sequentially filled from those arranged in the lower stage.
[0029]
The water permeable bag 11 is preferably composed of a woven fabric or a non-woven fabric having a tensile strength that does not break even when the mixed mud 8 is filled, for example, a tensile strength of about 50 kgf / cm 2 . In addition, what has a water permeability of a 10 <-2 > cm / s order, for example here is preferable.
[0030]
When the water-permeable bags 11 filled with the mixed mud 8 are left in a two-stage stack, the water contained in the dredged mud 4 leaches out from the inside of the water-permeable bags, When the dredged mud 4 is solidified by the slow-hardening cement 7, the water content of the dredged mud is lowered to a certain level.
[0031]
In addition, about the leachate from the water-permeable bag 11, after collecting this in the drainage groove 12, if it contains a large amount of silt, after adding a flocculant and performing a cohesive settlement process, It only has to be discharged into the river.
[0032]
Next, the water-permeable bag body 11 that has been left untreated is carried out and reused as a banking material, a bank body material, or a landfill material (step 105).
[0033]
As described above, according to the method for treating mud according to the present embodiment, the slow-hardening cement 7 is added to the dredged mud 4 and stirred to form the mixed mud 8, which is filled in the permeable bag 11 and left to stand. Since it did in this way, before the dredged mud 4 solidifies with the slow-hardening cement 7, the water | moisture content contained in this mud oozes out from the water-permeable bag body 11. FIG. That is, the dredged clay 4 having a high water content is dehydrated to a certain level before the hydration reaction by the slow-hardening cement 7 is started, and thus the dredged mud is in a state where the volume is reduced to a certain level. The strength of 4 can be improved. Further, since the water content of the dredged clay 4 is reduced by dehydration, the required amount of the slow-hardening cement 7 can be smaller than in the conventional case.
[0034]
FIG. 4 is an experiment for examining how the water content ratio is reduced by filling the permeable bag with dredged mud soil. The water content ratio, which was 400% at the beginning, decreases to 100% after 60 days. You can see how they are doing.
[0035]
If a method of adding solidification material after performing mechanical dewatering such as a filter press is adopted, volume reduction of dredged mud and saving of solidified material can be achieved as in this embodiment. In view of the fact that the equipment for carrying out the process is large, and that additional installation and maintenance costs are required, the dredged mud disposal method according to the present embodiment is extremely inexpensive, and the dredged mud volume reduction and solidification material. It can be said that this is a useful method that can simultaneously achieve savings.
[0036]
Moreover, according to this embodiment, since the water-permeable bag body 11 filled with the mixed mud 8 was stacked during standing, the dehydration action was promoted, and the water content of the dredged mud 4 was reduced more efficiently. In addition, even in a relatively narrow space, a sufficient load can be loaded on the water permeable bag 11 to efficiently perform dehydration. This is a significant area reduction compared to the area required for sun drying.
[0037]
Moreover, according to this embodiment, there is little possibility that a chemical substance elutes from the inside of the water-permeable bag 11 which has been dehydrated and solidified, and has a predetermined strength. Or by reusing it as landfill material, it becomes unnecessary to secure a waste disposal site and reuse of resources, which greatly contributes to environmental protection.
[0038]
In the present embodiment, the water-permeable bag body 11 that has been dehydrated and solidified after the leaving period has passed is taken out and reused as a levee body material or the like. It may be disposed of. In such a configuration, the volume of dredged mud is reduced to a predetermined level, so that the required capacity at the waste disposal site is small. In addition, if the water-permeable bag 11 is left without being carried out and is greened by applying embankment or the like on it, a park with moderate undulations can be created.
[0039]
【The invention's effect】
As described above, according to the method for treating mud according to the present invention, moisture contained in the mud is leached from the water-permeable bag before the mud is solidified by the slow-hardening solidifying material. In other words, mud with a high water content ratio is dewatered to a certain level before the solidification reaction with the slow-hardening solidification material starts, and the strength of the mud is improved with a certain volume reduction. Is possible. Further, since the water content of the mud is reduced by dehydration, the required amount of the slow-hardening solidifying material is smaller than in the conventional case.
[0040]
Moreover, according to the method for treating mud according to the third aspect of the present invention, the dewatering action is promoted, and the water content of the mud can be reduced more efficiently.
[0041]
Further, according to the mud treatment method of the present invention according to claim 4, if the water-permeable bags are stacked in several stages, the water-permeable bag is sufficient even in a relatively small space. There is also an effect that a load can be loaded.
[0042]
Moreover, according to the mud disposal method of the present invention according to claim 5, since it is not necessary to secure a waste disposal site and the resources are reused, there is also an effect of greatly contributing to environmental protection.
[0043]
[Brief description of the drawings]
FIG. 1 is a flowchart showing a procedure of a mud treatment method according to the present embodiment.
FIG. 2 is a layout view of facilities for performing a mud disposal method according to the present embodiment.
3 is a detailed cross-sectional view taken along the line AA in FIG. 2;
FIG. 4 is a graph showing the operation of the mud treatment method according to the present embodiment.
[Explanation of symbols]
4 dredged mud
7 Slow-hardening cement (slow-hardening solidification material)
8 Mixed mud 11 Permeable bag

