JPS6354092B2 - - Google Patents
Info
- Publication number
- JPS6354092B2 JPS6354092B2 JP9406283A JP9406283A JPS6354092B2 JP S6354092 B2 JPS6354092 B2 JP S6354092B2 JP 9406283 A JP9406283 A JP 9406283A JP 9406283 A JP9406283 A JP 9406283A JP S6354092 B2 JPS6354092 B2 JP S6354092B2
- Authority
- JP
- Japan
- Prior art keywords
- landfill
- water
- filter
- mud
- coarse
- 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
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 33
- 238000001179 sorption measurement Methods 0.000 claims description 15
- 238000000034 method Methods 0.000 claims description 13
- 235000008331 Pinus X rigitaeda Nutrition 0.000 claims description 12
- 235000011613 Pinus brutia Nutrition 0.000 claims description 12
- 241000018646 Pinus brutia Species 0.000 claims description 12
- 230000008961 swelling Effects 0.000 claims description 7
- 239000002245 particle Substances 0.000 claims description 6
- 230000008569 process Effects 0.000 claims description 5
- 239000002689 soil Substances 0.000 claims description 5
- 230000003204 osmotic effect Effects 0.000 claims description 4
- 238000007596 consolidation process Methods 0.000 description 10
- 239000007787 solid Substances 0.000 description 9
- 239000000463 material Substances 0.000 description 8
- 238000010276 construction Methods 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- 238000002203 pretreatment Methods 0.000 description 4
- 239000004927 clay Substances 0.000 description 3
- 230000008859 change Effects 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000010419 fine particle Substances 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 238000002347 injection Methods 0.000 description 2
- 239000007924 injection Substances 0.000 description 2
- 239000012466 permeate Substances 0.000 description 2
- 239000010802 sludge Substances 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- 230000009471 action Effects 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 230000000996 additive effect Effects 0.000 description 1
- 238000005054 agglomeration Methods 0.000 description 1
- 230000002776 aggregation Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000008394 flocculating agent Substances 0.000 description 1
- 230000008595 infiltration Effects 0.000 description 1
- 238000001764 infiltration Methods 0.000 description 1
- 230000035699 permeability Effects 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 238000010408 sweeping Methods 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
Classifications
-
- E—FIXED CONSTRUCTIONS
- E02—HYDRAULIC ENGINEERING; FOUNDATIONS; SOIL SHIFTING
- E02D—FOUNDATIONS; EXCAVATIONS; EMBANKMENTS; UNDERGROUND OR UNDERWATER STRUCTURES
- E02D17/00—Excavations; Bordering of excavations; Making embankments
- E02D17/18—Making embankments, e.g. dikes, dams
Landscapes
- Engineering & Computer Science (AREA)
- Mining & Mineral Resources (AREA)
- Life Sciences & Earth Sciences (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Paleontology (AREA)
- Civil Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Structural Engineering (AREA)
Description
本発明は、シルト・粘土成分の多い浚渫泥をポ
ンプ船によつて埋立る場合に、埋立直後の泥の体
積が浚渫前の体積よりも膨潤する現象を防止する
浚渫埋立泥の膨潤防止方法に関するものである。
シルト・粘土分の多い浚渫泥の埋立において、
従来工法による急速施工の場合、埋立終了直後の
泥の体積が浚渫前の体積の2倍を超えた実例は多
