JP2640616B2 - Solidification method of submerged sludge - Google Patents

Solidification method of submerged sludge

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Publication number
JP2640616B2
JP2640616B2 JP20209093A JP20209093A JP2640616B2 JP 2640616 B2 JP2640616 B2 JP 2640616B2 JP 20209093 A JP20209093 A JP 20209093A JP 20209093 A JP20209093 A JP 20209093A JP 2640616 B2 JP2640616 B2 JP 2640616B2
Authority
JP
Japan
Prior art keywords
soil
sludge
solidifying agent
solidified
water
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
JP20209093A
Other languages
Japanese (ja)
Other versions
JPH0731997A (en
Inventor
明 長縄
正 林
正次 大森
善一 間篠
好則 渡辺
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.)
CHODA KAKO KENSETSU KK
Original Assignee
CHODA KAKO KENSETSU KK
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Filing date
Publication date
Application filed by CHODA KAKO KENSETSU KK filed Critical CHODA KAKO KENSETSU KK
Priority to JP20209093A priority Critical patent/JP2640616B2/en
Publication of JPH0731997A publication Critical patent/JPH0731997A/en
Application granted granted Critical
Publication of JP2640616B2 publication Critical patent/JP2640616B2/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】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は、水底汚泥の固化処理方
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 method for solidifying submerged sludge.

【0002】[0002]

【従来の技術】港湾、河川、湖沼等の浚渫工事を行う場
合、含泥率(浚渫した水底汚泥中に占める水底に堆積し
ていた汚泥の割合)を高い状態で浚渫することが難し
く、多量の余分な水を同伴せざるを得ず、浚渫量が多大
となる。従って、水底汚泥は、浚渫した水底汚泥は、こ
れを貯留池に静置し、汚泥を構成する土粒子を沈降させ
た後、その沈降物層上に形成された余剰水を除去し、沈
降物を固化することによって処理されている。この場
合、水底汚泥中の土粒子の沈降を促進するためや、沈降
物を同時に脱水固化させるために、浚渫した水底汚泥に
直接土粒子固化剤を添加することも知られている(特開
昭61−149291号)。しかし、余剰水を分離した
後の沈降物に土粒子固化剤を添加混合する場合、沈降物
に土粒子固化剤を均一に混合するのに大きな困難を生じ
た。また、浚渫した水底汚泥に直接土粒子固化剤を添加
した場合は沈降物の脱水固化が不充分である場合が多
く、早期にトラック輸送に適するような脱水固化物を得
るのが困難であった。この場合、脱水機械を用いてその
改善を図ることも考えられているが、膨大な浚渫量を取
り扱う浚渫工事においては経済的ではない。
2. Description of the Related Art When performing dredging work for harbors, rivers, lakes and marshes, it is difficult to dredge the mud at a high mud content (the ratio of the sludge deposited on the water bottom in the dredged bottom sludge). Dredging amount is unavoidable. Therefore, the submerged sludge, dredged submerged sludge is allowed to stand still in a reservoir to settle the soil particles constituting the sludge, and then the excess water formed on the sediment layer is removed, and the sediment is removed. Has been treated by solidification. In this case, it is also known to add a soil particle solidifying agent directly to the dredged submarine sludge in order to promote the sedimentation of the soil particles in the submarine sludge and to simultaneously dehydrate and solidify the sediment (Japanese Unexamined Patent Publication No. 61-149291). However, when the soil particle hardening agent is added to and mixed with the sediment after the surplus water is separated, it is very difficult to uniformly mix the soil particle hardening agent into the sediment. In addition, when the soil particle solidifying agent was directly added to the dredged submerged sludge, the dewatering and solidification of the sediment was often insufficient, and it was difficult to obtain a dewatered and solidified material suitable for truck transportation at an early stage. . In this case, it is considered that the improvement is performed by using a dehydrating machine, but it is not economical in the dredging work that handles a huge amount of dredging.

