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JP2913632B2 - Dredging mud treatment method and treatment equipment - Google Patents
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JP2913632B2 - Dredging mud treatment method and treatment equipment - Google Patents

Dredging mud treatment method and treatment equipment

Info

Publication number
JP2913632B2
JP2913632B2 JP25018295A JP25018295A JP2913632B2 JP 2913632 B2 JP2913632 B2 JP 2913632B2 JP 25018295 A JP25018295 A JP 25018295A JP 25018295 A JP25018295 A JP 25018295A JP 2913632 B2 JP2913632 B2 JP 2913632B2
Authority
JP
Japan
Prior art keywords
mud
water
dredging
dredged
tank
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
JP25018295A
Other languages
Japanese (ja)
Other versions
JPH0971966A (en
Inventor
道彦 石田
光輝 炭田
正夫 黒岩
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.)
OOBAYASHIGUMI KK
Original Assignee
OOBAYASHIGUMI KK
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 OOBAYASHIGUMI KK filed Critical OOBAYASHIGUMI KK
Priority to JP25018295A priority Critical patent/JP2913632B2/en
Publication of JPH0971966A publication Critical patent/JPH0971966A/en
Application granted granted Critical
Publication of JP2913632B2 publication Critical patent/JP2913632B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Landscapes

  • Treatment Of Sludge (AREA)

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、海や湖沼あるいは
河川の水質改善を目的とした浚渫泥土の処理方法および
処理設備に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and a facility for treating dredged mud for improving the water quality of the sea, lakes, or rivers.

【0002】[0002]

【従来の技術】海や湖沼あるいは河川は、生活やレジャ
ーを含めた多目的利用のための空間として注目されてい
るが、その一方で、閉鎖性水域においては有機物による
富栄養化、貧酸素化が進み、かかる水質汚染に対する対
策が急務となっている。
2. Description of the Related Art The sea, lakes, or rivers are attracting attention as spaces for multipurpose use including living and leisure activities. On the other hand, in closed waters, eutrophication and hypoxia due to organic matter are caused. There is an urgent need to take measures against such water pollution.

【0003】有機物による水質汚染は、陸域からの過剰
な流入負荷が大きな原因となっており、産業排水の削
減、有機洗剤使用の自粛等によって徐々に改善されつつ
あるが、その一方で、過剰な有機物は分解されずに海底
に堆積し、底質と呼ばれるヘドロ層を形成し、かかるヘ
ドロ層からは、窒素、リンなどの栄養塩が水中に溶出し
て水質汚染を進行させる要因となる。
[0003] Water pollution by organic matter is largely caused by excessive inflow load from the terrestrial area, and is being gradually improved by reduction of industrial wastewater and voluntary use of organic detergents. Such organic matter is deposited on the seabed without being decomposed, and forms a sludge layer called sediment. From the sludge layer, nutrients such as nitrogen and phosphorus are eluted into water and become a factor of promoting water pollution.

【0004】したがって、有機物含有量が高い泥土を浚
渫によって除去するなどの対策を講ずることによって、
底質からの栄養塩の溶出を低減することが重要となる。
Accordingly, by taking measures such as removing mud having a high organic matter content by dredging,
It is important to reduce the elution of nutrients from sediment.

【0005】ここで、水底に堆積した泥土を浚渫する
際、大量の余剰水が泥土とともに吸い上げられ、含水比
はきわめて高くなる。そのため、かかる余剰水を天日乾
燥、ドレーン材による脱水処理、フィルタープレス等の
加圧脱水装置による機械脱水等によって泥土分から分離
除去する作業が必要となる。
[0005] Here, when the mud accumulated on the water bottom is dredged, a large amount of surplus water is sucked up together with the mud, and the water content becomes extremely high. Therefore, it is necessary to separate and remove such surplus water from mud by sun drying, dehydration treatment with a drain material, mechanical dehydration with a pressure dehydrator such as a filter press, or the like.

【0006】[0006]

【発明が解決しようとする課題】しかしながら、機械脱
水を行う場合であっても浚渫泥土に含まれる大量の余剰
水を分離するには広い沈殿池が必要となる。そして、近
年の土地事情を考えればかかる広大な用地の確保はきわ
めて困難であるとともに、周辺に飛散する悪臭がネック
となって施設を設置することが難しいという問題を生じ
ていた。
However, even when mechanical dewatering is performed, a wide sedimentation basin is required to separate a large amount of excess water contained in the dredged mud. In view of recent land conditions, it is extremely difficult to secure such a vast land, and at the same time, there has been a problem that it is difficult to install facilities due to a bad smell scattered around.

