JP3610458B2 - In-situ mixed processing method and in-situ mixed processing equipment for contaminated soil at the bottom of the water - Google Patents

In-situ mixed processing method and in-situ mixed processing equipment for contaminated soil at the bottom of the water Download PDF

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JP3610458B2
JP3610458B2 JP2002117844A JP2002117844A JP3610458B2 JP 3610458 B2 JP3610458 B2 JP 3610458B2 JP 2002117844 A JP2002117844 A JP 2002117844A JP 2002117844 A JP2002117844 A JP 2002117844A JP 3610458 B2 JP3610458 B2 JP 3610458B2
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mixing
water
casing
contaminated soil
stirring
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JP2003311297A (en
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尚史 細見
義文 藤井
博 遠藤
秀晃 中島
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Takenaka Civil Engineering and Construction Co Ltd
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Takenaka Civil Engineering and Construction Co Ltd
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Description

【0001】
【発明の属する技術分野】
この発明は、ダイオキシン類や鉛、水銀等の重金属、或いはポリ塩化ビフィニール(通例pcbと略す)等々に汚染された港湾、河川、湖沼などの水底を形成する底泥地盤を、原位置で前記の汚染物質が拡散しないように地盤安定材と攪拌混合して固化処理する原位置混合処理工法と、同工法の実施に使用する原位置混合処理装置の技術分野に属する。
【0002】
【従来の技術】
一般的に、ダイオキシン類や鉛、水銀等の重金属、或いはポリ塩化ビフィニール(pcb)等による汚染は内海や港湾部に多い。汚染された海域、河川、湖沼等におけるダイオキシン類等対策の考えは、先ず発生源対策を行い、汚染範囲の拡大を抑制することである。本来はダイオキシン類等で汚染された底泥を除去することが望ましいが、底泥の層厚は非常に薄く(通常30cm〜100cm程度、平均的には50cm程度)堆積している場合が多く、現在はこれを除去するのに適切な機械や作業船がないのが実状である。また、仮に除去したとしても、浚渫及び除去底泥の無害化に多額の費用が発生するし、最終処分する場所の確保などに困難な場合が多いのが現状である。
【0003】
従来、汚染された底泥の上に適度な層厚で砂をまき(敷砂)、所謂覆砂をして底泥を閉じ込める方法を実施することもあった。しかし、ダイオキシン類等の水中への拡散を完全には防止できない欠点がある。
一方、汚染物質が拡散しないように地盤安定材で固化処理する方法については未だ開発段階であり、技術的な完成を見ない。
【0004】
【発明が解決しようとする課題】
本発明の目的は、ダイオキシン類や重金属、或いはポリ塩化ビフィニール等々に汚染された港湾、河川、湖沼などの水底を形成する底泥地盤を、原位置で前記の汚染物質が拡散しないように地盤安定材と攪拌混合して固化処理する工法、及び同工法の実施に使用する原位置混合処理装置を提供することである。底泥のダイオキシン類等の汚染濃度が底質環境基準値以上の値である場合には、固化処理することが特に有効と考えられるからである。ダイオキシン類等に汚染されている底泥を固化処理しても、ダイオキシンの含有量が低減化される訳ではないが、ダイオキシン類等は水には溶解し難く,浮遊物質又は懸濁物質(いわゆるSS)に付着して移動、拡散すると考えられているので、底泥地盤を固化処理することでSSの発生を抑制できる。ひいてはダイオキシン類等に汚染された底泥の移動をし難くし、拡散を防止できる効果を期待できるのである。
【0006】
【課題を解決するための手段】
上述した従来技術の課題を解決するための手段として、請求項に記載した発明に係る水底の汚染土壌等の原位置混合処理工法は、
単数又は複数の攪拌混合軸を設置した原位置混合処理装置の下向きに開口する混合処理ケーシングを同ケーシング内の水を排水しながら水底の汚染土壌等に向かって下降させ、同混合処理ケーシングで汚染土壌等を乱さないように一定の深さまで仕切り、しかる後に前記攪拌混合軸を回転駆動すると共にセメント系固化材料その他のPH値の低い地盤安定材を注入し攪拌混合することにより原位置で水底の汚染土壌等を固化処理すること、その後混合処理ケーシングの中へ給水を行いつつ同混合処理ケーシングを上昇させることを特徴とする。
【0007】
請求項に記載した発明に係る水底の汚染土壌等の原位置混合処理工法は、
水底の汚染土壌等の上に所望の層厚で敷砂を行い、しかる後に単数又は複数の攪拌混合軸を設置した原位置混合処理装置の下向きに開口する混合処理ケーシングを同ケーシング内の水を排水しながら水底の汚染土壌等に向かって下降させ、混合処理ケーシングで覆砂及び汚染土壌等を乱さないように一定の深さまで仕切り、しかる後に前記攪拌混合軸を回転駆動すると共にセメント系固化材料その他のPH値の低い地盤安定材を注入し攪拌混合することにより原位置で水底の汚染土壌等を覆砂と共に固化処理すること、その後混合処理ケーシングの中へ給水を行いつつ同混合処理ケーシングを上昇させることを特徴とする。
【0008】
請求項に記載した発明は、請求項1又は2に記載した水底の汚染土壌等の原位置混合処理工法において、
混合処理ケーシング内の複数の攪拌混合軸は、水底の汚染土壌等を相互にラップ状態に攪拌混合することを特徴とする。
【0009】
請求項に記載した発明は、請求項1又は2に記載した水底の汚染土壌等の原位置混合処理工法において、
混合処理ケーシング内の単数又は複数の攪拌混合軸は、その攪拌翼における回転軸近傍の位置、及び先端位置から地盤安定材を注入することを特徴とする。
【0010】
請求項に記載した発明は、請求項又はに記載した水底の汚染土壌等の原位置混合処理工法において、
混合処理ケーシングを同ケーシング内の水を排水しながら水底の汚染土壌等に向かって下降させ、混合処理ケーシングで汚染土壌等を乱さないように一定の深さまで仕切り、更に混合処理ケーシング内の水が極力ない状態にまで排水し、極力水を巻き込まない状態で攪拌混合して固化処理することを特徴とする。
【0011】
請求項に記載した発明は、請求項1〜のいずれか一に記載した水底の汚染土壌等の原位置混合処理工法において、
水底の汚染土壌等の固化処理は、混合処理ケーシングの平面形状とその大きさを一単位として施工を進め、既処理部分と隣接する部位のケーシング側板は非使用状態に引き上げた状態のまま施工を進めることを特徴とする。
【0012】
請求項に記載した発明に係る水底の汚染土壌等の原位置混合処理装置は、
下向きに開口する混合処理ケーシングの中に単数又は複数の攪拌混合軸が設置されており、前記の攪拌混合軸を回転駆動する電動機又は油圧モータ等の原動機が前記混合処理ケーシングの外面部に設置され、攪拌混合軸とは伝動機構で連結されていること、
前記の混合処理ケーシングをほぼ水平姿勢に水面上又は陸上から吊って上昇又は下降させる手段と、水面上又は陸上から前記原動機へ動力源を供給し制御する手段、及び前記攪拌混合軸へ地盤安定材スラリーを供給する手段がそれぞれ設けられていること、
混合処理ケーシングの外面部に、同混合処理ケーシング内の水を排水し、又は混合処理ケーシング内へ水を供給する水中ポンプが設置されていること、を特徴とする。
【0014】
