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JP4207479B2 - How to treat dredged mud - Google Patents
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JP4207479B2 - How to treat dredged mud - Google Patents

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Publication number
JP4207479B2
JP4207479B2 JP2002206624A JP2002206624A JP4207479B2 JP 4207479 B2 JP4207479 B2 JP 4207479B2 JP 2002206624 A JP2002206624 A JP 2002206624A JP 2002206624 A JP2002206624 A JP 2002206624A JP 4207479 B2 JP4207479 B2 JP 4207479B2
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Prior art keywords
mud
water
primary
dredged
cake
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JP2004049933A (en
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正夫 黒岩
純 光本
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Obayashi Corp
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Obayashi Corp
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    • 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

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Treatment Of Sludge (AREA)

Description

【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に関する。
【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。
【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。
【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。
【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。
【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。
【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。
【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とともに、そのときに生じた脱水ケーキを有効利用することが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。
【0009】
【課題を解決するための手段】
上記目的を達成するため、本発明に係る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、浚渫された泥土を土砂分離し、次いで、土砂分離された泥土を遠心分離する一方、海、湖沼等の沿岸部水底に布製型枠を敷設し、該布製型枠内に前記遠心分離で生じた一次脱水ケーキを充填する浚渫泥土の処理方法であって、前記遠心分離で生じたオーバー泥水を凝集沈降させた後、該凝集沈降分を加圧脱水し、該加圧脱水で生じた二次脱水ケーキを前記一次脱水ケーキが充填された前記布製型枠の上に敷き均すものである。
【0012】
本発明に係る浚渫泥土の処理方法においては、まず、海、湖沼等の水底に堆積した泥土をグラブ浚渫船等で浚渫する。
【0013】
次に、浚渫された泥土を土砂分離装置等を用いて土砂分離する。
【0014】
次に、土砂分離された泥土を遠心分離し、そのアンダーを一次脱水ケーキとする。遠心分離は、例えばスクリューデカンタを用いることができる。
【0015】
一方、海、湖沼等の沿岸部水底に布製型枠を敷設する。
【0016】
次に、遠心分離で生じた一次脱水ケーキを布製型枠内に充填する。このとき、必要に応じて一次脱水ケーキに固化剤を添加しておく。
【0017】
このようにすると、一次脱水ケーキは、沿岸部水底に敷設された布製型枠内に充填されることにより、最終処分の必要がなくなるとともに、沿岸部水底に敷設された布製型枠内に一次脱水ケーキが充填されてなる造成物は、さまざまな用途に有効利用することが可能となる。例えば、布製型枠内に一次脱水ケーキを充填することで沿岸部水底に干潟を造成することができる。