【0003】[0003]

【発明が解決しようとする課題】本発明は、全体の作業
性にすぐれるとともに、水底汚泥と土粒子固化剤との混
合物の短期間の静置によりトラック輸送可能な固化土を
得ることのできる経済的な水底汚泥の固化処理方法を提
供することをその課題とする。
DISCLOSURE OF THE INVENTION The present invention has excellent overall workability and can obtain solidified soil which can be transported by truck by allowing a mixture of submerged sludge and a soil particle solidifying agent to stand for a short period of time. It is an object of the present invention to provide an economical method for solidifying submerged sludge.

【0004】[0004]

【課題を解決するための手段】本発明者らは、前記課題
を解決すべく鋭意研究を重ねた結果、本発明を完成する
に至った。即ち、本発明によれば、水底汚泥の固化処理
方法において、(i)真空吸引方式により水底汚泥を浚
渫し、その移送過程で連続的に土粒子固化剤を混合する
工程、(ii)得られた混合物を貯留池に投入する工程、
(iii)貯留池に投入した混合物を静置して水底汚泥に含
まれる土粒子と土粒子固化剤からなる沈降物層を形成さ
せる工程、(iv)沈降物層の上部に形成された余剰水を
除去する工程、(v)沈降物層を含水比300〜400
%の固化土が得られるまで静置する工程、(vi)固化土
の一部を堀起し、周辺の固化土の上に積み上げる工程、
(vii)固化土を堀起した跡の凹部に固化土に含まれる余
剰水を滲出させ、含水比200〜300%の固化土を生
成させる工程、(viii)凹部に滞留する滲出水を除去する
工程を含むことを特徴とする水底汚泥の固化処理方法が
提供される。
Means for Solving the Problems The present inventors have conducted intensive studies to solve the above-mentioned problems, and as a result, have completed the present invention. That is, according to the present invention, in the method for solidifying submerged sludge, (i) a step of dredging submerged sludge by a vacuum suction method and continuously mixing a soil particle solidifying agent in a transfer process thereof, (ii) obtained. Charging the mixture into the reservoir,
(iii) a step of allowing the mixture charged into the reservoir to stand to form a sediment layer formed of soil particles and a soil particle solidifying agent contained in the bottom sediment; (iv) surplus water formed on the upper part of the sediment layer Removing (v) the sediment layer with a water content of 300 to 400;
(Vi) digging a part of the solidified soil and stacking it on the surrounding solidified soil,
(vii) a step of oozing excess water contained in the solidified soil into a concave portion where the solidified soil has been excavated to generate solidified soil having a water content of 200 to 300%, and (viii) removing exuded water remaining in the concave portion. There is provided a method for solidifying submerged sludge, comprising the steps of:

【0005】本発明を実施するには、先ず、水底に堆積
する汚泥を水底から分離回収(浚渫)する。水底汚泥の
分離回収は、真空吸引装置を用いて行うことができる。
また、回収する水底汚泥の含水比は、堆積する汚泥の性
状と、真空吸引装置の先端を水底汚泥中に挿入する深度
によって変化するが、作業効率と分離回収する水底汚泥
の量を勘案し、500〜1000%程度にコントロール
するのが好ましい。本明細書中で言う汚泥の含水比と
は、汚泥中に含まれる土粒子重量(汚泥の乾燥物重量)
に対する汚泥中の水分重量比(%)を意味する。真空吸
引装置による吸引により分離回収された水底汚泥は、こ
れを土粒子固化剤混合装置に移送し、土粒子固化剤と均
一混合する。混合装置は、通常、陸上の適当な場所に設
置され、この装置までの水底汚泥の移送は配管を用いた
加圧輸送法により行うことができる。水底汚泥を分離回
収するための真空吸引装置及び水底汚泥を圧送するため
のポンプ装置は、陸上に浮べた船体に設置することがで
きる。また、水底汚泥を圧送する配管は、この船体に設
置されたポンプ装置と土粒子固化剤混合装置との間を連
結する。このような水底汚泥の分離回収系と水底汚泥圧
送系を用いることにより、周囲環境に悪影響を与えるこ
となく水底汚泥を土粒子混合装置にまで移送することが
できる。
[0005] In order to carry out the present invention, first, sludge deposited on the water bottom is separated and recovered (dredged) from the water bottom. Separation and recovery of water bottom sludge can be performed using a vacuum suction device.
In addition, the water content of the collected bottom sediment varies depending on the properties of the deposited sludge and the depth at which the tip of the vacuum suction device is inserted into the bottom sediment, but taking into account the working efficiency and the amount of separated bottom sediment, It is preferable to control it to about 500 to 1000%. The sludge water content ratio referred to in this specification is the weight of soil particles contained in sludge (the weight of dried sludge).
Means the weight ratio (%) of the water content in the sludge. The submerged sludge separated and collected by the suction by the vacuum suction device is transferred to a soil particle solidifying agent mixing device and uniformly mixed with the soil particle solidifying agent. The mixing apparatus is usually installed at an appropriate place on land, and the transfer of the submarine sludge to this apparatus can be performed by a pressurized transport method using piping. The vacuum suction device for separating and recovering the submarine sludge and the pump device for pumping the submarine sludge can be installed on a hull floating on land. Further, a pipe for pumping the submerged sludge connects the pump device installed on the hull and the soil particle solidifying agent mixing device. By using such a submerged sludge separation and recovery system and a submerged sludge pumping system, the submerged sludge can be transferred to the soil particle mixing device without adversely affecting the surrounding environment.