請求項に記載した発明は、請求項に記載した水底の汚染土壌等の原位置混合処理装置において、
混合処理ケーシングを形成する略垂直な側板は複数に分割され、各分割板毎に上下方向へのスライドが可能に設置されており、同側板のスライド駆動手段が設けられていることを特徴とする。
【0015】
【発明の実施形態】
以下に、図示した本発明の実施形態を説明する。図面は、請求項1〜に記載した発明に係る水底の汚染土壌等の原位置混合処理工法の実施に使用する、請求項7、8記載の発明に係る原位置混合処理装置の実施形態を示している。したがって、以下には先ず原位置混合処理装置の実施形態を説明し、合わせて原位置混合処理工法の実施例を逐次説明する。
【0016】
図1では、水面に浮かべた専用作業船2上のクレーンアーム3のウインチ(滑車)4の吊りワイヤー5で吊り下げた原位置混合処理装置6で固化処理する概況を示している。専用作業船2上には、地盤安定材を収容するサイロ21や、同地盤安定材をスラリー状に加工処理するスラリープラント22、その他汚染土壌等の原位置混合処理に必要とされる資材やエネルギ源、制御装置その他の設備機器類、操船室及び櫓などが一式搭載、装備されている。図1中の符号12は専用作業船2の櫓から突き出したクレーンアーム3に吊りワイヤー5で吊り下げた原位置混合処理装置6の施工位置を正確に確定するためのガイドロッド機構を示している。
【0017】
図2と図3は、上記原位置混合処理装置6の構造詳細を示している。図3は一例として垂直な攪拌混合軸60を16軸設置した多軸装置であることを示しているが、この限りではない。固化処理の層厚は、汚染土壌等の底泥1と敷砂10を合わせても、50cm〜150cmと薄いから、施工が割高とならないように多軸の混合処理装置6を使用するのが好ましい。しかし、攪拌混合軸60が1軸の装置で施工してもかまわない訳である。多軸型の装置は、技術的には攪拌混合軸60が最大で32軸程度の規模までは実施可能であろう。攪拌混合軸60の有効高さ(長さ)は、底泥1の層厚が既述したように通例30cm〜100cm程度であること、そして、底泥1以外の敷砂10や本来の水底地盤11を無駄に攪拌混合しないためには、できるだけ100cm前後に設計するのが好ましい。
この原位置混合処理装置6の主体は、水平なケーシングの上面を形成する剛強な水平フレーム61(囲い板を含む)であり、その四辺には辺毎に分割し独立した構成の側板63が各分割板毎に上下方向へのスライドが可能な構成で設置されている。前記水平フレーム61と側板63との組み合わせにより、下向きに開口したお椀形でほぼ水密的構造の混合処理ケーシング64が構成されている(請求項記載の発明)。図2中の符号66は前記の各側板63を個別に上下動させるため設置した摩擦車又はラック・ピニオン機構等によるスライド駆動手段である。
【0018】
詳しく図示することを省略したが、前記混合処理ケーシング64内には、水平フレーム61に設置した軸受に支持された攪拌混合軸60が、図3のように各々の攪拌翼60aが回転角にして約90°の位相差で一部ラップして回転する配置で下向きに設置されている。そして、水平フレーム61の上面(ケーシング外)に設置された電動機又は油圧モータの如き回転原動機62と前記の各攪拌混合軸60とは、やはり水平フレーム61を利用して設けた図示省略の歯車式或いはチェン、ベルト式等々の伝動機構により同期回転するように連結されている。回転原動機62は必要に応じて複数台が水平フレーム61上に設置される。
なお、回転原動機62に必要な油圧ホース又は電源ケーブル及び制御用ケーブル等の図示は便宜上省略した。また、専用作業船2上のスラリープラント22で製造した地盤安定材スラリーを各攪拌混合軸60へ供給するスラリーホース及び分配器などの図示も省略した。
【0019】
図2中の符号65は、水平フレーム61の上に設置された水中ポンプである。これは上記混合処理ケーシング64内の水を吸引し、パイプ65aを通じて外部へ排除したり、又は逆に前記パイプ65aを通じて吸引した外部の水を攪拌混合処理ケーシング64内へ送り込む構成で1台或いは複数台設置されている。
【0020】
次に、上記構成の原位置混合処理装置6を使用して、水底の汚染土壌等(底泥1)を固化処理する原位置混合処理工法の進め方について説明する。
述したように攪拌混合軸60を設置した原位置混合処理装置6を、例えば図1のように専用作業船2から吊り、その下向きに開口する混合処理ケーシング64を、水底の底泥1に向かって下降させてゆく(図4aも参照)。次いで図4bのように、同混合処理ケーシング64を汚染土壌等を乱さないようにゆっくりと土壌中へ進入させて、基本的には本来の水底地盤11へ到達する深さまで混合処理ケーシング64で仕切る。しかる後に各攪拌混合軸60を回転駆動すると共に専用作業船2上のスラリープラント22で製造した地盤安定材スラリーを注入して、混合処理ケーシング64内で底泥1と攪拌混合することにより、原位置で固化処理を行う。従って、固化処理に際して底泥1の汚濁が発生したり、拡散するおそれは極めて少ない。こうして十分に固化処理を行った後に、図4cのように原位置混合処理装置6を引き上げて次の固化処理位置に向かう。
【0021】
本発明が採用した固化処理工法は、スラリー状のセメント系固化材料、或いは必要に応じてPH値の低いセメント等の地盤安定材を使用し、これを汚染土壌中へ注入し、安定材と汚染土壌を攪拌混合し、両者の化学反応などを利用して汚染物質を固化土中に封じ込める工法である。地盤安定材としては、セメント系固化材には高炉セメント、普通ポルトランドセメント、セメント系特殊固化材等を使用できる。PH値の上昇を極力抑える必要のある場合にはそうした目的に合ったセメントを使用する。
【0022】
次に、請求項に記載した発明に係る汚染土壌等の原位置混合処理工法の場合は、原位置混合処理装置6の下向きに開口する混合処理ケーシング64を水底の底泥1に向かって下降させるにあたり、水中ポンプ65を運転して同ケーシング64内の水を排水(排除)しながら下降させ、水の抵抗による原位置混合処理装置6の位置ずれや揺らぎ等を防止すると共に、混合処理ケーシング64が下降移動することによって巻き起こす水流で水底の汚染土壌等(底泥1)に乱れ、拡散が極力生じないように工夫したことを特徴とする。かくして混合処理ケーシング64で汚染土壌等を乱さないように所定の深さまで仕切った後に、各攪拌混合軸60を回転駆動すると共に地盤安定材スラリーを注入し攪拌混合することにより原位置で水底の汚染土壌等(底泥1)を固化処理する。混合処理ケーシング64で仕切った底泥部分を水が極力少ない状態にまで排水することにより、攪拌混合時に水を巻き込まず、強度が高く良質の固化処理を行うことも好ましい。
固化処理を終了した後の原位置混合処理装置6の引き上げに際しては、今度は水中ポンプ65を逆転運転して、外部の水を混合処理ケーシング64の中へ給水し、同混合処理ケーシング64を上昇させる際の水流抵抗及び水圧抵抗を可及的に軽減することも特徴とする。
【0023】
更に、請求項に記載した発明に係る汚染土壌等の原位置混合処理工法は、水底に堆積した汚染土壌(底泥1)の上に予め敷砂10を行うことが特徴である。敷砂10は既に公知であるとおり、ガット船や砂撒き船などにより砂を散布して行う。敷砂10の目的は、覆砂によって汚染土壌の汚濁、拡散を可及的に抑えること、及び既述したようにダイオキシン類等による汚染土壌の層厚が一般的に薄いので、混合処理を実施するためには敷砂10によって固化層を実質厚くして施工する必要が有るためである。即ち、攪拌混合の処理に際して攪拌翼による底泥1の巻き上げ・拡散を可及的に防止する必要がある。よって原位置混合処理装置6の攪拌混合軸60における最上位の攪拌翼60aは、敷砂10の最下層を一部分だけ攪拌混合するように施工条件を設定するのが好ましい。そのため底泥1の層厚が通常30cm〜100cm、平均的には50cm程度の堆積であるのに対して敷砂10は数10cm程度にできるだけ薄層に散布する。シルト7のみの固化体よりも、敷砂10が存在することによる砂混じりの固化体の方が一般的にはるかに高強度なものとなり、処理後の底泥1の強度を高められることは公知である。
【0024】
請求項記載の発明は、上記のように水底の汚染土壌等の上に所望の層厚で敷砂10を行った後に、上記請求項の発明と同様、原位置混合処理装置6の下向きに開口する混合処理ケーシング64を、水中ポンプ65で同ケーシング64内の水を排水しながら水底の汚染土壌等に向かって下降させてゆき、混合処理ケーシング64で敷砂10及びその下の底泥1を乱さないように一定の深さまで仕切る。しかる後に混合処理ケーシング64内の攪拌混合軸60を回転駆動すると共に地盤安定材スラリーを注入して攪拌混合することにより、原位置で水底の汚染土壌等(底泥1)を一部の敷砂10と共に固化処理する。その後、原位置混合処理装置6の引き上げに際しては、水中ポンプ65を逆転運転して、混合処理ケーシング64の中へ外部の水を供給して上昇させることは、上記請求項記載の発明と同様である。
