Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JP4528080B2 - Purification method of contaminated soil, underground structure and underground structure - Google Patents
[go: Go Back, main page]

JP4528080B2 - Purification method of contaminated soil, underground structure and underground structure - Google Patents

Purification method of contaminated soil, underground structure and underground structure Download PDF

Info

Publication number
JP4528080B2
JP4528080B2 JP2004286610A JP2004286610A JP4528080B2 JP 4528080 B2 JP4528080 B2 JP 4528080B2 JP 2004286610 A JP2004286610 A JP 2004286610A JP 2004286610 A JP2004286610 A JP 2004286610A JP 4528080 B2 JP4528080 B2 JP 4528080B2
Authority
JP
Japan
Prior art keywords
soil
contaminated soil
purification
reinforced concrete
voc
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 - Fee Related
Application number
JP2004286610A
Other languages
Japanese (ja)
Other versions
JP2006095464A (en
Inventor
康治 川上
純一 鹿浦
幸雄 加藤
重徳 石本
直美 西田
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.)
Oriental Shiraishi Corp
Original Assignee
Oriental Shiraishi Corp
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 Oriental Shiraishi Corp filed Critical Oriental Shiraishi Corp
Priority to JP2004286610A priority Critical patent/JP4528080B2/en
Publication of JP2006095464A publication Critical patent/JP2006095464A/en
Application granted granted Critical
Publication of JP4528080B2 publication Critical patent/JP4528080B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Images

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Physical Water Treatments (AREA)

Description

本発明は、ニューマチックケーソン工法を用いた汚染土壌の浄化処理方法に係り、特に、揮発性有機化合物(以下、VOCという)により汚染された土地の土壌をオンサイト(場内)で浄化すると共に、この浄化した土地に設ける構造物の基礎や地下設備等の地下構造物及び地中構造、並びに、浄化した後に埋め戻した土地の状態を調査するための観測井を構築する方法に関するものである。   The present invention relates to a method for purifying contaminated soil using a pneumatic caisson method, and in particular, purifies soil on land contaminated with a volatile organic compound (hereinafter referred to as VOC) on-site (on-site), The present invention relates to a method of constructing an observation well for investigating the underground structure and underground structure such as the foundation of the structure and the underground facilities provided in the purified land, and the state of the land that has been backfilled after the purification.

VOCによる土壌汚染は、顕在化して10年程しか経過しておらず、浄化方法として様々な新しい技術が試みられているが、主な技術としては、原位置による浄化処理と掘削除去による浄化処理に大別される。   Soil contamination due to VOC has only been revealed for about 10 years, and various new technologies have been tried as purification methods, but the main technologies are purification in-situ and purification by excavation and removal. It is divided roughly into.

原位置による浄化処理は、さらに原位置抽出と原位置分解の方法に分類される。原位置抽出方法は、土壌中の汚染物質の位置を特定し、その場所に汚染物質を抽出、浄化処理を行う設備を構築した後、土壌より汚染物質を抽出し、浄化処理を行う技術である。原位置分解方法は、事前の適正試験等で分解経路や分解生成物の挙動確認を行った後、分解生成物を土壌に注入するための設備をその場所に構築し、分解生成物を土壌に注入し浄化処理を行う技術である。   The in-situ purification process is further classified into in-situ extraction and in-situ decomposition methods. The in-situ extraction method is a technology that identifies the position of pollutants in the soil, extracts the pollutants at that location, constructs equipment to perform the purification process, and then extracts the contaminants from the soil and performs the purification process. . In-situ decomposition method, after confirming the decomposition route and the behavior of the decomposition product in the appropriate test etc. in advance, the equipment for injecting the decomposition product into the soil is built in the place, and the decomposition product is put into the soil. It is a technology for injecting and purifying.

原位置による浄化処理は、原位置抽出と原位置分解どちらの技術も上記過程により実施されるため、比較的時間を要する方法である。また、原位置による浄化処理を行った土地に構造物の基礎や地下設備を構築する場合は、浄化処理を行った後に土壌の掘削及び地下構造物の構築を実施するため、浄化処理を含めるとかなりの時間を要する方法である。   The in-situ purification process is a relatively time-consuming method because both the in-situ extraction and in-situ decomposition techniques are performed by the above process. In addition, when building foundations and underground facilities on land that has undergone in-situ purification processing, soil purification is included in order to excavate soil and build underground structures after purification processing. This is a time consuming method.