【0018】
ここで、遠心分離で生じたオーバー泥水を凝集沈降させた後、該凝集沈降分を加圧脱水し、該加圧脱水で生じた二次脱水ケーキを一次脱水ケーキが充填された布製型枠の上に敷き均すようにしたならば、遠心分離のオーバー泥水に残留していた土粒子分までも布製型枠の上に敷き均すことで有効利用することが可能となり、二次脱水ケーキの最終処分が不要になるとともに、結果として、浚渫泥土中の土粒子分はそのほとんどが有効されることとなる。
【0019】
なお、一次脱水ケーキは、遠心分離の効果によって土粒子が互いに分離しにくい状態となっているため、布製型枠の隙間を介して水中に分散するおそれはないとともに、二次脱水ケーキについては、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。
【0020】
そして、りんや窒素等の栄養塩は、このように一次脱水ケーキ及び二次脱水ケーキ内に閉じこめられ、水中には溶出しないため、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とともに、一次脱水ケーキや二次脱水ケーキを用いて沿岸部水底に例えば干潟を造成することができるため、優れた自然環境を形成することも可能となる。
【0021】
【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。
【0022】
図1及び図2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3及び図4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3(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、同図に示すグラブ浚渫船でもよいが、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ようにしてもよい。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することができる。
【0023】
次に、浚渫された泥土2を図3(b)に示すように、陸上に設置された原水槽5に投入し一時貯留する(ステップ102)。なお、浚渫された泥土を原水槽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。
【0024】
次に、原水槽5から送られてきた泥土を土砂分離装置6で土砂分離し、そのオーバー泥水を貯留槽7に一次貯留する(ステップ103)。
【0025】
次に、図3(c)に示すように、貯留槽7内のオーバー泥水をスクリューデカンタ8に打ち込んで分級するとともに、そのアンダーを一次脱水ケーキ14とする(ステップ104)。
【0026】
一方、スクリューデカンタ8のオーバー泥水に凝集剤タンク9に貯留された凝集剤を添加し、これをラインミキサー10で管内で撹拌した後、送泥管11を介してスラリー槽等の凝集沈降槽12に送り、該槽内で泥土分を凝集沈降させる(ステップ105)。
【0027】
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150kg程度添加する。
【0028】
なお、必要に応じて、pH調整剤、消臭剤、有害金属イオンの溶出を防止する添加剤等を添加してもよい。例えば、臭気の原因となる弱酸性の硫化水素が含まれている場合には、セメントや消石灰を添加してpHを中性又は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を中性又はアルカリ性にすればよい。
【0029】
次に、凝集沈降槽12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13に移して加圧脱水し、そのアンダーを二次脱水ケーキ15とする(ステップ106)。
【0030】
なお、機械式脱水処理装置13からの濾液は、pH調整等、必要な処理を行った後、適宜、河川等に放流する。
【0031】
一方、図4(a)に示すように、海、湖沼等の沿岸部水底21に布製型枠22を敷設する(ステップ107)。
【0032】
布製型枠22は、例えば筒状の布製生地を格子状に連通接続してなり、その中空内部にフレッシュコンクリートやフレッシュモルタルを注入するようになっている法面保護や護岸を用途した市販のコンクリートマットを使用することができる。具体的には、タコムの商品名で太陽工業株式会社から市販されているものや、ファブリフォーム(登録商標)の商品名で旭化成ジオテック株式会社から市販されているものを用いることができる。
【0033】
次に、図4(b)に示すように、布製型枠22内に図示しない送泥ポンプを介して一次脱水ケーキ14を充填し、沿岸部水底21にマット状造成物23を造成する(ステップ108)。一次脱水ケーキ14を充填するにあたっては、必要に応じてセメント等の固化剤を適宜添加しておく。
【0034】
次に、図4(c)に示すように、マット状造成物23の上に二次脱水ケーキ15を敷き均し、さらにその上に必要に応じて覆砂を施して干潟24を造成する(ステップ109)。二次脱水ケーキ15や覆砂の厚みあるいは布製型枠の厚みは、満潮位(H.W.L)や干潮位(L.W.L)を考慮して適宜決定する。