【0007】また、機械脱水の最終工程で生成される大
量の脱水ケーキを処分する場所が確保困難であるという
問題も生じていた。
Another problem is that it is difficult to secure a place for disposing of a large amount of dewatered cake generated in the final step of mechanical dewatering.

【0008】本発明は、上述した事情を考慮してなされ
たもので、浚渫泥土を脱水処理するための用地や脱水ケ
ーキを処分するための用地を確保する必要なしに浚渫泥
土を処理して水質汚染の進行を阻止することができる浚
渫泥土の処理方法および処理設備を提供することを目的
とする。
The present invention has been made in view of the above-mentioned circumstances, and has no need to secure a site for dewatering the dredged mud and a site for disposing of the dewatered cake, thereby treating the dredged mud. An object of the present invention is to provide a dredging mud treatment method and a treatment facility capable of preventing the progress of contamination.

【0009】[0009]

【課題を解決するための手段】上記目的を達成するた
め、本発明の浚渫泥土の処理方法は請求項1に記載した
ように、水底に堆積した泥土を浚渫し、次いで、浚渫さ
れた泥土に対して凝集剤を用いた凝集沈降処理および加
圧脱水処理を含む水分除去処理を行い、次いで、該水分
除去処理で生じたケーキを水底に沈めるものである。
In order to achieve the above object, a method for treating dredged mud according to the present invention comprises the steps of: dredging mud deposited on the water bottom; On the other hand, a water removal treatment including a coagulation sedimentation treatment using a flocculant and a pressure dehydration treatment is performed, and then the cake generated by the water removal treatment is submerged in the water bottom.

【0010】また、本発明の浚渫泥土の処理方法は、前
記水分除去処理を水上に浮かべた浮体構造物の上で処理
するものである。
Further, in the method for treating dredged mud according to the present invention, the water removal treatment is carried out on a floating structure floating on water.

【0011】また、本発明の浚渫泥土の処理設備は請求
項3に記載したように、水底に堆積した泥土を浚渫する
浚渫装置と、該浚渫装置から送られてきた浚渫泥土を貯
留する貯泥槽と、該貯泥槽から送られてきた泥土を所定
の凝集剤で凝集沈降させる凝集沈降槽と、凝集沈降させ
た泥土を加圧脱水する加圧脱水装置とを所定の浮体構造
物の上に設置したものである。
Further, the dredging mud treatment equipment of the present invention is a dredging device for dredging mud deposited on the water bottom and a mud storage for storing the dredged mud sent from the dredging device. A tank, a coagulation sedimentation tank for coagulating and sedimenting the mud sent from the mud storage tank with a predetermined coagulant, and a pressure dehydrator for pressurizing and dewatering the coagulated and sedimented mud on a predetermined floating structure. It was installed in.

【0012】本発明の浚渫泥土の処理方法および処理設
備においては、浚渫された泥土に対して凝集剤を用いた
凝集沈降および加圧脱水を含む水分除去処理を行う。そ
して、該処理で発生した脱水ケーキを水底、例えば元通
りの水底に沈めて最終処分とする。
In the method and equipment for treating dredged mud according to the present invention, the dredged mud is subjected to water removal treatment including coagulation sedimentation using a coagulant and dehydration under pressure. Then, the dehydrated cake generated in the treatment is submerged on the bottom of the water, for example, the original bottom, and is finally disposed.

【0013】水底に沈められた脱水ケーキは、凝集剤お
よび加圧脱水の効果によって水中での分散が抑止され、
再び泥状化することはない。そして、りんや窒素等の栄
養塩は脱水ケーキ内に閉じこめられ、水中には溶出しな
い。したがって、水質汚染を進行させるヘドロ層を上述
のごとく処理して脱水ケーキの状態で元通り水底に沈め
れば、脱水ケーキの処分場所を新たに確保する必要なし
に、該水域の富栄養化、貧酸素化といった水質汚染の進
行が阻止される。
The dewatered cake submerged in the water bottom is prevented from dispersing in water by the effect of the coagulant and dehydration under pressure.
It will not be muddy again. Nutrients such as phosphorus and nitrogen are trapped in the dehydrated cake and do not elute into water. Therefore, if the sludge layer that promotes water pollution is treated as described above and submerged in the state of a dewatered cake to the bottom of the water, eutrophication of the water area without the need to newly secure a disposal site for the dewatered cake, Water pollution such as hypoxia is prevented from progressing.

【0014】ここで、水分除去処理を水上に浮かべた浮
体構造物の上で処理する場合、陸地での用地確保の問題
も併せて解消される。
Here, when the water removal treatment is performed on a floating structure floating on water, the problem of securing land on land is also solved.