【0006】土粒子固化剤混合装置に移送された水底汚
泥は、ここで土粒子固化剤と均一に混合される。混合装
置としては、攪拌羽根を有する通常の攪拌混合装置を用
いることができる。土粒子固化剤としては、土粒子と反
応し、これを固化する作用を有するものであればどのよ
うなものでも使用することができるが、セメント系固化
剤を好ましく用いることができる。セメント系固化剤と
しては、高炉水滓/ポルトランドセメント/石コウ系固
化剤、硫酸変成高炉滓/ポルトランドセメント系固化
剤、硫酸変性高炉滓/ポルトランドセメント/石コウ系
固化剤の他、高炉セメント等の固化剤を挙げることがで
きる。このようなセメント系固化剤は、例えば、特開昭
55−102677号公報や、特開昭56−10092
0号公報、特開昭57−174523号公報、特開昭5
7−030783号公報、特開昭58−032680号
公報等に記載されている。本発明で用いる好ましい固化
剤は、高炉水滓:73〜18重量%、好ましくは54〜
34重量%と、ポルトランドセメント:70〜16重量
%、好ましくは50〜30重量%と、石コウ:2〜38
重量%、好ましくは10〜25重量%からなるものであ
る。水底汚泥に対する土粒子固化剤の添加量は、水底汚
泥中の土粒子100重量部に対して、50〜150重量
部、好ましくは70〜120重量部の割合である。土粒
子固化剤は、粉末状又はスラリー状(固化剤と水との混
合液)で水底汚泥に添加されるが、好ましくはスラリー
状で添加される。土粒子固化剤をスラリー状で添加する
場合、スラリー中の固化剤濃度は25〜63重量%、好
ましくは35〜60重量%である。本発明における水底
汚泥と土粒子固化剤との混合は、配管内においてあるい
は配管と配管との間に設けた攪拌混合装置を用いて行う
ことができ、その混合作業は容易であり、しかも均一に
行うことができる。
[0006] The submerged sludge transferred to the soil particle solidifying agent mixing device is uniformly mixed with the soil particle solidifying agent here. As the mixing device, an ordinary stirring and mixing device having stirring blades can be used. As the soil particle hardening agent, any material can be used as long as it reacts with the soil particles and has an action of solidifying the same, but a cement-based hardening agent can be preferably used. Examples of cement-based solidifying agents include blast furnace slag / Portland cement / calcium-based solidifying agent, sulfuric acid-modified blast furnace slag / Portland cement-based solidifying agent, sulfuric acid-modified blast-furnace slag / Portland cement / calcium-based solidifying agent, blast furnace cement, etc. Solidifying agent. Such cement-based solidifying agents are disclosed, for example, in JP-A-55-102677 and JP-A-56-10092.
0, JP-A-57-174523 and JP-A-5-174523.
No. 7,030,783 and JP-A-58-032680. The preferred solidifying agent used in the present invention is blast furnace slag: 73 to 18% by weight, preferably 54 to 18% by weight.
34% by weight, Portland cement: 70 to 16% by weight, preferably 50 to 30% by weight, stone masonry: 2 to 38%
%, Preferably 10 to 25% by weight. The amount of the soil particle solidifying agent added to the bottom sediment is 50 to 150 parts by weight, preferably 70 to 120 parts by weight, based on 100 parts by weight of the soil particles in the bottom sediment. The soil particle solidifying agent is added to the submerged sludge in the form of powder or slurry (mixed liquid of the solidifying agent and water), but is preferably added in the form of slurry. When the soil particle solidifying agent is added in the form of a slurry, the solidifying agent concentration in the slurry is 25 to 63% by weight, preferably 35 to 60% by weight. The mixing of the submerged sludge and the soil particle solidifying agent in the present invention can be performed using a stirring and mixing device provided in a pipe or between a pipe and a pipe, and the mixing operation is easy and uniform. It can be carried out.