【0025】
ところで、本発明が目的とする、ダイオキシン類等による汚染土壌の原位置混合処理で大事なことは、未処理部分(未固化部分)を残してはならないのであり、底泥1は全面を固化処理する必要がある。そのため多軸の攪拌混合軸60は、図3で説明したように、各々の攪拌翼60aが一部ラップして回転する構成とされている(請求項に記載した発明)。
しかし、図3と図5に例示したように、最外周位置の攪拌混合軸60の攪拌翼60aの外周とケーシング側板63の内面との隙間S1、および隣り合う攪拌混合軸60の相互間において攪拌翼60aが届かない隙間S2は、それぞれ物理的、機械的に必ず発生して未処理部分となり易い。この問題を解決する手段として、本発明では、図5に示したように、混合処理ケーシング64内の攪拌混合軸60は、その攪拌翼60aにおける回転軸近傍の位置に地盤安定材スラリーを注入する軸寄り側注入部60bを設け、先端位置から地盤安定材スラリーを注入する先端注入部60cも設けている。そして、先端注入部60cからの強力なスラリー噴流Qにより、攪拌翼60aが届かない部分についても全面固化処理の実効を奏する構成としている(請求項に記載した発明)。これによって実質の未処理部分の発生が防止されている。
【0026】
次に、上記請求項又はに記載した発明のように、水中ポンプ65の運転を前提とする場合の有効活用の一案として、水底の汚染土壌等の固化処理に際し、混合処理ケーシング64を同ケーシング64内の水を排水しながら水底の汚染土壌等に向かって下降させ、混合処理ケーシング64で汚染土壌等を乱さないように一定の深さまで仕切った上で、更に混合処理ケーシング64内の水が極力ない状態にまで排水を続行し、極力水を巻き込まない状態で攪拌混合の固化処理を行うことが好ましい(請求項に記載した発明)。
【0027】
次に、図2及び図3に例示したような構成の原位置混合処理装置6を使用して原位置混合処理を行う工法は、言うなれば、混合処理ケーシング64で密閉して行うバッチ方式の固化処理工法である。必然的に、水底の汚染土壌等を固化処理する原位置混合処理は、混合処理ケーシング64の平面形状とその大きさを一単位として施工を進めることになる。一例として、図3に示す16軸型装置の場合は、一辺の長さが4m程度の正方形を一単位とするバッチ方式の施工を進めることになる。
【0028】
そうした施工の進捗状況を示したのが図6である。符号1、2、3、4の順で施工を進める。2列目のn+1が現在施工中であるが、この場合、ハッチングで示す既処理部分と隣接する部位のケーシング側板は、非使用状態に引き上げた状態のままとし、他の2辺のケーシング側板63、63のみを使用して施工を進めることになる(請求項に記載した発明)。既処理部分は既に固化が進行しているし、そこへケーシング側板を無理矢理介在させると、固化体相互の実質的なラップ施工(一体化施工)ができないからである。その意味で、例えば図2に示した側板63のスライド駆動手段66の存在意義が大きいのである。
【0029】
次に図7は、参考的に作業台船70の上にクローラクレーン71を乗り込ませてワイヤー73で原位置混合処理装置6を吊り、水底の汚染土壌等の原位置混合処理を実施する形態を示している。作業台船70上に汚染土壌等の原位置混合処理に必要な材料やプラント類、その他の設備機器を積み込むことは、図1の実施形態と同じである。
【0030】
従って、敢えて図示することは省略したが、岸辺の近辺での原位置混合処理を実施する場合には、陸上のクローラクレーン等で原位置混合処理装置6を吊り、水底の汚染土壌等の原位置混合処理を実施することもできる。
【0031】
最後に図8〜10は、水平な攪拌混合軸60による原位置混合処理装置6の実施形態を示している。図9は4軸型であることを示している。勿論、各軸の攪拌翼60aは相互に一定の位相差で回転しラップする配置とされている(図10)。各攪拌混合軸60は、水平フレーム61上の回転原動機62で同期回転される。その他の構成は図2等に示した装置と変わるところは特になく、同様な要領で使用して水底の汚染土壌等の原位置混合処理が行われる。
【0032】
【発明の効果】
請求項7、8に記載した発明に係る原位置混合処理装置を使用して、請求項1〜に記載した発明のように水底の汚染土壌等の原位置混合処理が行われるから、汚染された底泥は原位置で有害物質を封じ込める条件下で固化処理され、汚染物質による懸濁、拡散の心配がない。勿論、固化処理後は水域に汚染物質が溶出したり、拡散する二次汚染を確実に防止できる。固化体は劣化することがなく長期的に安定しているからである。
【0033】
本発明によれば、比較的に薄層の底泥を広範囲に大量に能率良く短期間に処理できるから、トータルコストを安価にできる。
【図面の簡単な説明】
【図1】本発明による水底の汚染土壌等の原位置混合処理工法の実施形態を示した立面図である。
【図2】原位置混合処理装置を示す立面図である。
【図3】原位置混合処理装置の底面図である。
【図4】a〜cは原位置混合処理工法の枢要な工程を示した説明図である。
【図5】原位置混合処理の説明図である。
【図6】原位置混合処理工法の進捗説明図である。
【図7】本発明による水底の汚染土壌等の原位置混合処理工法の異なる実施形態を示した立面図である。
【図8】原位置混合処理装置の異なる実施形態を示す立面図である。
【図9】上記原位置混合処理装置の底面図である。
【図10】上記原位置混合処理装置の側面図である。
【符号の説明】
60 混合攪拌軸
6 原位置混合処理装置
64 混合処理ケーシング
1 汚染土壌(底泥)
65 水中ポンプ
10 敷砂
60a 攪拌翼
66 スライド駆動手段
5 吊りワイヤー
[0001]
BACKGROUND OF THE INVENTION
In the present invention, the bottom mud ground forming the bottom of a harbor, river, lake, etc. contaminated with dioxins, heavy metals such as lead and mercury, polychlorinated bifinyl (usually abbreviated as pcb), etc. It belongs to the technical field of in-situ mixing processing method that stirs and mixes with the ground stabilizer so that the pollutants do not diffuse, and the in-situ mixing processing device used for the implementation of the method.
[0002]
[Prior art]
In general, contamination by dioxins, heavy metals such as lead and mercury, polychlorinated bifinyl (pcb), etc. is common in inland seas and harbors. The idea of countermeasures such as dioxins in contaminated sea areas, rivers, lakes, etc. is to first take measures against the source and suppress the expansion of the contamination range. Originally, it is desirable to remove the bottom mud contaminated with dioxins, etc., but the bottom mud layer thickness is very thin (usually about 30 cm to 100 cm, on average about 50 cm) in many cases, At present, there is no machine or work boat suitable for removing this. Moreover, even if it is removed, a large amount of money is incurred for detoxifying the dredging and removed bottom mud, and it is often difficult to secure a place for final disposal.