【0015】[0015]

【発明の実施の形態】以下、本発明に係る浚渫泥土の処
理方法および処理設備の実施の形態について、添付図面
を参照して説明する。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Embodiments of a method and a facility for treating dredged mud according to the present invention will be described below with reference to the accompanying drawings.

【0016】(第1実施形態)図1は、本実施形態に係
る浚渫泥土の処理方法を行う手順を示したフローチャー
ト、図2は、一連の処理を行うための設備を示した概念
図である。これらの図でわかるように、本実施形態に係
る処理方法においては、まず、図2(a) に示すように、
海、湖沼、河川等の水域1の水底に堆積した泥土2を浚
渫船3で浚渫する(図1、ステップ101)。浚渫にあ
たっては、高濃度でかつ安定的に浚渫可能なポンプ式高
濃度浚渫船を使用する。かかる高濃度浚渫船の採用によ
り、浚渫泥土に含まれる余剰水の量を極力少なくして、
凝集沈殿池等の大規模な収容空間を要することなく、後
述する密閉型の貯泥槽に浚渫泥土を給送してこれを貯留
することができる。したがって、後工程である凝集沈降
工程および脱水工程を含めた一連の工程を密閉空間内で
処理することができ、悪臭の飛散の問題を解消すること
が可能となるとともに、消臭剤や溶出抑制剤などの混合
による浚渫泥土の無害化を図りやすくなる。
(First Embodiment) FIG. 1 is a flowchart showing a procedure for performing a method of treating dredged mud according to the present embodiment, and FIG. 2 is a conceptual diagram showing equipment for performing a series of processes. . As can be seen from these figures, in the processing method according to the present embodiment, first, as shown in FIG.
The mud 2 deposited on the bottom of the water area 1 such as the sea, lake, river or river is dredged by the dredger 3 (step 101 in FIG. 1). For dredging, use a pump-type high-concentration dredge that can stably dredge with high concentration. By adopting such a high concentration dredger, the amount of surplus water contained in the dredged mud is minimized,
The dredged mud can be fed to and stored in a closed type mud storage tank described later without requiring a large-scale storage space such as a coagulation sedimentation tank. Therefore, a series of processes including the coagulation sedimentation process and the dehydration process, which are the subsequent processes, can be processed in the enclosed space, and it is possible to eliminate the problem of the foul odor scattering, and to control the deodorant and elution. It is easy to make the dredged mud harmless by mixing the agent.

【0017】次に、浚渫された泥土を送泥パイプ4を介
して陸上に設置された貯泥槽5に移送し、該槽に一時的
に貯留する(ステップ102)。貯泥槽5は、密閉式の
タンク本体、その内部に配置された攪拌翼、該攪拌翼を
駆動する駆動機構(図示せず)等から構成され、悪臭を
飛散させることなく浚渫泥土を一時貯留できるようにな
っている。また、槽5内の濃度を比重計で管理し、必要
に応じて浚渫の一時停止や再開を行うようにすれば、槽
内濃度の安定化を図ることができる。
Next, the dredged mud is transferred via a mud feeding pipe 4 to a mud storage tank 5 installed on land, and temporarily stored in the tank (step 102). The mud storage tank 5 is composed of a closed tank main body, a stirring blade disposed inside the tank body, a drive mechanism (not shown) for driving the stirring blade, and the like, and temporarily stores dredged mud without scattering odor. I can do it. The concentration in the tank 5 can be stabilized by managing the concentration in the tank 5 with a hydrometer and suspending or resuming the dredging as necessary.

【0018】なお、高濃度の浚渫船を使用することによ
って含水比を抑えた泥土を貯留するため、貯泥槽5のタ
ンク容量は比較的小規模のもので足りるが、浚渫船3の
処理能力が大きい場合には、貯泥槽5を複数設置するよ
うにしてもよい。また、浚渫された泥土を貯泥槽5に移
す前に予めスクリーンにかけ、比較的粒径の大きな土砂
を選別除去するようにしてもよい。
In order to store mud with a reduced water content by using a high-concentration dredger, the tank capacity of the mud storage tank 5 is relatively small, but the processing capacity of the dredger 3 is large. In this case, a plurality of storage tanks 5 may be provided. Before the dredged mud is transferred to the mud storage tank 5, it may be screened in advance to selectively remove relatively large-sized soil.