また、掘削除去による浄化処理方法は、汚染土壌を掘削し、掘削した土壌に熱を加えるなどして汚染物質を除去する技術である。掘削除去により浄化する土地に構造物の基礎や地下設備を構築する場合は、汚染土壌の除去、地下構造物の構築、汚染土壌の浄化、浄化した土壌の埋め戻しの工程を経て実施するため、比較的時間を要する技術といえる。また、掘削した汚染土壌の浄化はオンサイト(場内)で実施する場合とオフサイト(場外)で実施する場合に大別される。オンサイト(場内)で実施する場合は、浄化処理設備、掘削した汚染土壌及び浄化した土壌を仮置きするスペースを確保する必要があり、狭い土地での施工は困難になる。オフサイト(場外)で浄化処理を行う場合は、汚染土壌の受け入れ先が少なく、受け入れ先によっては処理費用が増大する。また、運搬経路において汚染物質の拡散が懸念されるといった問題が存在する。なお、この種の従来技術としては、特許文献1がある。
特開2003−103244
The purification treatment method by excavation and removal is a technique for excavating contaminated soil and removing the contaminants by applying heat to the excavated soil. When constructing foundations and underground facilities for land to be purified by excavation and removal, it is carried out through the steps of removing contaminated soil, constructing underground structures, purifying contaminated soil, and backfilling purified soil. This is a relatively time-consuming technology. In addition, purification of excavated contaminated soil is broadly divided into cases where it is performed on-site (in the field) and cases where it is performed off-site (outside the field). When it is carried out on-site (on site), it is necessary to secure a space for temporarily storing the purification treatment equipment, excavated contaminated soil and purified soil, and it becomes difficult to perform construction in a small land. When purification treatment is performed off-site (off-site), there are few recipients of contaminated soil, and depending on the recipients, treatment costs increase. There is also a problem that there is a concern about the diffusion of pollutants in the transportation route. In addition, there exists patent document 1 as this type of prior art.
JP 2003-103244 A

本発明は、上記の問題点に鑑みて提案するもので、VOCで汚染された土壌の浄化処理にニューマチックケーソン工法を採用することで、従来の技術よりも短期間で施工することが可能となる浄化処理方法及び、汚染物質の浄化処理をオンサイト(場内)によりコンパクトな設備で実施することが可能となる方法を提供するものであり、特に、VOCで汚染された土壌の浄化処理と同時に、同じ土地に構造物の基礎や地下設備を構築する場合において、従来の技術よりも短期間での施工と処理設備のコンパクト化を可能とすることを目的とする。
The present invention is proposed in view of the above-mentioned problems. By adopting the pneumatic caisson method for the purification treatment of soil contaminated with VOC, it is possible to perform construction in a shorter period of time than conventional techniques. And a method capable of carrying out the purification treatment of pollutants on-site (on site) with compact equipment, and in particular, simultaneously with the purification treatment of soil contaminated with VOC In the case of constructing the foundations of structures and underground facilities on the same land, the purpose is to enable construction and compact processing facilities in a shorter period of time than conventional techniques.

上記の目的を達成するため本発明は、次のように構成する。   In order to achieve the above object, the present invention is configured as follows.