【0007】水底汚泥と土粒子固化剤との混合物は、こ
れを貯留池(ピット)に投入し、静置する。混合装置か
ら貯留池までの混合物の移送は配管を用いて圧送するこ
とができる。貯留池は、コンクリート製の大型貯槽その
他任意の貯槽の他、素堀りピットも利用することができ
る。この貯留池の深さは制約を受けるものではないが、
少なくとも1.5m以上、好ましくは2〜3mである。
貯留池の面積は特に制約されず、投入する混合物量に応
じて適当に選べばよい。また、混合物の貯留池の数は何
ら制約されず、1つ又は複数であることができる。
[0007] The mixture of the submerged sludge and the soil particle solidifying agent is charged into a reservoir (pit) and allowed to stand. The transfer of the mixture from the mixing device to the reservoir can be pumped using piping. The reservoir may be a large concrete pit or any other pit, as well as an unpitted pit. The depth of this reservoir is not restricted,
It is at least 1.5 m, preferably 2-3 m.
The area of the reservoir is not particularly limited, and may be appropriately selected according to the amount of the mixture to be charged. Also, the number of reservoirs for the mixture is not limited at all and can be one or more.

【0008】水底汚泥と土粒子固化剤との混合物を貯留
池に投入し、静置する場合、その貯留池における混合物
の投入量には特に制約はなく、作業を考慮し、できるだ
け多く投入すれば良い。混合物を貯留池に静置すると、
汚泥中の土粒子と固化剤との混合物がしだいに沈降して
沈降物層が形成され、その上部には余剰水層が形成され
る。この余剰水層は予め貯留池に堰を設けておき、その
調節により排出することもできるが、吸引ポンプにより
除去するのが効率的である。この余剰水の除去は、混合
物を貯留池に投入静置した後1〜2日目に行うことがで
きる。貯留池から除去された余剰水は、余水ピット(別
の貯留池)に移送し、ここに貯留する。この余剰水は、
通常、固化剤によるアルカリ性を示すことから、余剰水
はこの貯留池において曝気(空気吹込み)や炭酸ガス吹
込みあるいは、硫酸等の薬剤投入により中和し、更に必
要であれば懸濁物を除去したのち、河川に放流する。
When the mixture of the submerged sludge and the soil particle solidifying agent is charged into the reservoir and allowed to stand still, the amount of the mixture in the reservoir is not particularly limited. good. When the mixture is left in the reservoir,
The mixture of the soil particles in the sludge and the solidifying agent gradually settles to form a sediment layer, and an excess water layer is formed above the sediment layer. This surplus water layer can be discharged in advance by providing a weir in the reservoir and adjusting it, but it is more efficient to remove it by a suction pump. The removal of the surplus water can be performed one to two days after the mixture is charged and left in the reservoir. Excess water removed from the reservoir is transferred to a spill pit (another reservoir) and stored there. This surplus water is
Normally, since the alkalinity is exhibited by the solidifying agent, excess water is neutralized in this reservoir by aeration (air blowing), carbon dioxide gas blowing, or injection of a chemical such as sulfuric acid. After removal, release to river.