【0019】次に、貯泥槽5から送られてきた泥土に凝
集剤タンク6に貯留された凝集剤を添加し、これを例え
ばラインミキサーで管内で攪拌した後、送泥管7を介し
てポンプ8でスラリー槽、シックナ等の凝集沈降槽9に
送り、該槽9内で泥土分を凝集沈降させる(ステップ1
03)。
Next, the coagulant stored in the coagulant tank 6 is added to the mud sent from the mud storage tank 5, and this is agitated in a pipe by, for example, a line mixer, and then is passed through a mud feed pipe 7. The slurry is sent to a coagulation sedimentation tank 9 such as a slurry tank or a thickener by a pump 8, and the mud is coagulated and settled in the tank 9 (step 1).
03).

【0020】凝集剤は、例えば硫酸バンドと呼ばれる硫
酸アルミニウムやPACと呼ばれるポリ塩化アルミニウ
ムといったアルミニウム系の凝集剤や消石灰などのカル
シウム系の凝集剤を乾燥重量1トンあたり10乃至15
0kg程度添加する。
The coagulant is, for example, an aluminum-based coagulant such as aluminum sulfate called polysulfate band or polyaluminum chloride called PAC or a calcium-based coagulant such as slaked lime per 10 tons of dry weight per ton.
Add about 0 kg.

【0021】なお、必要に応じて、消臭剤や有害金属イ
オンの溶出を防止する添加剤を添加してもよい。例え
ば、臭気の原因が弱酸性の硫化水素である場合には、セ
メントや消石灰を添加してpHをアルカリ性にしたり、
過酸化水素を添加して硫黄分を酸化してやることで消臭
を行うことができる。また、鉄、マンガン等の溶出を抑
制したいのであれば、セメント、石灰等でpHをアルカ
リ性にすればよい。
If necessary, a deodorant or an additive for preventing elution of harmful metal ions may be added. For example, if the cause of the odor is weakly acidic hydrogen sulfide, add cement or slaked lime to make the pH alkaline,
By adding hydrogen peroxide to oxidize sulfur, deodorization can be performed. If it is desired to suppress elution of iron, manganese and the like, the pH may be made alkaline with cement, lime or the like.

【0022】次に、凝集沈降槽9内で沈降した泥土を引
き抜き、これをフィルタープレス、ロールプレス等の機
械式脱水処理装置10に移して加圧脱水する(ステップ
104)。なお、凝集沈降槽9の上澄水は、元の水域に
放流する。
Next, the mud which has settled in the coagulation settling tank 9 is pulled out, transferred to a mechanical dewatering apparatus 10 such as a filter press, a roll press or the like, and dewatered under pressure (step 104). The supernatant water of the coagulation settling tank 9 is discharged to the original water area.

【0023】次に、図2(b) に示すように、脱水工程で
生じた脱水ケーキ11を例えばベルトコンベア12およ
び船13を用いて元の水域1に搬送し、これを水底に沈
めて最終処分とする(ステップ105)。
Next, as shown in FIG. 2 (b), the dewatered cake 11 generated in the dewatering step is transported to the original water area 1 using, for example, a belt conveyor 12 and a ship 13, and is submerged to the bottom of the water. It is disposed (step 105).

【0024】ここで、水底に沈められた脱水ケーキ11
は、凝集処理および加圧処理によって水中での分散が抑
止され、再び泥状化することはない。そして、りんや窒
素等の栄養塩は脱水ケーキ内に閉じこめられ、水中に溶
出しにくくなる。
Here, the dewatered cake 11 submerged in the water bottom
Is prevented from dispersing in water by coagulation treatment and pressure treatment, and does not become muddy again. Then, nutrients such as phosphorus and nitrogen are trapped in the dehydrated cake and hardly elute in water.

【0025】以上説明したように、本実施形態に係る浚
渫泥土の処理方法によれば、水質汚染を進行させるヘド
ロ層であっても、これを本実施形態のごとく凝集剤を添
加して凝集沈降させ、これを加圧脱水して脱水ケーキの
状態で元通り沈めれば、栄養塩の水中への溶出を防止す
ることが可能となる。
As described above, according to the method for treating dredged mud according to the present embodiment, even in the case of a sludge layer which causes water pollution, the sludge layer is coagulated and settled by adding a flocculant as in the present embodiment. If this is dehydrated under pressure and submerged in the state of a dehydrated cake, the elution of nutrients into water can be prevented.

【0026】したがって、脱水ケーキの処分場所を新た
に確保する必要なしに、水域の富栄養化、貧酸素化とい
った水質汚染の進行を阻止することができる。また、栄
養塩に限らず、有害金属イオン等の溶出も防止すること
ができる。
Therefore, it is possible to prevent the progress of water pollution such as eutrophication and hypoxia of the water area without having to secure a new disposal site for the dehydrated cake. In addition, elution of harmful metal ions and the like, not limited to nutrient salts, can be prevented.