[0003]
Conventionally, a method of trapping the bottom mud by soaking sand with a suitable layer thickness (laying sand) on the contaminated bottom mud and so-called covering sand has been carried out. However, there is a drawback that the diffusion of dioxins and the like into water cannot be completely prevented.
On the other hand, the method of solidifying with a ground stabilizer so that the pollutants do not diffuse is still in the development stage, and no technical completion has been seen.
[0004]
[Problems to be solved by the invention]
The object of the present invention is to stabilize the ground so that the pollutants do not diffuse in situ at the bottom mud ground forming the bottom of harbors, rivers, lakes, etc. contaminated with dioxins, heavy metals, polychlorinated bifinyl, etc. It is providing the construction method which stirs and mixes with a material and solidifies, and the in-situ mixing processing apparatus used for implementation of the construction method. This is because solidification treatment is considered to be particularly effective when the concentration level of dioxins in the bottom mud is a value equal to or higher than the sediment environmental standard value. Solidification of bottom mud contaminated with dioxins, etc. does not reduce the dioxin content, but dioxins are difficult to dissolve in water. Since it is thought that it moves and diffuses by adhering to (SS), the occurrence of SS can be suppressed by solidifying the bottom mud ground. As a result, it is difficult to move the bottom mud contaminated with dioxins and the like, and an effect of preventing diffusion can be expected.
[0006]
[Means for Solving the Problems]
As a means for solving the above-described problems of the prior art, an in-situ mixing treatment method such as water-bottom contaminated soil according to the invention described in claim 1 is:
The mixing treatment casing that opens downwardly in the in-situ mixing treatment equipment with one or more stirring and mixing shafts is lowered toward the contaminated soil etc. of the bottom of the water while draining the water in the casing, and contaminated with the mixing treatment casing. Partition to a certain depth so as not to disturb the soil, etc., and then rotate the stirring and mixing shaft and inject a cement-based solidified material or other ground stabilization material with a low pH value to mix and stir It is characterized by solidifying the contaminated soil and the like, and then raising the mixing treatment casing while supplying water into the mixing treatment casing.
[0007]
In-situ mixing treatment method such as contaminated soil of the bottom of the water according to the invention described in claim 2 ,
Lay the sand with a desired layer thickness on the contaminated soil at the bottom of the water, and then remove the water in the casing from the in-situ mixing processing unit that opens downwardly in the in-situ mixing processing unit equipped with one or more stirring and mixing shafts. While draining, it descends toward the contaminated soil at the bottom of the water and partitions it to a certain depth so as not to disturb the covered sand and contaminated soil with a mixing treatment casing. After that, the stirring and mixing shaft is driven to rotate and the cement-based solidified material. By injecting other ground stabilizers with low PH value and stirring and mixing, the contaminated soil at the bottom of the water is solidified with the covering sand, and then the mixing treatment casing is supplied while supplying water into the mixing treatment casing. It is characterized by raising.