【0009】貯留池における土粒子と固化剤との混合物
からなる沈降物層は、土粒子と固化剤との反応により固
化し、その強度を増加し、固化土となる。本発明では、
沈降物の含水比が300〜400%程度になった時点
(水底汚泥と固化剤との混合物から余剰水を分離後1〜
4日目)において、その沈降物(固化土)の一部を堀起
し、その堀起した固化土をその周辺の固化土層上に積み
上げる。堀起す固化土の割合は、全固化土の5〜40容
積%、好ましくは10〜30容積%であり、その堀起し
個所は1つ又は複数の個所であることができ、その堀起
した跡の凹部の形状は、特に制約はないが溝状であるこ
とが好ましい。この堀起した跡の凹部には、固化土に含
まれている余剰水が滲出(ブリージング)し、その凹部
にこの余剰水が滞留する。この余剰水はこれを吸引ポン
プにより除去し、前記余水ピットに移送し、そこに貯留
する。
The sediment layer composed of a mixture of the soil particles and the solidifying agent in the reservoir becomes solidified by the reaction between the soil particles and the solidifying agent, increases its strength, and becomes solidified soil. In the present invention,
When the water content of the sediment reaches about 300 to 400% (after separating the excess water from the mixture of the bottom sediment and the solidifying agent,
On the fourth day), a part of the sediment (solidified soil) is excavated, and the excavated solidified soil is piled up on the surrounding solidified soil layer. The ratio of the solidified soil to be excavated is 5 to 40% by volume, preferably 10 to 30% by volume of the total solidified soil, and the excavated location can be one or more locations, and the excavated location can be one or more. The shape of the concave portion of the mark is not particularly limited, but is preferably a groove. Excess water contained in the solidified soil oozes (bleeds) into the concave portion of the excavated trace, and the excess water stays in the concave portion. This surplus water is removed by a suction pump, transferred to the surplus water pit, and stored there.

【0010】前記のようにして、固化土に凹部を形成し
た後、2〜6日目には、固化土の含水比は200〜30
0%程度に低下し、トラック輸送可能なものであること
が知見された。含水比が前記範囲より大きい固化土の場
合、これをトラック輸送しようとすると、その輸送に際
しての振動等の外力により、土粒子と固化剤との反応物
中に固定化されていた水の一部が遊離して固化土を泥粘
液化させる。このような泥粘液化された固化土はもはや
トラックの荷台には積載不可能のものであり、荷台から
流出してしまう。
[0010] After the recesses are formed in the solidified soil as described above, on the second to sixth days, the water content of the solidified soil is 200 to 30 days.
It was reduced to about 0%, and it was found that the product could be transported by truck. In the case of solidified soil having a water content ratio larger than the above range, when attempting to transport it by truck, due to external force such as vibration during the transportation, a part of the water fixed in the reaction product between the soil particles and the solidifying agent Is released and the solidified soil is made muddy and mucous. Such solidified mudified mud can no longer be loaded on the truck bed and flows out of the bed.