【0027】なお、脱水ケーキは、元のヘドロを機械脱
水してあるためにその容量は大幅に減少しており、該ケ
ーキを沈めたことで有効貯水量が減少するといったおそ
れはない。
The capacity of the dewatered cake has been greatly reduced because the original sludge has been mechanically dewatered, and there is no danger that the effective water storage capacity will be reduced by sinking the cake.

【0028】(第2実施形態)次に、第2実施形態に係
る浚渫泥土の処理方法および処理設備について説明す
る。なお、第1実施形態と実質的に同一の装置等につい
ては同一の符号を付してその説明を省略する。
(Second Embodiment) Next, a method and equipment for treating dredged mud according to a second embodiment will be described. Note that the same reference numerals are given to the same devices and the like as those in the first embodiment, and description thereof will be omitted.

【0029】図3は、本実施形態に係る浚渫泥土の処理
方法を行う手順を示したフローチャート、図4は、これ
らの処理を行うための設備を示した概念図である。これ
らの図でわかるように、本実施形態に係る処理方法にお
いては、まず、図4に示す浚渫泥土の処理設備21を水
面に浮かべ、これを所定の水域1まで曳航する(図3、
ステップ111)。
FIG. 3 is a flowchart showing a procedure for performing the method for treating dredged mud according to the present embodiment, and FIG. 4 is a conceptual diagram showing equipment for performing these processes. As can be seen from these figures, in the treatment method according to the present embodiment, first, the dredging mud treatment equipment 21 shown in FIG. 4 is floated on the water surface, and this is towed to a predetermined water area 1 (FIG. 3,
Step 111).

【0030】浚渫泥土の処理設備21は、水底に堆積し
た泥土2を浚渫する浚渫装置22と、該浚渫装置22か
ら送られてきた浚渫泥土を貯留する貯泥槽5と、該貯泥
槽5から送られてきた泥土を所定の凝集剤で凝集沈降さ
せる凝集沈降槽9と、凝集剤を貯留した凝集剤タンク6
と、凝集沈降させた泥土を加圧脱水する加圧脱水装置1
0とを浮体構造物23の上に設置して構成してある。浮
体構造物23は、例えばコンクリートブロックや中空鋼
管を適宜連結して製造することができる。
The dredging mud treatment equipment 21 includes a dredging device 22 for dredging the mud 2 deposited on the water bottom, a mud storage tank 5 for storing the dredged mud sent from the dredging device 22, and a mud storage tank 5. Sedimentation tank 9 for coagulating and sedimenting the mud sent from the plant with a predetermined coagulant, and coagulant tank 6 for storing the coagulant
Pressurized dewatering device 1 for pressurizing and dewatering the coagulated sedimented mud
0 is disposed on the floating structure 23. The floating structure 23 can be manufactured by appropriately connecting concrete blocks or hollow steel pipes, for example.

【0031】浚渫装置22は、高濃度でかつ安定的に浚
渫可能なものを採用する。かかる高濃度浚渫装置の採用
により、浚渫泥土に含まれる余剰水の量を極力少なくし
て、凝集沈殿池等の大規模な収容空間を要することな
く、密閉型の貯泥槽に浚渫泥土を給送してこれを貯留す
ることができる。したがって、後工程である凝集沈降工
程および脱水工程を含めた一連の工程を密閉空間内で処
理することができ、悪臭の飛散の問題を解消することが
可能となるとともに、消臭剤や溶出抑制剤などの混合に
よる浚渫泥土の無害化を図りやすくなる。
As the dredging device 22, a device which can stably dredge with high concentration is adopted. By employing such a high concentration dredging device, the amount of surplus water contained in the dredged mud is minimized, and the dredged mud is supplied to the closed type mud storage tank without requiring a large-scale storage space such as a coagulation sedimentation tank. This can be sent and stored. Therefore, a series of processes including the coagulation sedimentation process and the dehydration process, which are the subsequent processes, can be processed in the enclosed space, and it is possible to eliminate the problem of the foul odor scattering, and to control the deodorant and elution. It is easy to make the dredged mud harmless by mixing the agent.

【0032】次に、かかる浚渫装置22で水底に堆積し
た泥土を浚渫し(ステップ112)、引き続いて浚渫泥
土を貯泥槽5に移してこれを該槽に一時的に貯留する
(ステップ113)。
Next, the mud accumulated on the water bottom is dredged by the dredging device 22 (step 112), and subsequently, the dredged mud is transferred to the mud storage tank 5 and temporarily stored in the tank (step 113). .