【0035】
ここで、一次脱水ケーキ14は、遠心分離の効果によって土粒子が互いに分離しにくい状態となっているため、布製型枠22の隙間を介して水中に分散するおそれはないとともに、二次脱水ケーキ15については、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。
【0036】
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、浚渫された泥土2を土砂分離し、次いで、土砂分離された泥土をスクリューデカンタ8で遠心分離する一方、海、湖沼等の沿岸部水底21に布製型枠22を敷設し、該布製型枠内に遠心分離で生じた一次脱水ケーキ14を充填するとともに、加圧脱水で生じた二次脱水ケーキ15を布製型枠22の上に敷き均すようにしたので、一次脱水ケーキ14及び二次脱水ケーキ15を用いて沿岸部水底21に図4(c)に示す干潟24を造成することが可能となり、該干潟に育成する葦などの植物や該干潟に集まってくる鳥類あるいは魚介類といったさまざまな水棲生物が互いに作用しあって優れた自然環境を形成することが可能となる。
【0037】
また、本実施形態に係る浚渫泥土の処理方法によれば、浚渫泥土を脱水して得られた一次脱水ケーキ14や二次脱水ケーキ15を干潟24の造成に有効利用することが可能となり、該脱水ケーキの最終処分地が不要となる。
【0038】
なお、浚渫泥土に含まれていたりんや窒素等の栄養塩は、一次脱水ケーキ14及び二次脱水ケーキ15内に閉じこめられ、水中には溶出しない。そのため、一次脱水ケーキ14及び二次脱水ケーキ15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を阻止することも可能となる。
【0039】
また、本実施形態に係る浚渫泥土の処理方法によれば、スクリューデカンタ8からのアンダー、すなわち一次脱水ケーキ14を布製型枠22内に充填するようにしたので、比較的軟弱で取り扱いが難しいスクリューデカンタからの脱水ケーキの水中への拡散を防止するとともに、その形状を長期間維持することが可能となり、水流によって干潟の形状が変化してしまうといった事態を未然に防止することが可能となる。
【0040】
本実施形態では、布製型枠22内に一次脱水ケーキ14が充填されてなる造成物23の上に二次脱水ケーキ15を敷き均すようにしたが、場合によっては二次脱水ケーキ15の敷き均しを省略してもかまわないし、その場合に該布製型枠の上を覆砂するかどうかも任意である。
【0041】
また、本実施形態では、布製型枠22内に一次脱水ケーキ14を充填することで沿岸部水底21に干潟24を造成するようにしたが、沿岸部水底にどのような造成物を造成するかは任意であり、例えば通常の海浜を造成する場合に本発明を適用してもよい。
【0042】
また、本実施形態では特に言及しなかったが、土砂分離装置6のオーバー泥水を貯留槽7に一次貯留する際、必要に応じて上述したと同様の凝集剤を添加し、凝集沈殿を行うようにしてもよい。
【0043】
また、本実施形態では、スクリューデカンタ8のアンダーを一次脱水ケーキ14とするとともに、該スクリューデカンのオーバー泥水に対して凝集沈降処理を凝集沈降槽12にて行い(ステップ104〜105)、次いで、該凝集沈降槽内で沈降した泥土を引き抜いて機械式脱水処理装置13で加圧脱水し、そのアンダーを二次脱水ケーキ15としたが(ステップ106)、貯留槽7内のオーバー泥水に含まれる土粒子をスクリューデカンタ8で実質的にすべて分離することができるのであれば、そのアンダーである一次脱水ケーキ14を、上述したと同様、布製型枠22内に充填して沿岸部水底21にマット状造成物23を造成する一方、二次脱水ケーキ15は発生しないため、これをマット状造成物23の上に敷き均す工程を省略するようにしてもかまわない。
【0044】
なお、かかる構成の場合、スクリューデカンタ8は脱水機として機能するとともに、凝集剤タンク9、ラインミキサー10、送泥管11、凝集沈降槽12及び機械式脱水処理装置13は不要となる。また、スクリューデカンタ8のオーバー水は、pH調整等、必要な処理を行った後、適宜、河川等に放流すればよい。
【0045】
【発明の効果】
以上述べたように、本発明に係る浚渫泥土の処理方法によれば、一次脱水ケーキや二次脱水ケーキを用いて沿岸部水底に干潟等の造成物を造成することが可能となり、浚渫泥土を脱水して得られた一次脱水ケーキや二次脱水ケーキを有効利用することができるとともに、該脱水ケーキの最終処分地も不要となる。
【0046】
【図面の簡単な説明】
【図1】本実施形態に係る浚渫泥土の処理方法の手順を示したフローチャート。
【図2】同じく本実施形態に係る浚渫泥土の処理方法の手順を示したフローチャート。
【図3】本実施形態に係る浚渫泥土の処理方法を実施している様子を示した作業図。
【図4】引き続き本実施形態に係る浚渫泥土の処理方法を実施している様子を示した作業図。
【符号の説明】
14 一次脱水ケーキ
15 二次脱水ケーキ
22 布製型枠
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method for treating dredged mud for the purpose of improving the water quality of seas, lakes or rivers.