[0008]
The invention described in claim 3 is an in-situ mixed treatment method for contaminated soil in the bottom of the water according to claim 1 or 2 ,
The plurality of agitation and mixing shafts in the mixing treatment casing are characterized by agitating and mixing the contaminated soil and the like at the bottom of the water in a lapped state.
[0009]
The invention described in claim 4 is the in-situ mixed processing method for contaminated soil in the bottom of the water according to claim 1 or 2 ,
One or a plurality of stirring and mixing shafts in the mixing treatment casing is characterized in that the ground stabilizing material is injected from the position near the rotation shaft and the tip position of the stirring blade.
[0010]
The invention described in claim 5 is the in-situ mixed treatment method for contaminated soil in the bottom of the water according to claim 1 or 2 ,
The mixed treatment casing is lowered toward the contaminated soil at the bottom of the water while draining the water in the casing, and the mixed treatment casing is partitioned to a certain depth so as not to disturb the contaminated soil. It is characterized in that it is drained to a state where it is as little as possible, and is solidified by stirring and mixing in a state that does not involve water as much as possible.
[0011]
The invention described in claim 6 is an in-situ mixing treatment method such as contaminated soil in the bottom of the water according to any one of claims 1 to 5 ,
Consolidation treatment of contaminated soil at the bottom of the water is carried out with the planar shape and size of the mixed treatment casing as one unit, and the casing side plates adjacent to the already treated part are left in the unused state. It is characterized by advancing.
[0012]
An in-situ mixing treatment apparatus for contaminated soil at the bottom of the invention according to claim 7 ,
One or a plurality of stirring and mixing shafts are installed in the mixing treatment casing that opens downward, and a motor such as an electric motor or a hydraulic motor that rotationally drives the stirring and mixing shafts is installed on the outer surface of the mixing processing casing. The stirring and mixing shaft is connected by a transmission mechanism;
Means for lifting or lowering the mixing treatment casing in a substantially horizontal position on the water surface or from the land, means for supplying and controlling a power source from the water surface or from the land to the motor, and a ground stabilizer for the stirring and mixing shaft Each means for supplying slurry is provided,
A submersible pump for draining water in the mixing treatment casing or supplying water into the mixing treatment casing is installed on an outer surface portion of the mixing treatment casing .
[0014]
The invention described in claim 8 is the in-situ mixing treatment apparatus for contaminated soil in the bottom of the water according to claim 7 ,
The substantially vertical side plate forming the mixing casing is divided into a plurality of pieces, each of the divided plates is installed so as to be slidable in the vertical direction, and a slide driving means for the same side plate is provided. .
[0015]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, illustrated embodiments of the present invention will be described. The drawings show an embodiment of the in-situ mixing processing apparatus according to the inventions according to claims 7 and 8 , which is used for carrying out the in-situ mixing processing method for contaminated soil at the bottom of the water according to the inventions described in claims 1 to 6. Show. Accordingly, first, an embodiment of the in-situ mixing processing apparatus will be described first, and examples of the in-situ mixing processing method will be sequentially described.
[0016]
FIG. 1 shows an outline of solidification processing by an in-situ mixing processing device 6 suspended by a suspension wire 5 of a winch (pulley) 4 of a crane arm 3 on a dedicated work ship 2 floating on the water surface. On the dedicated work ship 2, a silo 21 for storing a ground stabilizer, a slurry plant 22 for processing the ground stabilizer into a slurry, and other materials and energy required for in-situ mixing processing such as contaminated soil. Power source, control device and other equipment, ship maneuvering room and dredging are installed and equipped. Reference numeral 12 in FIG. 1 indicates a guide rod mechanism for accurately determining the construction position of the in-situ mixing processing apparatus 6 suspended by the suspension wire 5 on the crane arm 3 protruding from the anchor of the dedicated work ship 2. .
[0017]
2 and 3 show details of the structure of the in-situ mixing processing device 6. FIG. 3 shows, as an example, a multi-axis apparatus in which 16 vertical stirring and mixing axes 60 are installed, but this is not restrictive. The layer thickness of the solidification treatment is preferably 50 cm to 150 cm even if the bottom mud 1 such as contaminated soil and the covering sand 10 are combined, so it is preferable to use the multiaxial mixing treatment device 6 so that the construction is not expensive. . However, the stirring and mixing shaft 60 may be constructed by a single-shaft device. Technically, the multi-shaft type apparatus can be implemented up to a scale of about 32 shafts with the stirring and mixing shaft 60 at the maximum. The effective height (length) of the stirring and mixing shaft 60 is that the layer thickness of the bottom mud 1 is usually about 30 cm to 100 cm as described above, and the sand 10 other than the bottom mud 1 and the original bottom ground In order not to stir and mix 11 unnecessarily, it is preferable to design it as about 100 cm as possible.
The main component of the in-situ mixing processing apparatus 6 is a rigid horizontal frame 61 (including a surrounding plate) that forms the upper surface of a horizontal casing, and side plates 63 that are divided and divided into four sides are independent. Each split plate is installed in a configuration that allows sliding up and down. The combination of the horizontal frame 61 and the side plate 63 constitutes a mixed processing casing 64 having a bowl-shaped and substantially watertight structure that opens downward (the invention according to claim 8 ). Reference numeral 66 in FIG. 2 denotes a sliding drive means such as a friction wheel or a rack and pinion mechanism installed to move the side plates 63 up and down individually.
[0018]
Although not shown in detail, in the mixing treatment casing 64, the stirring and mixing shaft 60 supported by the bearings installed in the horizontal frame 61 has a rotating angle of each stirring blade 60a as shown in FIG. It is installed in a downward direction with an arrangement in which it partially wraps and rotates with a phase difference of about 90 °. A rotary motor 62 such as an electric motor or a hydraulic motor installed on the upper surface (outside of the casing) of the horizontal frame 61 and each of the stirring and mixing shafts 60 is a gear type (not shown) provided using the horizontal frame 61. Alternatively, they are connected so as to rotate synchronously by a transmission mechanism such as a chain or belt type. A plurality of rotary prime movers 62 are installed on the horizontal frame 61 as necessary.
In addition, illustration of hydraulic hoses or power cables and control cables necessary for the rotary motor 62 is omitted for the sake of convenience. Further, illustration of a slurry hose and a distributor for supplying the ground stabilizer slurry produced at the slurry plant 22 on the dedicated work ship 2 to each stirring and mixing shaft 60 is also omitted.
[0019]
Reference numeral 65 in FIG. 2 is a submersible pump installed on the horizontal frame 61. This is because the water in the mixing treatment casing 64 is sucked and removed to the outside through the pipe 65a, or conversely, the external water sucked through the pipe 65a is sent into the stirring and mixing treatment casing 64, and one or more stand that has been installed.