【0011】図1に固化土の一部を堀起し、周辺の固化
土の上に積み上げて固化土を静置した後の貯留池の断面
状態図の一例を示す。図1において、1及び2はそれぞ
れ貯留池の周壁及び底部を形成するコンクリート板を示
す。3は固化土を示し、4は固化土の一部堀起しによっ
てその堀起し跡に形成された溝状凹部を示す。5は固化
土の一部堀起しによって得られた固化土を周辺の固化土
3上に積み上げた固化土を示す。6はその溝状凹部に貯
留する固化土からの滲出水を示す。図1に示した貯留池
の高さは約2.8mであり、縦の長さは約20mであ
り、横の長さは約5mである。固化土3の高さは約2m
であり、溝状凹部5の幅は約1.5mである。前記のよ
うにして固化土の一部堀起しを行うことにより、トラッ
ク輸送可能な固化土を短期間で得ることができる。例え
ば、水底汚泥と固化剤との混合物を貯留池に投入静置
後、トラック輸送可能な固化土を得るまでの期間は、冬
の場合、堀起しを行わないときに14日間程度を要する
ようなものは、堀起しを行うことにより11〜12日程
度に短縮することができる。また、夏の場合には、堀起
しを行わないときには7日間を要したものが、堀起しを
行うことにより、4〜5日間に短縮することができる。
前記のようにして得られる含水比が200〜300%程
度の固化土は、埋立土として利用し得る他、植栽土や土
壌改良土等として利用することができる。
FIG. 1 shows an example of a sectional state diagram of a reservoir after excavating a part of the solidified soil, stacking it on the surrounding solidified soil and allowing the solidified soil to stand still. In FIG. 1, reference numerals 1 and 2 denote concrete plates forming the peripheral wall and the bottom of the reservoir, respectively. Reference numeral 3 denotes a solidified soil, and reference numeral 4 denotes a groove-shaped concave portion formed in the excavation trace by partially excavating the solidified soil. Reference numeral 5 denotes a solidified soil obtained by stacking solidified soil obtained by partially raising the solidified soil on the solidified soil 3 around the solidified soil. Numeral 6 indicates seepage water from the solidified soil stored in the groove-shaped concave portion. The height of the reservoir shown in FIG. 1 is about 2.8 m, the vertical length is about 20 m, and the horizontal length is about 5 m. The height of the solidified soil 3 is about 2m
And the width of the groove-shaped recess 5 is about 1.5 m. By partially digging the solidified soil as described above, the solidified soil that can be transported by truck can be obtained in a short period of time. For example, after the mixture of the submerged sludge and the solidifying agent is put into the storage tank and allowed to stand, the time required to obtain solidified soil that can be transported by truck is about 14 days in winter, when excavation is not performed. Can be reduced to about 11 to 12 days by excavation. Also, in the case of summer, what would take seven days when the excavation is not performed can be reduced to 4 to 5 days by performing the excavation.
The solidified soil having a water content of about 200 to 300% obtained as described above can be used not only as a landfill soil but also as a planting soil or a soil improvement soil.

【0012】[0012]

【発明の効果】本発明によれば、水底汚泥を作業効率よ
くかつ短期間でトラック輸送可能な土壌(固化土)に転
換させることができる。しかも、本発明で得られる土壌
は、埋立土や、植栽土、土壌改良土等として有効利用で
きる。
According to the present invention, submerged sludge can be converted into soil (solidified soil) which can be transported by truck in a short period of time with good work efficiency. Moreover, the soil obtained by the present invention can be effectively used as landfill soil, planting soil, soil improvement soil, and the like.

【0013】[0013]

【実施例】次に、本発明を実施例によりさらに詳細に説
明する。
Next, the present invention will be described in more detail with reference to examples.

【0014】実施例1 城の堀池の水底に堆積した汚泥を船体上に設置した真空
吸引装置により水底から吸い上げ、これを加圧ポンプに
より配管を通して陸上に設置した攪拌混合槽に導入し、
ここでスラリー状の土粒子固化剤と混合した。この場
合、攪拌混合槽に導入する水底汚泥の含水比は、約90
0%であった。固化剤としては、高炉水滓:38重量%
と、ポルトランドセメント:42重量%と、石コウ:2
0重量%からなる混合物を水中に分散させ、濃度を59
重量%としたスラリーを用いた。このスラリー状の固化
剤は、固形分換算で、水底汚泥に含まれる土粒子100
重量部に対し、100重量部の割合で添加混合した。
Example 1 Sludge deposited on the bottom of a castle moat pond is sucked up from the bottom by a vacuum suction device installed on a hull, and introduced into a stirring and mixing tank installed on land through a pipe by a pressure pump.
Here, it was mixed with a slurry-like soil particle solidifying agent. In this case, the water content of the bottom sludge introduced into the stirring and mixing tank is about 90%.
It was 0%. Blast furnace slag: 38% by weight as a solidifying agent
And Portland cement: 42% by weight and stone stone: 2
A mixture consisting of 0% by weight is dispersed in water and the concentration is 59%.
A slurry in which the weight% was used was used. This slurry-like solidifying agent is equivalent to the solid particles 100 in the soil sediment contained in the bottom sediment.
100 parts by weight with respect to parts by weight were added and mixed.