[0002]
[Prior art]
Seas, lakes, and rivers are attracting attention as spaces for multipurpose use, including living and leisure. On the other hand, in closed waters, eutrophication and hypoxia with organic substances have progressed, and such water pollution There is an urgent need for countermeasures.
[0003]
Water pollution caused by organic matter is caused by excessive inflow load from the land area, and is gradually being improved by reducing industrial wastewater and using organic detergents. It accumulates on the sea floor without being decomposed to form a sludge layer called sediment, from which nutrient salts such as nitrogen and phosphorus are eluted into the water and cause water pollution.
[0004]
Therefore, it is important to reduce the elution of nutrient salts from the sediment by taking measures such as removing mud with high organic matter content by dredging.
[0005]
Here, when dredging mud deposited on the bottom of the water, a large amount of excess water is sucked up together with the mud, and the water content becomes extremely high. Therefore, it is necessary to separate and remove the excess water from the mud by sun drying, dewatering with a drain material, mechanical dewatering with a pressure dewatering device such as a filter press.
[0006]
[Problems to be solved by the invention]
However, even when mechanical dehydration is performed, a large sedimentation basin is required to separate a large amount of surplus water contained in dredged mud. Considering the recent land conditions, it was extremely difficult to secure such a large site, and the problem was that it was difficult to install facilities due to the foul odor scattered around.
[0007]
In addition, there has been a problem that it is difficult to secure a place for disposal of a large amount of dehydrated cake produced in the final process of mechanical dehydration.
[0008]
The present invention has been made in consideration of the above-mentioned circumstances, and the progress of water pollution by treating dredged mud without the need to secure a site for dewatering dredged mud and a site for disposing dewatered cake. An object of the present invention is to provide a method for treating dredged mud that can effectively prevent dewatering cake generated at that time.
[0009]
[Means for Solving the Problems]
In order to achieve the above object, the dredged mud treatment method according to the present invention dredged mud deposited on the bottom of the water, then separated the dredged mud, and then separated the earth and sand. This is a method for treating dredged mud, in which a cloth formwork is laid on the bottom of a coastal area such as a sea or a lake, and the primary dewatered cake generated by the centrifugation is filled in the cloth formwork. Then, after coagulating and sedimenting the over mud produced by the centrifugation, the coagulated sediment is subjected to pressure dehydration, and the secondary dehydrated cake produced by the pressure dehydration is filled with the primary dehydrated cake. It is laid on the frame and leveled .
[0012]
In the dredged mud processing method according to the present invention, first, mud deposited on the bottom of the sea, lakes and the like is dredged with a grab dredger or the like.
[0013]
Next, the dredged mud is separated into sediment using a sediment separator or the like.
[0014]
Next, the mud thus separated is centrifuged, and the underside is used as a primary dewatered cake. For example, a screw decanter can be used for the centrifugation.
[0015]
On the other hand, cloth formwork will be laid on the bottom of coastal areas such as seas and lakes.
[0016]
Next, the primary dehydrated cake generated by centrifugation is filled into a cloth mold. At this time, a solidifying agent is added to the primary dehydrated cake as necessary.
[0017]
In this way, the primary dewatered cake is filled in the cloth formwork laid on the coastal water bottom, eliminating the need for final disposal, and the primary dewatering in the cloth formwork laid on the coastal water bottom. The product formed by filling the cake can be effectively used for various purposes. For example, it is possible to create a tidal flat on the coastal water bottom by filling a primary dehydrated cake in a cloth formwork.