第1の発明に係る汚染土壌の浄化処理方法は、VOCに汚染された土壌の掘削方法としてニューマチックケーソン工法を用い、作業室天井の外周に周壁部を設けその下端に刃口金物を具備してなる作業室形成用の鉄筋コンクリート躯体(ケーソン躯体)の作業室内に地上からの遠隔操作が可能な掘削機を配備し、この掘削機によりケーソン下の汚染土壌を掘削し撹拌して空気に曝すことによりVOCを土壌より放出し、放出されたVOC汚染気体と汚染水を地上に設置した浄化処理設備に導き浄化処理すると共に、VOCを放出した掘削土をケーソン躯体の沈下に伴って作業室天井の上側に排土することを特徴とする。 Purification treatment method contaminated soil according to the first invention, using a pneumatic caisson method as drilling methods the soil contaminated with VOC, comprises a working chamber ceiling plate blade die was at its lower end provided with a peripheral wall portion on the outer periphery of the An excavator that can be remotely controlled from the ground is installed in the work room of the reinforced concrete frame (caisson frame) for forming the work chamber, and the excavator excavates the contaminated soil under the caisson and exposes it to the air. The VOC is discharged from the soil, and the discharged VOC polluted gas and the contaminated water are guided to the purification processing equipment installed on the ground and purified, and the excavated soil from which the VOC has been discharged is subsided with the caisson enclosure. It is characterized by discharging to the upper side of the board .

第2の発明は、第1の発明において、VOC汚染土壌を撹拌して空気にさらすことにより放出させたVOCを、ケーソン作業室と地上に設置した浄化設備をつなぐパイプを通じて該浄化設備に送気し、浄化処理を行うことを特徴とする。   According to a second invention, in the first invention, the VOC discharged by agitating the VOC-contaminated soil and exposing it to air is supplied to the purification equipment through a pipe connecting the caisson work room and the purification equipment installed on the ground. And performing a purification process.

第3の発明は、第1または第2の発明において、作業室内の気圧と地下水位により作用するケーソン刃口金物の刃先深さの水圧とで生じる圧力差を、作業室内の気圧が小さくなるように調整することで、作業室内部にVOCに汚染された地下水を浸水させ、水中ポンプによりケーソン作業室と地上に設置した浄化設備をつなぐパイプを通じて該浄化設備に送水し、浄化処理を行うことにより、汚染物質を散逸させることなく回収し、浄化処理することを特徴とする。 The third invention is the first or second aspect of the invention, the pressure difference generated by the cutting edge depth of water pressure caisson blade die which act by pressure and groundwater level of the working chamber, the pressure in the working chamber is reduced By adjusting as described above, groundwater contaminated with VOCs is submerged in the work chamber, and water is sent to the purification equipment through a pipe connecting the caisson work room and the purification equipment installed on the ground by a submersible pump to perform purification treatment. Thus, it is possible to collect and purify the pollutants without dissipating them.

第4の発明は、第1〜第3の何れかの発明において、浄化する土地の利用用途として、構造物の基礎や地下設備等の地下構造物を構築することが予め分かっている場合は、ケーソン下の掘削による作業室形成用のコンクリート躯体の沈設に伴いその上端に上部鉄筋コンクリート躯体を構築していくと共に、その上部鉄筋コンクリート躯体の内側に浄化した掘削土を排土することで汚染土壌の浄化処理と地下構造物の構築を並行して行うことを特徴とする。 The fourth invention, in any one of the first to third inventions, when it is known in advance that a ground structure such as a foundation of a structure or an underground facility is constructed as a use application of the land to be purified. As the concrete frame for working room formation by excavation under the caisson is set up , an upper reinforced concrete frame is constructed at the upper end of the concrete frame, and the contaminated soil is purified by discharging the purified excavated soil inside the upper reinforced concrete frame. It is characterized by parallel processing and construction of underground structures.

第5の発明は、第1〜第3の何れかの発明において、浄化した土地の利用用途が未定で土地の浄化のみのための実施においては、作業室を形成する鉄筋コンクリート躯体のみを掘削に伴い沈設し、該コンクリート躯体の沈設により作業室天井の上側に浄化した掘削土を埋め戻すことによりコンクリート躯体を沈設した後を浄化処理した土の状態とすることを特徴とする。 In the fifth invention, in any one of the first to third inventions, the use of the purified land is undecided, and in the implementation only for the purification of the land, only the reinforced concrete frame forming the working room is excavated. and sinking, characterized by a state of the soil was cleaned processes after sinking the concrete skeleton by backfilling the excavation soil was cleaned on the upper side of the working chamber ceiling plate by sinking of the concrete skeleton.