[0020]
Next, a method of proceeding with the in-situ mixing processing method for solidifying the bottom soil contaminated soil (bottom mud 1) using the in-situ mixing processing apparatus 6 having the above configuration will be described.
Situ mixing apparatus 6 installed stirring and mixing shaft 60 as above mentioned, for example, suspended from a dedicated work ship 2 as shown in FIG. 1, the mixing process casing 64 which is open to its downward, the bottom of the water sediment 1 It is lowered (see also FIG. 4a). Next, as shown in FIG. 4b, the mixed processing casing 64 is slowly entered into the soil so as not to disturb the contaminated soil and the like, and is basically partitioned by the mixed processing casing 64 to a depth that reaches the original water bottom ground 11. . Thereafter, each agitating and mixing shaft 60 is rotationally driven, and a ground stabilizer slurry produced at the slurry plant 22 on the dedicated work ship 2 is injected and agitated and mixed with the bottom mud 1 in the mixing treatment casing 64, whereby the original Solidify at the position. Therefore, there is very little possibility that the bottom mud 1 is polluted or diffused during the solidification process. After sufficiently solidifying in this way, the in-situ mixing processing device 6 is pulled up to the next solidifying position as shown in FIG. 4c.
[0021]
The solidification treatment method adopted by the present invention uses a slurry-type cement-based solidified material, or a ground stabilizing material such as cement having a low PH value as required, and injects this into the contaminated soil. This is a construction method in which the soil is stirred and mixed and the pollutants are contained in the solidified soil using the chemical reaction between the two. As the ground stabilizing material, blast furnace cement, ordinary Portland cement, cement-based special solidifying material, etc. can be used as the cement-based solidifying material. When it is necessary to suppress the increase in the PH value as much as possible, a cement suitable for such purpose is used.
[0022]
Next, in the case of the in-situ mixing processing method for contaminated soil or the like according to the invention described in claim 1 , the mixing processing casing 64 that opens downwardly in the in-situ mixing processing device 6 is lowered toward the bottom mud 1 of the water bottom. In doing so, the submersible pump 65 is operated to lower the water in the casing 64 while draining (excluding) the water, thereby preventing the displacement and fluctuation of the in-situ mixing processing device 6 due to the resistance of the water and the mixing processing casing. 64 is devised so that diffusion is not generated as much as possible due to disturbance caused by contaminated soil or the like (bottom mud 1) in the water flow caused by the downward movement of 64. Thus, after partitioning to a predetermined depth so as not to disturb the contaminated soil or the like with the mixing treatment casing 64, each of the stirring and mixing shafts 60 is driven to rotate, and the ground stabilizer slurry is injected and mixed by stirring and mixing. soil or the like (sediment 1) you solidification processing. By draining the bottom mud portion partitioned by the mixing treatment casing 64 to a state where water is as little as possible, it is also preferable to perform solidification treatment with high strength and high quality without involving water during stirring and mixing.
When the in-situ mixing processing device 6 is lifted after the solidification processing is finished, this time, the submersible pump 65 is operated in reverse to supply external water into the mixing processing casing 64, and the mixing processing casing 64 is raised. It is also characterized by reducing the water flow resistance and water pressure resistance as much as possible.
[0023]
Furthermore, the in-situ mixed processing method for contaminated soil and the like according to the invention described in claim 2 is characterized in that the sand 10 is preliminarily applied on the contaminated soil (bottom mud 1) deposited on the bottom of the water. As already known, the laying sand 10 is carried out by spraying sand with a gut ship, a sanding ship or the like. The purpose of the laying sand 10 is to suppress contamination and diffusion of contaminated soil as much as possible by covering sand, and as mentioned above, the layer thickness of contaminated soil due to dioxins is generally thin, so mixing treatment is performed This is because it is necessary to make the solidified layer substantially thick with the sand 10 for the construction. That is, it is necessary to prevent as much as possible the hoisting and spreading of the bottom mud 1 by the stirring blades during the stirring and mixing process. Therefore, it is preferable that the uppermost stirring blade 60a in the stirring and mixing shaft 60 of the in-situ mixing processing device 6 is set in a working condition so that only a part of the lowermost layer of the bed sand 10 is stirred and mixed. Therefore, while the bottom mud 1 is usually deposited with a layer thickness of 30 cm to 100 cm, on average about 50 cm, the sand 10 is spread as thin as possible to about several tens of cm. It is publicly known that the solidified body mixed with sand due to the presence of the sand 10 is much stronger than the solidified body of only the silt 7 and the strength of the bottom mud 1 after the treatment can be increased. It is.
[0024]
According to a second aspect of the invention, after the laying sand 10 in the desired layer thickness on such contaminated soil water bottom as described above, similar to the invention described in claim 1, downward situ mixing apparatus 6 The mixing treatment casing 64 opened to the bottom is lowered toward the contaminated soil or the like on the bottom of the water while draining the water in the casing 64 with the submersible pump 65, and the sand 10 and the bottom mud below the mixing treatment casing 64. Partition to a certain depth so as not to disturb 1. Thereafter, the agitation and mixing shaft 60 in the mixing treatment casing 64 is rotated and the ground stabilizer slurry is injected and agitated and mixed, so that the contaminated soil or the like (bottom mud 1) in the bottom of the water is partially laid. 10 is solidified. Thereafter, when the in-situ mixing treatment device 6 is pulled up, the submersible pump 65 is operated in reverse to supply and raise external water into the mixing treatment casing 64, as in the first aspect of the invention. It is.
[0025]
By the way, what is important in the in-situ mixing treatment of contaminated soil with dioxins, which is the object of the present invention, is to leave no untreated part (unsolidified part), and the bottom mud 1 is solidified. There is a need to. Therefore, the multi-shaft stirring and mixing shaft 60 is configured such that each of the stirring blades 60a partially wraps and rotates as described with reference to FIG. 3 (invention described in claim 3 ).
However, as illustrated in FIG. 3 and FIG. 5, the gap S <b> 1 between the outer periphery of the stirring blade 60 a of the stirring and mixing shaft 60 at the outermost peripheral position and the inner surface of the casing side plate 63, and the stirring and mixing shaft 60 adjacent to each other. The gaps S2 that cannot be reached by the blades 60a are inevitably generated physically and mechanically and easily become unprocessed portions. As a means for solving this problem, in the present invention, as shown in FIG. 5, the stirring and mixing shaft 60 in the mixing treatment casing 64 injects the ground stabilizer slurry at a position near the rotating shaft of the stirring blade 60a. A shaft side injection portion 60b is provided, and a tip injection portion 60c for injecting the ground stabilizer slurry from the tip position is also provided. Further, the entire solidification process is effected even in the portion where the stirring blade 60a does not reach by the powerful slurry jet Q from the tip injection portion 60c (the invention described in claim 4 ). This prevents the occurrence of substantial unprocessed parts.