【0033】なお、浚渫された泥土を貯泥槽5に移す前
に予めスクリーンにかけ、比較的粒径の大きな土砂を選
別除去するようにしてもよい。
It is to be noted that the dredged mud may be screened before being transferred to the mud storage tank 5 so as to selectively remove the soil having a relatively large particle diameter.

【0034】次に、貯泥槽5から送られてきた泥土に凝
集剤タンク6に貯留された凝集剤を添加し、これを例え
ばラインミキサーで管内で攪拌した後、送泥管7を介し
てポンプ8でスラリー槽、シックナ等の凝集沈降槽9に
送り、該槽9内で泥土分を凝集沈降させる(ステップ1
14)。
Next, the coagulant stored in the coagulant tank 6 is added to the mud sent from the mud storage tank 5, and this is stirred in a pipe by, for example, a line mixer. The slurry is sent to a coagulation sedimentation tank 9 such as a slurry tank or a thickener by a pump 8, and the mud is coagulated and settled in the tank 9 (step 1).
14).

【0035】凝集剤については、上述の実施形態とほぼ
同様であるので、その説明を省略する。また、必要に応
じて、消臭剤や有害金属イオンの溶出を防止する添加剤
を添加してもよいが、かかる説明についても同様な理由
により説明を省略する。
The coagulant is substantially the same as in the above-described embodiment, and a description thereof will be omitted. Further, if necessary, a deodorant and an additive for preventing elution of harmful metal ions may be added. However, such description is omitted for the same reason.

【0036】次に、凝集沈降槽9内で沈降した泥土を引
き抜き、これをフィルタープレス、ロールプレス等の機
械式脱水処理装置10に移して加圧脱水する(ステップ
115)。なお、凝集沈降槽9の上澄水は、元の水域に
放流する。
Next, the mud which has settled in the coagulation settling tank 9 is pulled out, transferred to a mechanical dewatering apparatus 10 such as a filter press or a roll press, and dewatered under pressure (step 115). The supernatant water of the coagulation settling tank 9 is discharged to the original water area.

【0037】次に、脱水工程で生じた脱水ケーキ11を
水底に沈めて最終処分とする(ステップ116)。
Next, the dewatered cake 11 generated in the dewatering step is submerged in the water bottom and is finally disposed (step 116).

【0038】以上説明した一連の工程を、浮体構造物2
3の位置を少しずつ変えながら繰り返し行い、所定範囲
の水底の泥土を処理する。
The series of steps described above are performed by the floating structure 2
The process is repeated while changing the position of No. 3 little by little to treat mud on the bottom of the water in a predetermined range.

【0039】ここで、水底に沈められた脱水ケーキ11
は、凝集処理および加圧処理によって水中での分散が抑
止され、再び泥状化することはない。そして、りんや窒
素等の栄養塩は脱水ケーキ内に閉じこめられ、水中に溶
出しにくくなる。
Here, the dewatered cake 11 submerged in the water bottom
Is prevented from dispersing in water by coagulation treatment and pressure treatment, and does not become muddy again. Then, nutrients such as phosphorus and nitrogen are trapped in the dehydrated cake and hardly elute in water.

【0040】以上説明したように、本実施形態に係る浚
渫泥土の処理方法および処理設備によれば、第1実施形
態と同様、水質汚染を進行させるヘドロ層であっても、
これを本実施形態のごとく凝集剤を添加して凝集沈降さ
せ、これを加圧脱水して脱水ケーキの状態で元通り沈め
れば、栄養塩の水中への溶出を防止することが可能とな
る。
As described above, according to the method and equipment for treating dredged mud according to the present embodiment, similar to the first embodiment, even in a sludge layer that promotes water pollution,
If this is added as a coagulant and coagulated and sedimented as in the present embodiment, it is possible to prevent nutrient salts from being eluted into water by dehydrating under pressure and submerging in the state of a dehydrated cake. .

【0041】したがって、脱水ケーキの処分場所を新た
に確保する必要なしに、水域の富栄養化、貧酸素化とい
った水質汚染の進行を阻止することができる。また、栄
養塩に限らず、有害金属イオン等の溶出も防止すること
ができる。
Therefore, it is possible to prevent the progress of water pollution such as eutrophication and hypoxia of the water area without having to newly secure a disposal site for the dehydrated cake. In addition, elution of harmful metal ions and the like, not limited to nutrient salts, can be prevented.