Claims (5)

泥土に遅硬性固化材を添加攪拌して混合泥土とし、該混合泥土を透水性袋体に充填して所定の間放置する泥土の処理方法であって、前記遅硬性固化材を遅硬性セメントで構成したことを特徴とする泥土の処理方法。  A method for treating mud by adding a slow-hardening solidifying material to mud and stirring to form mixed mud, filling the mixed mud in a water-permeable bag and leaving it for a predetermined time, wherein the slow-hardening solidifying material is made of slow-hardening cement. A method for treating mud characterized by comprising. 泥土に遅硬性固化材を添加攪拌して混合泥土とし、該混合泥土を透水性袋体に充填して所定の間放置する泥土の処理方法であって、前記遅硬性固化材を超遅延剤及びセメントで構成したことを特徴とする泥土の処理方法。  A method for treating mud by adding and stirring a slow-hardening solidifying material to a mud to make a mixed mud, filling the mixed mud in a water-permeable bag and leaving it for a predetermined time, wherein the slow-hardening solidifying material is a super-retarding agent and A method for treating mud characterized by comprising cement. 前記放置中において、前記混合泥土が充填された透水性袋体に所定の荷重を載荷する請求項1乃至請求項2のいずれか一記載の泥土の処理方法。  The method for treating mud according to any one of claims 1 to 2, wherein a predetermined load is loaded on the water permeable bag filled with the mixed mud during the standing. 前記放置中において、前記混合泥土が充填された透水性袋体を積み置きする請求項3記載の泥土の処理方法。  The method for treating mud according to claim 3, wherein the permeable bag filled with the mixed mud is stacked during the standing. 放置期間が経過した前記透水性袋体を盛土材、堤体材若しくは埋立材として再利用する請求項1乃至請求項2のいずれか一記載の泥土の処理方法。  The method for treating mud according to any one of claims 1 to 2, wherein the water permeable bag after the leaving period has elapsed is reused as a banking material, a bank material, or a landfill material.
JP26270497A 1997-09-10 1997-09-10 Mud disposal method Expired - Fee Related JP3800375B2 (en)

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JP2006281080A (en) * 2005-03-31 2006-10-19 Sumitomo Osaka Cement Co Ltd Processing method of contaminated soil
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CN110922136B (en) * 2019-12-13 2021-06-01 福州大学 Water permeable brick prepared from dredged mud and preparation method thereof
CN114427230B (en) * 2021-12-23 2022-10-21 黄河水利委员会黄河水利科学研究院 Ring type cavity lattice earthwork tube bag structure

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