[0026]
Next, as a plan for effective use when the operation of the submersible pump 65 is premised as in the invention described in the first or second aspect , the mixing treatment casing 64 is used for solidifying the contaminated soil on the bottom of the water. The water in the casing 64 is lowered toward the contaminated soil at the bottom of the water while draining the water, and the mixed processing casing 64 is partitioned to a certain depth so as not to disturb the contaminated soil. It is preferable to continue the drainage until the water is as little as possible, and to perform the solidification treatment with stirring and mixing in the state where the water is not involved as much as possible (the invention described in claim 5 ).
[0027]
Next, the method of performing the in-situ mixing process using the in-situ mixing processing apparatus 6 having the configuration illustrated in FIG. 2 and FIG. It is a solidification processing method. Inevitably, the in-situ mixing process for solidifying contaminated soil at the bottom of the water will proceed with the planar shape of the mixing process casing 64 and its size as a unit. As an example, in the case of the 16-axis type apparatus shown in FIG. 3, the construction of the batch system is advanced with a square having a side length of about 4 m as one unit.
[0028]
FIG. 6 shows the progress of such construction. Construction is proceeded in the order of reference numerals 1, 2, 3, and 4. Although n + 1 in the second row is currently under construction, in this case, the casing side plate adjacent to the already-processed portion indicated by hatching is left in a non-use state, and the other two casing side plates 63 are disposed. , 63 is used to proceed with the construction (the invention described in claim 6 ). This is because the already processed portion has already been solidified, and if the casing side plate is forcibly interposed there, a substantial lap construction (integrated construction) between the solidified bodies cannot be performed. In this sense, for example, the existence significance of the slide driving means 66 of the side plate 63 shown in FIG. 2 is significant.
[0029]
Next, FIG. 7 shows a mode in which a crawler crane 71 is placed on a work table ship 70 for reference and the in-situ mixing processing device 6 is suspended by a wire 73 to perform in-situ mixing processing such as contaminated soil on the bottom of the water. Show. The loading of materials, plants, and other equipment necessary for in-situ mixing processing such as contaminated soil on the work table ship 70 is the same as in the embodiment of FIG.
[0030]
Therefore, although not shown in the figure, when the in-situ mixing process in the vicinity of the shore is performed, the in-situ mixing processing device 6 is hung by a land crawler crane or the like, and the in-situ position such as contaminated soil on the bottom of the water A mixing process can also be carried out.
[0031]
Finally, FIGS. 8 to 10 show an embodiment of the in-situ mixing apparatus 6 with a horizontal stirring and mixing shaft 60. FIG. 9 shows a four-axis type. Of course, the stirring blades 60a of the respective axes are arranged so as to rotate and wrap with a constant phase difference (FIG. 10). Each stirring and mixing shaft 60 is synchronously rotated by a rotary prime mover 62 on a horizontal frame 61. The other configurations are not particularly different from the apparatus shown in FIG. 2 and the like, and are used in the same manner to perform in-situ mixing processing such as contaminated soil on the bottom of the water.
[0032]
【The invention's effect】
Since the in-situ mixing treatment apparatus according to the inventions described in claims 7 and 8 is used to perform in-situ mixing processing such as contaminated soil on the bottom of the water as in the inventions described in claims 1 to 6 , Sediment mud is solidified under the conditions to contain harmful substances in-situ, and there is no concern about suspension or diffusion due to pollutants. Of course, after the solidification treatment, it is possible to reliably prevent the secondary contamination that the pollutant is eluted or diffused in the water area. This is because the solidified body does not deteriorate and is stable in the long term.
[0033]
According to the present invention, a relatively thin bottom mud can be processed in a large amount and efficiently in a short period of time, so that the total cost can be reduced.
[Brief description of the drawings]
FIG. 1 is an elevational view showing an embodiment of an in-situ mixed treatment method for contaminated soil at the bottom of the water according to the present invention.
FIG. 2 is an elevation view showing the in-situ mixing processing apparatus.
FIG. 3 is a bottom view of the in-situ mixing processing apparatus.
FIGS. 4A to 4C are explanatory views showing the main steps of the in-situ mixing treatment method.
FIG. 5 is an explanatory diagram of in-situ mixing processing.
FIG. 6 is a progress explanatory diagram of the in-situ mixing processing method.
FIG. 7 is an elevational view showing different embodiments of the in-situ mixed processing method for contaminated soil in the bottom of the water according to the present invention.
FIG. 8 is an elevational view showing a different embodiment of the in-situ mixing processing apparatus.
FIG. 9 is a bottom view of the in-situ mixing processing apparatus.
FIG. 10 is a side view of the in-situ mixing processing apparatus.