【0042】なお、脱水ケーキは、元のヘドロを機械脱
水してあるためにその容量は大幅に減少しており、該ケ
ーキを沈めたことで有効貯水量が減少するといったおそ
れはない。
The capacity of the dewatered cake is greatly reduced because the original sludge is mechanically dewatered, and there is no danger that the effective water storage capacity will be reduced by sinking the cake.

【0043】また、本実施形態によれば、凝集沈降およ
び加圧脱水といった水分除去処理を水面に浮かべた浮体
構造物の上で行うようにしたので、陸地に用地を確保す
る必要がなくなる。
Further, according to the present embodiment, since the water removal processing such as coagulation sedimentation and pressure dehydration is performed on the floating structure floating on the water surface, it is not necessary to secure land on land.

【0044】また、本実施形態によれば、浚渫泥土の処
理に合わせて浮体構造物を曳航しその位置を変更してい
けば、広範囲にわたって浚渫泥土を処理することができ
る。
Further, according to the present embodiment, dredging mud can be processed over a wide range if the position of the floating structure is changed by towing the floating structure in accordance with the processing of dredging mud.

【0045】本実施形態では、高濃度浚渫によって沈殿
池の設置を省略する構成としたが、沿岸から離れた箇所
での作業となって悪臭が市街地にまで飛散するおそれは
少ないため、大型の浮体構造物に開放型の沈殿池を設置
し、該沈殿池において大量の余剰水を処理する方法を採
用してもよい。
In this embodiment, the construction of the sedimentation basin is omitted by the high concentration dredging. However, since the work is performed at a location away from the coast and the odor is unlikely to scatter to the city, a large floating body is required. An open sedimentation basin may be installed in the structure, and a method of treating a large amount of excess water in the sedimentation basin may be adopted.

【0046】[0046]

【発明の効果】以上述べたように、本発明の浚渫泥土の
処理方法は、水底に堆積した泥土を浚渫し、次いで、浚
渫された泥土に対して凝集剤を用いた凝集沈降処理およ
び加圧脱水処理を含む水分除去処理を行い、次いで、該
水分除去処理で生じたケーキを水底に沈めるようにした
ので、脱水ケーキの処分場所を新たに確保する必要なし
に浚渫泥土を処理して水質汚染の進行を阻止することが
できる。
As described above, the method for treating dredged mud according to the present invention is to dredge mud deposited on the water bottom, and then subject the dredged mud to coagulation sedimentation treatment using a flocculant and pressurization. A water removal process including a dehydration process was performed, and then the cake generated in the water removal process was sunk to the bottom of the water. Can be prevented.

【0047】また、本発明の浚渫泥土の処理設備は、水
底に堆積した泥土を浚渫する浚渫装置と、該浚渫装置か
ら送られてきた浚渫泥土を貯留する貯泥槽と、該貯泥槽
から送られてきた泥土を所定の凝集剤で凝集沈降させる
凝集沈降槽と、凝集沈降させた泥土を加圧脱水する加圧
脱水装置とを所定の浮体構造物の上に設置したので、浚
渫泥土を脱水処理するための用地や脱水ケーキの処分場
所を確保する必要なしに浚渫泥土を処理して水質汚染の
進行を阻止することができる。
Further, the dredging mud treatment facility of the present invention comprises a dredging device for dredging mud deposited on the water bottom, a mud storage tank for storing the dredged mud sent from the dredging device, and The coagulation sedimentation tank for coagulating and sedimenting the sent mud with a predetermined coagulant, and the pressurized dewatering device for pressurizing and dewatering the coagulated and sedimented mud were installed on a predetermined floating structure, so dredged mud was removed. The dredged mud can be treated to prevent the progress of water pollution without having to secure a site for the dehydration treatment or a disposal site for the dewatered cake.

【0048】[0048]

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

【図1】第1実施形態に係る浚渫泥土の処理方法を示し
たフローチャート。
FIG. 1 is a flowchart showing a method for treating dredged mud according to a first embodiment.

【図2】第1実施形態に係る浚渫泥土の処理方法を実施
するための設備を示した概念図。
FIG. 2 is a conceptual diagram showing equipment for carrying out the method for treating dredged mud according to the first embodiment.

【図3】第2実施形態に係る浚渫泥土の処理方法を示し
たフローチャート。
FIG. 3 is a flowchart showing a method for treating dredged mud according to a second embodiment.

【図4】第2実施形態に係る浚渫泥土の処理方法を実施
するための設備を示した概念図。
FIG. 4 is a conceptual diagram showing equipment for carrying out a method for treating dredged mud according to a second embodiment.