く、このため計画浚渫土量の半分も埋立地に収容
できなかつたケースや、埋立地護岸の嵩上げ、護
岸背後の再築堤を行つて収容した例も少なくな
い。また、埋立工期が3〜10年という緩速施工の
場合にあつても、ほゞ1.6倍以下の体積変化率を
示している。このようにシルト・粘土分の多い浚
渫泥によつて造成された埋立地盤は、埋立終了後
に地盤改良工事を実施しており、本発明は埋立工
事過程において、上記泥の体積変化を抑制し、埋
立地護岸の嵩上げや再築堤の不要な施工ができる
ようにするとともに埋立工事終了後に行う地盤改
良工事についても初期の工程省略ができる膨潤防
止方法である。
以下図面について発明の内容を説明する。
第1図は、本発明の浚渫埋立泥の膨潤防止方法
を説明する埋立地の平面形状を示し、埋立護岸1
により囲まれた埋立地へポンプ船からの浚渫泥水
を流入させるに当り、排泥管2の任意の位置にお
いて薬注装置3により凝集剤を注入する。凝集剤
は、泥水中の微粒土分が凝集結合し、埋立地内に
沈澱堆積する堆積泥の透水性を増大させるための
ものである。埋立地内には、埋立工事開始前に排
水ポケツト4を設け、排水ポケツトに向つて透水
マツト管5、粗粒濾過体6を敷設する。透水マツ
ト管と粗粒濾過体は、堆積泥からの浸透水を排水
ポケツト内に導くものである。排水ポケツトは、
浸透余水量の残余水量を迂回させる導流築堤7と
通過させる吸着濾過体8により囲み、排水ポケツ
トに流入する浸透水、残余水を排水ポンプ9によ
り汲み上げ排水する。余水吐10は、排水ポンプ
を使用しなくなる埋立工事の終期以後における余
水排水を行う。
第2図は、本発明の方法による埋立地の任意断
面を示したもので、埋立地の元の地盤11上に排
泥管2から流入した沈澱堆積泥12があり、余水
は、埋立地の元の地盤上に配置した透水マツト管
5に向つて浸透する。透水マツト管の一方の端部
は粗粒濾過体に連接し、浸透水は排水ポケツト4
に集まるようになつている。粗粒濾過体6は、粗
粒濾材を網袋等に入れて積上げ構成する。
第3図は、本発明の透水マツト管の敷設状況を
示す断面図であり、作業台船13上に透水マツト
材14を積載し、順次敷設していく過程で粗粒濾
材15を運搬機16により封入架台17に送り透
水マツト上に落下させ、接合機18により透水マ
ツト内に粗粒濾材を封じ込め閉じる。
第4図は、上記透水マツトに粗粒濾材を封入し
て成る透水マツト管の断面図である。透水マツト
は浸透水を通過させるに適した空隙のある透水シ
ート類でもよい。浸透水は凝集剤が注入されてい
るので徴細粒子が凝集して出来た造粒堆積泥の間
隙を通過し、堆積泥による吸着作用もあつて、浮
遊物質量の少ない清澄水であり、埋立過程中に透
水マツトが目詰りすることはない。
第5図は、本発明において埋立泥が自重圧密と
浸透水圧力による圧密作用を受けることを説明す
る模式図であり、Aは従来の埋立地内における堆
積泥12が、水中重量で表わされる圧力を受ける
状態を、Bは、水中重量で表わした自重による圧
力の他に、埋立地内と排水ポケツト内の水位差H
により、堆積泥内に発生する浸透水圧力16を受
け、その圧力により圧密速度を増す状態を示すも
ので、この圧密速度と関係する埋立泥の透水係数
k(Kg/min)は、圧密荷重P(Kg/cm2)に対し第
1表に示す試験例がある。
The present invention relates to a method for preventing the swelling of dredged and reclaimed mud, which prevents the volume of the mud immediately after the reclaiming from swelling more than the volume before dredging, when the dredged mud containing a large amount of silt and clay is reclaimed by a pump ship. It is something. When reclaiming dredged mud with a high content of silt and clay,
In the case of rapid construction using conventional construction methods, there are many cases in which the volume of mud immediately after the completion of reclamation is more than twice the volume before dredging, and as a result, there are cases in which even half of the planned dredged volume could not be accommodated in the landfill, and There are many cases in which the land has been contained by raising the level of the seawall or rebuilding the embankment behind the seawall. Furthermore, even in the case of slow construction with a reclamation period of 3 to 10 years, the volume change rate is approximately 1.6 times or less. In this way, the reclaimed ground created using dredged mud with a high content of silt and clay undergoes ground improvement work after the completion of the reclamation, and the present invention suppresses the volume change of the mud during the reclamation work process, This is a swelling prevention method that eliminates the need for raising the level of the reclaimed land embankment or rebuilding the embankment, as well as omitting the initial stages of ground improvement work to be carried out after the completion of the reclamation work. The content of the invention will be explained below with reference to the drawings. FIG. 1 shows the planar shape of a reclaimed land for explaining the method of preventing swelling of dredged reclaimed mud of the present invention, and shows the reclaimed seawall 1.