【0015】次に、前記のようにして得られた水底汚泥
と固化剤との混合物を、図1に示した構造の縦:20
m、横:5m、高さ:2.8mのコンクリートピットに
高さ2.6mまで投入し、2日間静置した。この静置に
より水底汚泥中の土粒子と固化剤との混合物が沈降し、
高さ2.2mの沈降物を得た。その沈降物(含水比:3
64%)層の上部には余剰水層が形成された。この余剰
水層を除去した後、さらに4日間静置した。この静置に
より沈降物層中の土粒子と固化剤との反応が進み、強度
増加した固化土(含水化:330%)が形成された。こ
の時点において、バックホウを用いて固化土の一部を堀
起し、図1に示すようにその周辺の固化土の上に積み上
げた。この作業後、固化土に含まれる余剰水の凹部への
滲出が起り、固化土の堀起し後、5日目にその凹部に滞
留する滲出水を吸引ポンプで除去した。この時点におけ
る固化土の含水比は約248%であり、トラック輸送の
可能のものであることが確認された。なお、前記水底汚
泥の固化処理において、固化土の堀起し作業を行わない
場合には、トラック輸送可能な固化土(含水比:296
%)を得るには、貯留池への水底汚泥と固化剤との混合
物を投入静置後、4日間を要した。
Next, the mixture of the submerged sludge obtained as described above and the solidifying agent was mixed with the mixture shown in FIG.
m, the width: 5 m, and the height: 2.8 m. The concrete pit was charged up to a height of 2.6 m, and allowed to stand for 2 days. By this standing, the mixture of the soil particles in the bottom sediment and the solidifying agent settles,
A sediment with a height of 2.2 m was obtained. The sediment (water content: 3
An excess water layer was formed on the upper part of the (64%) layer. After removing this surplus aqueous layer, it was left still for 4 days. By this standing, the reaction between the soil particles in the sediment layer and the solidifying agent proceeded, and solidified soil with increased strength (water content: 330%) was formed. At this point, a part of the solidified soil was excavated using a backhoe, and was piled up on the solidified soil around the part as shown in FIG. After this operation, excess water contained in the solidified soil oozed into the concave portion. After excavation of the solidified soil, the exuded water remaining in the concave portion was removed on the fifth day by a suction pump. At this point, the water content of the solidified soil was about 248%, and it was confirmed that the soil could be transported by truck. In the solidification treatment of submerged sludge, when excavation work of solidified soil is not performed, solidified soil capable of being transported by truck (water content: 296)
%), It took 4 days after the mixture of the submerged sludge and the solidifying agent was put into the reservoir and allowed to stand.

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

【図1】図1は固化土の一部を堀起し、周辺の固化土の
上に積み上げて固化土を静置した後の貯留池の断面状態
図を示す。
BRIEF DESCRIPTION OF DRAWINGS FIG. 1 is a cross-sectional view of a reservoir after excavating a part of the solidified soil, stacking the solidified soil on a surrounding solidified soil, and allowing the solidified soil to stand still.