[0018]
Here, after the over mud produced by centrifugation is coagulated and settled, the coagulated sediment is subjected to pressure dehydration, and the secondary dewatered cake generated by the pressure dewatering is filled with a primary dewatered cake. If it is spread on the top, it will be possible to effectively use even the soil particles remaining in the centrifuge over mud water on the cloth formwork. As a result, most of the soil particles in the dredged mud are effective.
[0019]
In addition, since the primary dewatered cake is in a state in which the soil particles are difficult to separate from each other due to the effect of centrifugation, there is no risk of being dispersed in water through the gaps in the cloth formwork, and for the secondary dehydrated cake, Dispersion in water is suppressed by the effect of pressure dehydration and does not become muddy again.
[0020]
Since nutrient salts such as phosphorus and nitrogen are confined in the primary dehydrated cake and the secondary dehydrated cake in this way and do not elute into the water, it is not necessary to newly secure a disposal place for the dehydrated cake. Water pollution such as eutrophication and hypoxia of water is prevented, and an excellent natural environment can be created because, for example, tidal flats can be created at the bottom of coastal areas using primary and secondary dehydrated cakes. It is also possible to do.
[0021]
DETAILED DESCRIPTION OF THE INVENTION
DESCRIPTION OF EMBODIMENTS Hereinafter, embodiments of a dredged mud disposal method according to the present invention will be described 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.
[0022]
FIGS. 1 and 2 are flowcharts showing a procedure for performing the dredged mud processing method according to the present embodiment, and FIGS. 3 and 4 are conceptual diagrams showing equipment for performing a series of processing. As can be seen from these figures, in the treatment method according to the present embodiment, first, as shown in FIG. 3 (a), mud soil 2 deposited on the bottom of the water area 1 such as the sea, lake, river, etc. Hesitate (FIG. 1, step 101). For dredging, the grab dredger shown in the figure may be used, but a pump type high concentration dredger capable of dredging with high concentration and stability may be used. By employing such a high-concentration dredger, the amount of surplus water contained in dredged mud can be reduced as much as possible.
[0023]
Next, the dredged mud 2 is put into the raw water tank 5 installed on land as shown in FIG. 3 (b) and temporarily stored (step 102). In addition, before transferring the dredged mud to the raw water tank 5, it may be screened in advance to selectively remove earth and sand having a relatively large particle size.
[0024]
Next, the mud sent from the raw water tank 5 is separated by the earth / sand separator 6 and the over mud is primarily stored in the storage tank 7 (step 103).
[0025]
Next, as shown in FIG. 3 (c), the over mud water in the storage tank 7 is driven into the screw decanter 8 and classified, and the underflow is used as the primary dewatered cake 14 (step 104).
[0026]
On the other hand, the flocculant stored in the flocculant tank 9 is added to the over mud water of the screw decanter 8, and the flocculant is stirred in the pipe by the line mixer 10, and then the flocculant settling tank 12 such as a slurry tank is passed through the mud pipe 11. The mud is agglomerated and settled in the tank (step 105).
[0027]
As the flocculant, for example, about 10 to 150 kg of aluminum-based flocculant such as aluminum sulfate called sulfate band and polyaluminum chloride called PAC and calcium-based flocculant such as slaked lime are added.
[0028]
In addition, you may add a pH adjuster, a deodorizing agent, the additive which prevents the elution of a harmful metal ion, etc. as needed. For example, if weakly acidic hydrogen sulfide that causes odor is contained, add cement or slaked lime to make the pH neutral or alkaline, or add hydrogen peroxide to oxidize sulfur. Deodorization can be performed with. If it is desired to suppress elution of iron, manganese, etc., the pH may be neutral or alkaline with cement, lime, or the like.
[0029]
Next, the mud settled in the coagulation sedimentation tank 12 is drawn out, transferred to a mechanical dehydration processing device 13 such as a filter press or a roll press, and dehydrated under pressure, and the underside is used as a secondary dehydrated cake 15 (step) 106).
[0030]
The filtrate from the mechanical dehydration apparatus 13 is discharged to a river or the like as appropriate after performing necessary treatments such as pH adjustment.