When dredged mud water from a pump ship flows into a landfill surrounded by a tank, a flocculant is injected by a chemical injection device 3 at an arbitrary position of the mud drain pipe 2. The flocculant is used to coagulate fine soil particles in mud and increase the water permeability of sediment deposited in a landfill. A drainage pocket 4 is provided in the landfill before the start of the landfill work, and a permeable mat pipe 5 and a coarse filter 6 are laid toward the drainage pocket. The water-permeable pine pipe and the coarse-grained filter conduct the seepage water from the accumulated mud into the drainage pocket. The drainage pocket is
It is surrounded by a diversion embankment 7 that detours the residual amount of permeated water and an adsorption filter 8 that allows it to pass through, and the permeated water and residual water flowing into the drainage pocket are pumped up by a drainage pump 9 and drained. The spillway 10 drains excess water after the end of the landfill work when the drainage pump is no longer used. FIG. 2 shows an arbitrary cross-section of a reclaimed land according to the method of the present invention, where there is sedimentary mud 12 flowing from the mud drain pipe 2 on the original ground 11 of the reclaimed land, and the surplus water flows into the reclaimed land. The water permeates into the permeable pine pipe 5 placed on the original ground. One end of the permeable mat pipe is connected to the coarse filter, and the permeated water is drained into the drainage pocket 4.
They are starting to gather together. The coarse filter medium 6 is constructed by stacking coarse filter media in a mesh bag or the like. FIG. 3 is a sectional view showing how the water-permeable pine pipe of the present invention is laid. In the process of loading the water-permeable pine material 14 on the work barge 13 and sequentially laying it, the coarse filter material 15 is transferred to the transporter 16. The coarse filter material is sent to the enclosure frame 17 and dropped onto a water-permeable mat, and the coarse filter material is sealed and closed within the water-permeable mat by the bonding machine 18. FIG. 4 is a sectional view of a water-permeable mat tube formed by enclosing a coarse filter medium in the water-permeable mat. The water-permeable mat may be a water-permeable sheet with voids suitable for allowing permeate water to pass through. The seepage water has a flocculant injected into it, so it passes through the gaps in the granulated mud created by the agglomeration of fine particles, and due to the adsorption effect of the mud, it is clear water with a small amount of suspended solids, and it is not disposed of in a landfill. The permeable pine will not become clogged during the process. FIG. 5 is a schematic diagram illustrating that in the present invention, the reclaimed mud is subjected to the consolidation action by its own weight consolidation and seepage water pressure. In addition to the pressure due to its own weight expressed as underwater weight, B is the water level difference H between the landfill and the drainage pocket.
This indicates a state in which the consolidation rate is increased by the infiltration water pressure 16 generated in the accumulated mud, and the hydraulic conductivity k (Kg/min) of the reclaimed mud, which is related to the consolidation rate, is the consolidation load P. (Kg/cm 2 ), there are test examples shown in Table 1.
【表】
第1表より、凝集剤を添加した堆積泥は、圧密
荷重Pの小さい範囲において、無添加の場合より
も透水係数が大きい。このことは、埋立過程の凝
集剤を添加した軟弱な状態の堆積泥は、ある圧密
レベルまで浸透水圧を利用して急速圧密させるこ
とが可能であることを意味し、施工計画に際して
は、凝集剤の種類、薬品の添加率および堆積泥の
浸透圧密特性等を充分把握しておく必要がある。
第6図は、堆積泥と分離して生成する余水のう
ち、浸透水とならなかつた残余水の浮遊物質量を
低減させて、排水ポケツトに導くための吸着濾過
体の断面図である。基礎盛土19の上部に透水マ
ツトまたは透水シートを通水面とする前処理濾過
板20を配し、その下流側に保持杭22を棚板2
3にて保持し、両者の間に網袋入り粗粒濾材を積
上げた吸着濾過体21を設けて構成する2段濾過
装置である。この吸着濾過体に流入する余水は、
排泥管において凝集剤を添加しているために浮遊
物質としては主に凝集粒子で若干の徴細粒子を含
有する程度である。従つて、浮遊物質は、ほゞ前
処理濾過板の透水マツト表面に付着し、吸着濾過
体本体には低濃度余水が流入する。吸着濾過体内
で更に浮遊物質量が吸着低減され、排水の浮遊物
質量(SS)=20〜50ppmとなり、一般の排水基準値
を満足させることができる。埋立工事の終期にお
いて、吸着濾過体へ流入する余水の浮遊物質量が
過大になつたときには、吸着濾過体の上流側に水
流抑制装置を設置して、物理的対策により浮遊物
質量を低減させる。なお、前処理濾過板の透水マ
ツト表面に付着した浮遊物質は、適時下方へ掃き
落し除去する。[Table] From Table 1, the mud piled with flocculant added has a higher hydraulic conductivity than the case without additive in the range of small consolidation load P. This means that it is possible to rapidly consolidate soft mud piled with flocculants added during the landfill process to a certain consolidation level using seepage water pressure. It is necessary to fully understand the types of chemicals, the addition rate of chemicals, and the osmotic consolidation characteristics of the deposited mud. FIG. 6 is a cross-sectional view of an adsorption filter for reducing the amount of suspended solids in the residual water that does not become percolated water, out of the residual water generated by separation from the accumulated mud, and guiding it to the drainage pocket. A pre-treatment filter plate 20 with a permeable pine or a permeable sheet as a water-permeable surface is arranged on the upper part of the foundation embankment 19, and a retaining pile 22 is installed on the downstream side of the pre-treatment filter plate 20.