【符号の説明】[Explanation of symbols]

1 コンクリート周壁 2 コンクリート底板 3 固化土 4 固化土を堀起した跡の凹部 5 積み上げた固化土 6 凹部に滞留する滲出水 DESCRIPTION OF SYMBOLS 1 Concrete surrounding wall 2 Concrete bottom plate 3 Solidified soil 4 Concavity of the mark which excavated solidified soil 5 Solidified soil piled up 6

───────────────────────────────────────────────────── フロントページの続き (72)発明者 間篠 善一 神奈川県横浜市鶴見区鶴見中央二丁目12 番1号 千代田化工建設株式会社内 (72)発明者 渡辺 好則 神奈川県横浜市鶴見区鶴見中央二丁目12 番1号 千代田化工建設株式会社内 (56)参考文献 特開 昭50−153454(JP,A) 特公 昭60−12120(JP,B2) 特公 昭52−49912(JP,B2) ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Zenichi Mashino 2-1-1, Tsurumichuo, Tsurumi-ku, Yokohama-shi, Kanagawa Prefecture Inside Chiyoda Chemical Works (72) Inventor Yoshinori Watanabe Tsurumi-ku, Yokohama-shi, Kanagawa Tsurumi Chuo 2-chome No. 12 Chiyoda Kako Construction Co., Ltd. (56) References JP 50-153454 (JP, A) JP-B 60-12120 (JP, B2) JP-B 52-49912 (JP, B2)

Claims (3)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 水底汚泥の固化処理方法において、
(i)真空吸引方式により水底汚泥を浚渫し、その移送
過程で連続的に土粒子固化剤を混合する工程、(ii)得
られた混合物を貯留池に投入する工程、(iii)貯留池に
投入した混合物を静置して水底汚泥に含まれる土粒子と
土粒子固化剤からなる沈降物層を形成させる工程、(i
v)沈降物層の上部に形成された余剰水を除去する工
程、(v)沈降物層を含水比300〜400%の固化土
が得られるまで静置する工程、(vi)固化土の一部を堀
起し、周辺の固化土の上に積み上げる工程、(vii)固化
土を堀起した跡の凹部に固化土に含まれる余剰水を滲出
させ、含水比200〜300%の固化土を生成させる工
程、(viii)凹部に滞留する滲出水を除去する工程を含む
ことを特徴とする水底汚泥の固化処理方法。
1. A method for solidifying submerged sludge, comprising:
(I) a step of dredging submerged sludge by a vacuum suction method and continuously mixing the soil particle solidifying agent in the transfer process, (ii) a step of charging the obtained mixture into a reservoir, and (iii) a step of charging the reservoir. A step of allowing the input mixture to stand to form a sediment layer comprising soil particles contained in the submarine sludge and a soil particle solidifying agent, (i.
v) a step of removing excess water formed on the upper part of the sediment layer, (v) a step of allowing the sediment layer to stand until a solidified soil having a water content of 300 to 400% is obtained, (vi) one of the solidified soils (Vii) exuding surplus water contained in the solidified soil into the concave portion of the trace where the solidified soil has been digged, and solidifying the solidified material having a water content of 200 to 300%. A method of solidifying submerged sludge, comprising: a step of generating; and (viii) a step of removing exuded water remaining in the concave portions.
【請求項2】 土粒子固化剤を水中に濃度25〜63重
量%で分散させたスラリー液として水底汚泥に混合する
請求項1の方法。
2. The method according to claim 1, wherein the soil particle solidifying agent is mixed with the submerged sludge as a slurry liquid having a concentration of 25 to 63% by weight dispersed in water.
【請求項3】 土粒子固化剤としてセメント系固化剤を
用いる請求項1又は2の方法。
3. The method according to claim 1, wherein a cement-based solidifying agent is used as the soil particle solidifying agent.
JP20209093A 1993-07-23 1993-07-23 Solidification method of submerged sludge Expired - Lifetime JP2640616B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP20209093A JP2640616B2 (en) 1993-07-23 1993-07-23 Solidification method of submerged sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP20209093A JP2640616B2 (en) 1993-07-23 1993-07-23 Solidification method of submerged sludge

Publications (2)

Publication Number Publication Date
JPH0731997A JPH0731997A (en) 1995-02-03
JP2640616B2 true JP2640616B2 (en) 1997-08-13

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Country Link
JP (1) JP2640616B2 (en)

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KR101666074B1 (en) * 2016-01-15 2016-10-14 한국경량혼합토 주식회사 System that allow for high-speed site renovation using high water content dredged sediment and dredging work at the same time and method for hihg-speed site renovation

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