【符号の説明】[Explanation of symbols]

3 浚渫船 5 貯泥槽 6 凝集剤タンク 9 凝集沈降槽 10 加圧脱水装置 11 脱水ケーキ 21 処理設備 22 浚渫装置 23 浮体構造物 DESCRIPTION OF SYMBOLS 3 Dredge vessel 5 Mud storage tank 6 Coagulant tank 9 Coagulation sedimentation tank 10 Pressure dehydration apparatus 11 Dehydration cake 21 Processing equipment 22 Dredging apparatus 23 Floating structure

フロントページの続き (56)参考文献 特開 平4−228730(JP,A) 特開 平8−270002(JP,A) 実用新案登録3008015(JP,Y2) (58)調査した分野(Int.Cl.6,DB名) E02F 3/88 C02F 11/00 ZAB C02F 11/12 ZAB C02F 11/14 ZAB Continuation of the front page (56) References JP-A-4-228730 (JP, A) JP-A-8-270002 (JP, A) Utility model registration 3008015 (JP, Y2) (58) Fields investigated (Int.Cl) . 6, DB name) E02F 3/88 C02F 11/00 ZAB C02F 11/12 ZAB C02F 11/14 ZAB

Claims (3)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 水底に堆積した泥土を浚渫し、次いで、
浚渫された泥土に対して凝集剤を用いた凝集沈降処理お
よび加圧脱水処理を含む水分除去処理を行い、次いで、
該水分除去処理で生じたケーキを水底に沈めることを特
徴とする浚渫泥土の処理方法。
1. Dredging mud deposited on the bottom of the water,
The dredged mud is subjected to a coagulation sedimentation process using a coagulant and a water removal process including a pressure dehydration process,
A method for treating dredged mud, characterized by submerging the cake generated by the water removal treatment to the bottom of the water.
【請求項2】 前記水分除去処理を水上に浮かべた浮体
構造物の上で処理する請求項1記載の浚渫泥土の処理方
法。
2. The method for treating dredged mud according to claim 1, wherein the water removal treatment is performed on a floating structure floating on water.
【請求項3】 水底に堆積した泥土を浚渫する浚渫装置
と、該浚渫装置から送られてきた浚渫泥土を貯留する貯
泥槽と、該貯泥槽から送られてきた泥土を所定の凝集剤
で凝集沈降させる凝集沈降槽と、凝集沈降させた泥土を
加圧脱水する加圧脱水装置とを所定の浮体構造物の上に
設置したことを特徴とする浚渫泥土の処理設備。
3. A dredging device for dredging mud deposited on the water floor, a mud storage tank for storing the dredged mud sent from the dredging device, and a mud fed from the mud storage tank with a predetermined flocculant. A dredging mud treatment facility, wherein a coagulating sedimentation tank for coagulating and sedimenting and a pressure dewatering device for pressurizing and dewatering the coagulated sediment are installed on a predetermined floating structure.
JP25018295A 1995-09-04 1995-09-04 Dredging mud treatment method and treatment equipment Expired - Lifetime JP2913632B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP25018295A JP2913632B2 (en) 1995-09-04 1995-09-04 Dredging mud treatment method and treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP25018295A JP2913632B2 (en) 1995-09-04 1995-09-04 Dredging mud treatment method and treatment equipment

Publications (2)

Publication Number Publication Date
JPH0971966A JPH0971966A (en) 1997-03-18
JP2913632B2 true JP2913632B2 (en) 1999-06-28

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Country Link
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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001303461A (en) * 2000-04-28 2001-10-31 Asahi Denka Kogyo Kk Thickener for printing paste and composition for printing paste containing thickener for printing paste
KR100457383B1 (en) * 2002-03-14 2004-11-16 김남천 Accumulation matter processing method and system for water purification of lake and reservoir
JP4642671B2 (en) * 2006-02-10 2011-03-02 株木建設株式会社 Underwater ground improvement method
JP4758811B2 (en) * 2006-04-25 2011-08-31 株式会社トクヤマ Submarine dredging treatment method
KR100942444B1 (en) * 2008-01-31 2010-02-17 우진개발 주식회사 Sludge Treatment Method Using Dredger
JP5309747B2 (en) * 2008-07-15 2013-10-09 株式会社大林組 Carrier ship
CN108193726B (en) * 2017-12-29 2021-02-09 吴海锋 Multifunctional silt remover for hydraulic engineering
CN114075835A (en) * 2020-08-18 2022-02-22 伟泰科技(无锡)有限公司 A high-efficiency river dredging system

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH038015Y2 (en) 1984-08-22 1991-02-27

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH038015Y2 (en) 1984-08-22 1991-02-27

Also Published As

Publication number Publication date
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