This is a two-stage filtration device configured by holding an adsorption filter body 21 held at 3 and having an adsorption filter body 21 stacked with coarse filter media in a mesh bag between the two. The surplus water flowing into this adsorption filter is
Since a flocculant is added to the sludge pipe, the suspended solids are mainly flocculated particles and contain only a few fine particles. Therefore, the suspended solids adhere to the water-permeable mat surface of the pre-treatment filter plate, and the low concentration surplus water flows into the adsorption filter body. The amount of suspended solids is further adsorbed and reduced in the adsorption filter, and the amount of suspended solids (SS) in wastewater becomes 20 to 50 ppm, which satisfies general wastewater standards. When the amount of suspended solids in the surplus water flowing into the adsorption filter becomes excessive at the end of the landfill work, a water flow control device will be installed upstream of the adsorption filter to reduce the amount of suspended solids through physical measures. . In addition, floating substances adhering to the surface of the water-permeable mat of the pre-treatment filter plate are removed by sweeping them downwards in a timely manner.
第1図は、本発明の浚渫埋立泥の膨潤防止方法
を説明する埋立地の平面形状を示し、図中1は埋
立護岸、2は排泥管、3は薬品注入装置、4は排
水ポケツト、5は透水マツト管、6は粗粒濾過
体、7は導流築堤、8は吸着濾過体、9は排水ポ
ンプ、10は余水吐である。
第2図は、本発明の方法による埋立地の施工断
面を示し、図中1は埋立護岸、2は排泥管、4は
排水ポケツト、5は透水マツト管、6は粗粒濾過
体、7は導流築堤、9は排水ポンプ、10は余水
吐、11は埋立地在来地盤、12は沈澱堆積泥で
ある。
第3図は、本発明の透水マツト管の敷設状況を
示す断面図で、図中5は透水マツト管、6は粗粒
濾過体、11は埋立地在来地盤、13は作業台
船、14は透水マツト材、15は粗粒濾材、16
は運搬機、17は封入台、18は接合機である。
第4図は、透水マツト管の断面図を示し、図中
14は透水マツト材、15は粗粒濾材を示す。
第5図は、埋立泥が自重圧密と浸透水圧による
圧密をうけることを示す模式図で、図中12は沈
澱堆積泥、16は浸透水圧力の方向である。
第6図は、残余水を処理する吸着濾過体の断面
図で、図中19は基礎盛土、20は前処理濾過
板、21は吸着濾過体、22は保持杭、23は柵
板である。
FIG. 1 shows the planar shape of a landfill site for explaining the method for preventing swelling of dredged and landfill mud of the present invention, in which 1 is a landfill revetment, 2 is a mud drain pipe, 3 is a chemical injection device, 4 is a drainage pocket, 5 is a water permeable pine pipe, 6 is a coarse filter, 7 is a diversion embankment, 8 is an adsorption filter, 9 is a drainage pump, and 10 is a spillway. Fig. 2 shows a construction cross section of a reclaimed land according to the method of the present invention, in which 1 is a landfill revetment, 2 is a sludge pipe, 4 is a drainage pocket, 5 is a permeable pine pipe, 6 is a coarse filter, and 7 is a construction site. 9 is a diversion embankment, 9 is a drainage pump, 10 is a spillway, 11 is a reclaimed land, and 12 is sedimentary mud. FIG. 3 is a cross-sectional view showing how the water-permeable pine pipe of the present invention is laid. 15 is a coarse filter material, 16 is a water-permeable pine material,
1 is a transporter, 17 is an enclosure table, and 18 is a joining machine. FIG. 4 shows a cross-sectional view of the water-permeable mat tube, in which 14 indicates a water-permeable mat material, and 15 indicates a coarse filter material. FIG. 5 is a schematic diagram showing that the reclaimed mud is subjected to its own weight consolidation and consolidation due to osmotic water pressure. In the figure, 12 is the direction of the settled mud and 16 is the direction of the osmotic water pressure. FIG. 6 is a sectional view of an adsorption filter for treating residual water, in which 19 is a foundation embankment, 20 is a pretreatment filter plate, 21 is an adsorption filter, 22 is a holding stake, and 23 is a fence board.