第6の発明は、第1〜第4の何れかの発明において、埋め戻された土壌の状態を定期的に調査するための観測井を、鉄筋コンクリート躯体の沈設に伴い構築していくことを特徴とする。
第7の発明は、第1〜第3んも発明及び第5の発明の何れかの汚染土壌の浄化処理方法において、埋め戻された土壌の状態を定期的に調査するための観測井を、鉄筋コンクリート躯体の沈設に伴い構築していくことを特徴とする。
A sixth invention is characterized in that, in any one of the first to fourth inventions, an observation well for periodically investigating the state of the backfilled soil is constructed along with the set-up of the reinforced concrete frame. And
The seventh invention is the purification treatment method for contaminated soil according to any one of the first to third inventions and the fifth invention, wherein an observation well for periodically investigating the state of the backfilled soil is provided. It is constructed with the construction of the reinforced concrete frame.

第8の発明は、第1〜第4及び第6何れかの発明に記載の浄化処理方法により、基礎や地下設備等の地下構造物として構築された構造物であって、作業室を形成する鉄筋コンクリート躯体の上部に上部鉄筋コンクリート躯体が連設されており、上部鉄筋コンクリート躯体内に、VOCが放出された後の掘削土が排土されていることを特徴とする。 An eighth invention is a structure constructed as an underground structure such as a foundation or an underground facility by the purification treatment method according to any one of the first to fourth and sixth inventions, and forms a work chamber. The upper reinforced concrete frame is continuously provided on the upper part of the reinforced concrete frame, and the excavated soil after the VOC is discharged is discharged into the upper reinforced concrete frame.

第9の発明は、第1〜第3及び第5、第7の何れかの発明に記載の浄化処理方法が土地の浄化のみのために実施されてなる地中構造であって、作業室を形成する鉄筋コンクリート躯体が、VOC汚染土壌の最深層まで沈設されており、前記鉄筋コンクリート躯体を沈設した後の作業室天井の上面から地上までの範囲に渡って、かつケーソン躯体の外形で囲まれる内側が、VOCが放出された後の掘削土で埋め戻されていることを特徴とする。 A ninth invention is an underground structure in which the purification treatment method according to any one of the first to third, fifth, and seventh inventions is carried out only for the purification of land, and a working chamber is provided. inner reinforced concrete skeleton to be formed is, that over a range of being sinking to the deepest layer of VOC contaminated soil from the upper surface of the working chamber ceiling plate after sinking the reinforced concrete skeleton to the ground, and is surrounded by the outer shape of the caissons skeleton Is backfilled with excavated soil after the VOC has been released.

(1)VOCに汚染された土壌を周辺への影響が無い状態で浄化することが可能となり、環境を安全に保つことができる。
(2)掘削して浄化された土壌は,ケーソン躯体内に直接排土するため、掘削土砂を仮置きするスペースを必要とせずに土壌の処理が可能である。
(3)浄化する土地に地下構造物及び観測井を構築することが予め分かっている場合は、作業室を形成する鉄筋コンクリート躯体の沈設に伴い、その上部に連続して鉄筋コンクリート製の地下構造物及び観測井を構築していくことで、従来の方法より短期間での施工が可能となる。
(1) It becomes possible to purify soil contaminated with VOCs without affecting the surroundings, and the environment can be kept safe.
(2) Since the soil excavated and purified is directly discharged into the caisson enclosure, the soil can be treated without requiring a space for temporarily placing the excavated soil.
(3) If it is known in advance that an underground structure and observation wells will be built on the land to be purified, the reinforced concrete underground structure and By constructing an observation well, construction can be completed in a shorter period of time than conventional methods.