[0031]
On the other hand, as shown in FIG. 4 (a), a cloth form 22 is laid on the bottom 21 of the coastal area such as the sea or lake (step 107).
[0032]
The cloth formwork 22 is a commercially available concrete used for slope protection or revetment in which, for example, tubular cloth fabrics are connected in a grid pattern, and fresh concrete or fresh mortar is poured into the hollow interior. A mat can be used. Specifically, a product commercially available from Taiyo Kogyo Co., Ltd. under the trade name of Tacom, or a product commercially available from Asahi Kasei Geotech Co., Ltd. under the trade name of Fabry Foam (registered trademark) can be used.
[0033]
Next, as shown in FIG. 4 (b), the primary dewatered cake 14 is filled into the cloth form 22 via a mud pump (not shown), and a mat-like composition 23 is formed on the coastal water bottom 21 (step). 108). In filling the primary dewatered cake 14, a solidifying agent such as cement is appropriately added as necessary.
[0034]
Next, as shown in FIG. 4 (c), a secondary dewatered cake 15 is spread on the mat-like composition 23 and further covered with sand as necessary to create a tidal flat 24 ( Step 109). The thickness of the secondary dewatered cake 15 and the sand cover or the thickness of the cloth formwork is appropriately determined in consideration of the high tide level (HWL) and the low tide level (LWL).
[0035]
Here, since the primary dehydrated cake 14 is in a state in which the soil particles are difficult to separate from each other due to the effect of centrifugal separation, there is no possibility that the primary dehydrated cake 14 will be dispersed in water through the gaps in the cloth form 22, and the secondary dehydrated cake. About 15, the dispersion | distribution in water is suppressed by the effect of pressure dehydration, and it does not become muddy again.
[0036]
As described above, according to the dredged mud processing method according to the present embodiment, the dredged mud 2 is separated into the earth and sand, and then the separated mud is centrifuged with the screw decanter 8, while the sea, the lake A cloth form 22 is laid on the water bottom 21 of the coastal area, etc., and the primary dehydrated cake 14 generated by centrifugation is filled in the cloth form, and the secondary dehydrated cake 15 generated by pressure dehydration is filled with the cloth form. As shown in FIG. 4 (c), the tidal flat 24 shown in FIG. 4 (c) can be formed on the coastal bottom 21 using the primary dehydrated cake 14 and the secondary dehydrated cake 15. Various aquatic organisms such as birds and fish and shellfish gathered in the tidal flat can interact with each other to form an excellent natural environment.
[0037]
In addition, according to the dredged mud processing method according to the present embodiment, the primary dewatered cake 14 and the secondary dewatered cake 15 obtained by dewatering the dredged mud can be effectively used for creating the tidal flat 24, The final disposal site for dehydrated cake is no longer required.
[0038]
In addition, nutrient salts such as phosphorus and nitrogen contained in the dredged mud are confined in the primary dehydrated cake 14 and the secondary dehydrated cake 15 and do not elute in water. Therefore, it is also possible to prevent the progress of water pollution such as eutrophication and hypoxia of the water area without newly securing a disposal place for the primary dehydrated cake 14 and the secondary dehydrated cake 15.
[0039]
In addition, according to the dredged mud processing method according to the present embodiment, the underflow from the screw decanter 8, that is, the primary dewatered cake 14 is filled in the cloth mold 22, so that the screw is relatively soft and difficult to handle. While preventing the dewatered cake from decanter from diffusing into the water, it is possible to maintain its shape for a long period of time, and to prevent the situation where the shape of the tidal flat changes due to the water flow.
[0040]
In this embodiment, the secondary dehydrated cake 15 is spread on the composition 23 in which the primary dehydrated cake 14 is filled in the cloth form 22, but in some cases, the secondary dehydrated cake 15 is spread. The leveling may be omitted, and in this case, whether or not to cover the cloth formwork is optional.