[Explanation of symbols]
60 Mixing stirring shaft 6 In-situ mixing processing device 64 Mixing processing casing 1 Contaminated soil (bottom mud)
65 Submersible pump 10 Sediment sand 60a Agitation blade 66 Slide drive means 5 Hanging wire

Claims (8)

単数又は複数の攪拌混合軸を設置した原位置混合処理装置の下向きに開口する混合処理ケーシングを同ケーシング内の水を排水しながら水底の汚染土壌等に向かって下降させ、同混合処理ケーシングで汚染土壌等を乱さないように一定の深さまで仕切り、しかる後に前記攪拌混合軸を回転駆動すると共にセメント系固化材料その他のPH値の低い地盤安定材を注入し攪拌混合することにより原位置で水底の汚染土壌等を固化処理すること、その後混合処理ケーシングの中へ給水を行いつつ同混合処理ケーシングを上昇させることを特徴とする、水底の汚染土壌等の原位置混合処理工法。The mixing treatment casing, which opens downwardly in the in-situ mixing treatment device with one or more stirring and mixing shafts, is lowered toward the contaminated soil at the bottom of the water while draining the water in the casing, and contaminated with the mixing treatment casing. Partition to a certain depth so as not to disturb the soil, etc., and then rotate the stirring and mixing shaft and inject a cement-based solidified material or other ground stabilization material with a low PH value to mix and stir An in-situ mixed treatment method for contaminated soil in the bottom of the water, which solidifies the contaminated soil and then raises the mixed treatment casing while supplying water into the mixed treatment casing. 水底の汚染土壌等の上に所望の層厚で敷砂を行い、しかる後に単数又は複数の攪拌混合軸を設置した原位置混合処理装置の下向きに開口する混合処理ケーシングを同ケーシング内の水を排水しながら水底の汚染土壌等に向かって下降させ、混合処理ケーシングで覆砂及び汚染土壌等を乱さないように一定の深さまで仕切り、しかる後に前記攪拌混合軸を回転駆動すると共にセメント系固化材料その他のPH値の低い地盤安定材を注入し攪拌混合することにより原位置で水底の汚染土壌等を覆砂と共に固化処理すること、その後混合処理ケーシングの中へ給水を行いつつ同混合処理ケーシングを上昇させることを特徴とする、水底の汚染土壌等の原位置混合処理工法。Place sand with a desired layer thickness on contaminated soil, etc. at the bottom of the water, and then turn the water in the casing into a mixing treatment casing that opens downwardly in the in-situ mixing treatment device with one or more stirring and mixing shafts installed. While draining, it descends toward the contaminated soil etc. at the bottom of the water and partitions it to a certain depth so as not to disturb the covered sand and contaminated soil etc. with the mixing treatment casing, and then drives the stirring and mixing shaft and cement-based solidified material By injecting other ground stabilizers with low PH value and stirring and mixing, the contaminated soil at the bottom of the water is solidified with the covering sand, and then the mixing treatment casing is supplied while supplying water into the mixing treatment casing. An in-situ mixed treatment method for contaminated soil at the bottom of the water, characterized by raising the soil. 混合処理ケーシング内の複数の攪拌混合軸は、水底の汚染土壌等を相互にラップ状態に攪拌混合することを特徴とする、請求項1又は2に記載した水底の汚染土壌等の原位置混合処理工法。A plurality of stirring and mixing shaft of the mixing process the casing is characterized by mixing and stirring the water bottom of the contaminated soil or the like to each other in the lap state situ mixing process of water bottom or the like of the contaminated soil according to claim 1 or 2 Construction method. 混合処理ケーシング内の単数又は複数の攪拌混合軸は、その攪拌翼における回転軸近傍の位置、及び先端位置から地盤安定材を注入することを特徴とする、請求項1又は2に記載した水底の汚染土壌等の原位置混合処理工法。The bottom or bottom stirrer according to claim 1 or 2 , wherein the one or more stirring and mixing shafts in the mixing casing inject ground stabilization material from the position near the rotation shaft of the stirring blade and from the tip position. In-situ mixed processing method for contaminated soil. 混合処理ケーシングを同ケーシング内の水を排水しながら水底の汚染土壌等に向かって下降させ、混合処理ケーシングで汚染土壌等を乱さないように一定の深さまで仕切り、更に混合処理ケーシング内の水が極力ない状態にまで排水し、極力水を巻き込まない状態で攪拌混合して固化処理することを特徴とする、請求項1又は2に記載した水底の汚染土壌等の原位置混合処理工法。The mixed treatment casing is lowered toward the contaminated soil at the bottom of the water while draining the water in the casing, and the mixed treatment casing is partitioned to a certain depth so as not to disturb the contaminated soil. 3. The in-situ mixing treatment method for contaminated soil at the bottom of the water according to claim 1 or 2 , characterized by draining to the least possible state and stirring and mixing in a state in which water is not entrained as much as possible. 水底の汚染土壌等の固化処理は、混合処理ケーシングの平面形状とその大きさを一単位として施工を進め、既処理部分と隣接する部位のケーシング側板は非使用状態に引き上げた状態のまま施工を進めることを特徴とする、請求項1〜のいずれか一に記載した水底の汚染土壌等の原位置混合処理工法。Consolidation treatment of contaminated soil on the bottom of the water is carried out with the planar shape and size of the mixed treatment casing as a unit, and the casing side plate adjacent to the already treated part is left in the unused state. The in-situ mixing treatment method for contaminated soil in the bottom of the water according to any one of claims 1 to 5 , wherein the method proceeds. 下向きに開口する混合処理ケーシングの中に単数又は複数の攪拌混合軸が設置されており、前記の攪拌混合軸を回転駆動する電動機又は油圧モータ等の原動機が前記混合処理ケーシングの外面部に設置され、攪拌混合軸とは伝動機構で連結されていること、
前記の混合処理ケーシングをほぼ水平姿勢に水面上又は陸上から吊って上昇又は下降させる手段と、水面上又は陸上から前記原動機へ動力源を供給し制御する手段、及び前記攪拌混合軸へ地盤安定材スラリーを供給する手段がそれぞれ設けられていること、
混合処理ケーシングの外面部に、同混合処理ケーシング内の水を排水し、又は混合処理ケーシング内へ水を供給する水中ポンプが設置されていること、
を特徴とする、水底の汚染土壌等の原位置混合処理装置。
One or a plurality of stirring and mixing shafts are installed in a mixing treatment casing that opens downward, and a prime mover such as an electric motor or a hydraulic motor that rotationally drives the stirring and mixing shafts is installed on the outer surface of the mixing processing casing. The stirring and mixing shaft is connected by a transmission mechanism;
Means for lifting or lowering the mixing treatment casing in a substantially horizontal position on the water surface or from the land; means for supplying and controlling a power source from the water surface or from the land to the motor; and a ground stabilizer for the stirring and mixing shaft. Each means for supplying slurry is provided,
A submersible pump for draining water in the mixing treatment casing or supplying water into the mixing treatment casing is installed on the outer surface of the mixing treatment casing.
In-situ mixing treatment equipment for contaminated soil at the bottom of the water.
混合処理ケーシングを形成する略垂直な側板は複数に分割され、各分割板毎に上下方向へのスライドが可能に設置されており、同側板のスライド駆動手段が設けられていることを特徴とする、請求項に記載した水底の汚染土壌等の原位置混合処理装置。The substantially vertical side plate forming the mixed processing casing is divided into a plurality of pieces, each of the divided plates is installed so as to be slidable in the vertical direction, and slide drive means for the same side plate is provided. An in-situ mixing treatment apparatus for contaminated soil at the bottom of the water according to claim 7 .
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JP2007307498A (en) * 2006-05-19 2007-11-29 Takenaka Doboku Co Ltd Original-position mixing treatment method and original-position mixing treatment apparatus of contaminated soil of bottom of water
CN103172228A (en) * 2013-03-01 2013-06-26 同济大学 In-situ repair method of bottom mud in city watercourse

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JP2007307498A (en) * 2006-05-19 2007-11-29 Takenaka Doboku Co Ltd Original-position mixing treatment method and original-position mixing treatment apparatus of contaminated soil of bottom of water
CN103172228A (en) * 2013-03-01 2013-06-26 同济大学 In-situ repair method of bottom mud in city watercourse
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