Claims (1)
粗粒濾過体で構成された導流築堤により一部仕切
つて迂回路を形成すると共にこの区画内を吸着濾
過体により更に仕切つて排水ポケツト区画を形成
し、粗粒濾材を封入した透水マツト管の一端を前
記導流築堤下部の粗粒濾過体に連接させて埋立地
内の元の地盤上に配置して成る埋立地内へ、浚渫
泥の排送過程において凝集剤を添加した泥水を投
入することにより、埋立地内余水の堆積土粒子間
の通過を容易にし、透水マツト管と粗粒濾過体を
経て排水ポケツトに導くようにし、排水ポケツト
内に設けた排水ポンプを駆動して排水ポケツト内
の水位を低く保ち、埋立地内水位と排水ポケツト
内の水位差による堆積土粒子に作用する浸透圧力
と堆積土粒子の自重とにより、堆積土粒子層を急
速沈下させることを特徴とする浚渫埋立泥の膨潤
防止方法。 2 吸着濾過体が、前処理濾過板と棚板に保持さ
れた保持杭の間に網袋入り粗粒濾材を積上げたも
のである特許請求の範囲第1項記載の浚渫埋立泥
の膨潤防止方法。[Scope of Claims] 1. A section in a landfill having a spillway is partially partitioned by a diversion embankment whose lower part is composed of a coarse-grained filter to form a detour, and an adsorption filter is used in this section. The landfill is further partitioned to form a drainage pocket section, and one end of a permeable pine pipe containing a coarse filter medium is connected to the coarse filter body at the lower part of the diversion embankment, and is placed on the original ground within the landfill. By injecting muddy water with a flocculant added into the ground during the discharge process of dredged mud, surplus water from the landfill can easily pass between the deposited soil particles, and flow through the permeable pine pipes and coarse-grained filter into the drainage pocket. The water level inside the drainage pocket is kept low by driving the drainage pump installed inside the drainage pocket, and the osmotic pressure acting on the accumulated soil particles due to the difference between the water level in the landfill and the water level in the drainage pocket and the dead weight of the accumulated soil particles are reduced. A method for preventing swelling of dredged and reclaimed mud, which is characterized by rapidly sinking a layer of accumulated soil particles. 2. The method for preventing the swelling of dredged and reclaimed mud as set forth in claim 1, wherein the adsorption filter is one in which coarse-grained filter media in mesh bags are piled up between a pretreatment filter plate and a holding pile held on a shelf board. .
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9406283A JPS59220511A (en) | 1983-05-30 | 1983-05-30 | Prevention of swelling of dredged and reclaimed sludge |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9406283A JPS59220511A (en) | 1983-05-30 | 1983-05-30 | Prevention of swelling of dredged and reclaimed sludge |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS59220511A JPS59220511A (en) | 1984-12-12 |
| JPS6354092B2 true JPS6354092B2 (en) | 1988-10-26 |
Family
ID=14100035
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP9406283A Granted JPS59220511A (en) | 1983-05-30 | 1983-05-30 | Prevention of swelling of dredged and reclaimed sludge |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS59220511A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS61290107A (en) * | 1985-06-17 | 1986-12-20 | Penta Ocean Constr Co Ltd | Sludge reclamation work |
| CN103397646B (en) * | 2013-08-19 | 2015-01-21 | 安徽省水利水电勘测设计院 | Technique for fast filling constructed wetland in shore area |
-
1983
- 1983-05-30 JP JP9406283A patent/JPS59220511A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS59220511A (en) | 1984-12-12 |
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