[0041]
Further, in this embodiment, the primary dewatered cake 14 is filled in the cloth form 22 to create the tidal flat 24 on the coastal bottom 21. What kind of composition is created on the coastal bottom. Is optional. For example, the present invention may be applied to the case of creating a normal beach.
[0042]
Although not particularly mentioned in the present embodiment, when the over mud of the sediment separator 6 is primarily stored in the storage tank 7, a coagulant similar to that described above is added as necessary to perform coagulation sedimentation. It may be.
[0043]
In the present embodiment, the underside of the screw decanter 8 is used as the primary dewatered cake 14, and the coagulation sedimentation treatment is performed in the coagulation sedimentation tank 12 on the over mud of the screw decane (steps 104 to 105). The mud settled in the agglomeration settling tank is pulled out and dehydrated under pressure by the mechanical dehydration processing device 13 to form a secondary dewatered cake 15 (step 106), which is included in the over mud water in the storage tank 7. If substantially all of the soil particles can be separated by the screw decanter 8, the primary dewatered cake 14 which is the underside of the soil particles is filled in the cloth mold 22 and mated on the coastal bottom 21 as described above. On the other hand, since the secondary dehydrated cake 15 is not generated, the step of spreading this on the mat-like product 23 is omitted. It may also be in.
[0044]
In this configuration, the screw decanter 8 functions as a dehydrator, and the coagulant tank 9, the line mixer 10, the mud pipe 11, the coagulation sedimentation tank 12, and the mechanical dehydration apparatus 13 are not required. Further, the over water of the screw decanter 8 may be discharged into a river or the like as appropriate after performing necessary treatment such as pH adjustment.
[0045]
【The invention's effect】
As described above, according to the dredged mud disposal method according to the present invention, it becomes possible to create a tidal flat or other constructed material on the coastal bottom using the primary dewatered cake or the secondary dewatered cake. The primary dehydrated cake and the secondary dehydrated cake obtained by dehydration can be used effectively, and the final disposal site for the dehydrated cake is not required.
[0046]
[Brief description of the drawings]
FIG. 1 is a flowchart showing a procedure of a method for treating dredged mud according to the present embodiment.
FIG. 2 is a flowchart showing the procedure of the dredged clay treatment method according to the present embodiment.
FIG. 3 is a work diagram showing a state in which the method for treating dredged mud according to the present embodiment is being carried out.
FIG. 4 is a work diagram showing a state in which the dredged clay treatment method according to the present embodiment is being carried out.
[Explanation of symbols]
14 Primary dehydrated cake 15 Secondary dehydrated cake 22 Fabric formwork

Claims (1)

水底に堆積した泥土を浚渫し、次いで、浚渫された泥土を土砂分離し、次いで、土砂分離された泥土を遠心分離する一方、海、湖沼等の沿岸部水底に布製型枠を敷設し、該布製型枠内に前記遠心分離で生じた一次脱水ケーキを充填する浚渫泥土の処理方法であって、
前記遠心分離で生じたオーバー泥水を凝集沈降させた後、該凝集沈降分を加圧脱水し、該加圧脱水で生じた二次脱水ケーキを前記一次脱水ケーキが充填された前記布製型枠の上に敷き均すことを特徴とする浚渫泥土の処理方法。
The mud deposited on the bottom of the water is dredged, then the dredged mud is separated into sediments, and then the separated mud is centrifuged, while a cloth formwork is laid on the bottom of the coastal area of the sea, lake, etc. A method for treating dredged mud that fills a cloth formwork with the primary dewatered cake generated by the centrifugation ,
After coagulating and sedimenting the over mud produced by the centrifugal separation, the coagulated sediment is subjected to pressure dehydration, and the secondary dewatered cake produced by the pressure dewatering is added to the cloth formwork filled with the primary dewatered cake. A method for treating dredged mud, characterized by spreading on the top .
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