VOCに汚染された土壌の浄化処理及び、地下設備の構築方法の実施形態1を、図1〜図4を参照して説明する。図1は、VOCに汚染された土壌4bを浄化するためのコンクリート製のケーソン躯体の沈設時の縦断面図、図2は地上のVOC浄化設備の実施形態を示す側面図、図3は、ケーソン躯体の沈設後のケーソン沈下設備を撤去する工程の縦断面図、図4は地下構造物を構築した後の縦断面図である。   Embodiment 1 of the purification process of the soil contaminated with VOC and the construction method of an underground facility is demonstrated with reference to FIGS. FIG. 1 is a vertical cross-sectional view of a concrete caisson housing for purifying soil 4b contaminated with VOCs, FIG. 2 is a side view showing an embodiment of a ground VOC purification facility, and FIG. 3 is a caisson. FIG. 4 is a longitudinal sectional view of the process of removing the caisson subsidence facility after the enclosure is installed, and FIG. 4 is a longitudinal sectional view after the construction of the underground structure.

本発明は、VOCに汚染された土壌4bの掘削及び地下構造物の構築をニューマチックケーソン工法により実施する。この方法ではまず、VOCに汚染された土壌4b上の地表面4に作業室2を形成するコンクリート躯体1bを構築する(図1ではこの躯体1bが所定の深さまで沈下した態様が示されている)。その後、VOCに汚染された土壌4bを掘削しながら作業室2を形成するコンクリート躯体1bを沈下させると共に、この作業室形成躯体1bの上端14に上部の鉄筋コンクリート躯体1cを接続することで、最終的に図1に示す鉄筋コンクリート躯体1が完成する。図1において、作業室形成コンクリート躯体1bは、作業室天井15の外周に周壁部16を形成しその下端に刃口金物7を設けた構成であり、その内側に作業室2が形成される。 In the present invention, excavation of soil 4b contaminated with VOC and construction of an underground structure are performed by a pneumatic caisson method. In this method, first, a concrete casing 1b that forms the working chamber 2 is constructed on the ground surface 4 on the soil 4b contaminated with VOC (FIG. 1 shows a mode in which the casing 1b sinks to a predetermined depth. ). Then, while excavating the soil 4b contaminated with VOC, the concrete casing 1b forming the working chamber 2 is subsidized, and the upper reinforced concrete casing 1c is connected to the upper end 14 of the working chamber forming casing 1b, thereby finally The reinforced concrete frame 1 shown in FIG. 1 is completed. In Figure 1, the working chamber formed concrete skeleton 1b is a structure in which an outer peripheral wall 16 blades spinneret was 7 formed at the lower end of the working chamber ceiling plate 15, the working chamber 2 is formed inside .

作業室2内には、土壌4を掘削するための掘削機3を配備すると共に、作業室天井15の上部側には、作業室2に人用出入システム10と材料用出入室及び掘削土砂搬入用システム11が設けられている。人用出入システム10は、マンシャフト10bとマンロック10a等で構成され、作業員はこのシステム10により作業室天井15の開口部17を通して点検などのため作業室2に出入できる。材料用出入室及び掘削土砂搬入用システム11は、マテリアルシャフト11bとマテリアルロック11a等で構成され、作業室天井15の開口部18を通して掘削機3や後述のアースバケット8等の材料や掘削土砂の搬出入を行うことができる。人用出入システム10と材料用出入室及び掘削土砂搬入用システム11は通常のニューマチックケーソン工法と同じであるので詳細は省略する。 The working chamber 2, as well as deploy the excavator 3 for drilling soil 4, the working chamber on the upper side of the ceiling plate 15, a human for and out system 10 and the material for loading and unloading chamber and excavated soil into chamber 2 A carry-in system 11 is provided. People for and out system 10 is constituted by Mann shaft 10b and man lock 10a or the like, the worker can and from the working chamber 2, such as for inspection through the opening 17 of the working chamber ceiling plate 15 by the system 10. Material for loading and unloading chamber and excavated soil loading system 11 includes a material shaft 11b and material locks 11a, etc., excavator 3 and the ground bucket 8, such as below the material and excavated soil through the opening 18 of the working chamber ceiling plate 15 Can be carried in and out. The person entry / exit system 10, the material entry / exit chamber, and the excavated sediment loading / unloading system 11 are the same as the normal pneumatic caisson method, and therefore the details are omitted.

作業室2内に配備された掘削機3により作業室2下の土壌4aを掘削することにより、鉄筋コンクリート躯体1を沈設することが可能である。掘削機3は地上からの遠隔操作が可能であり、作業室2に人が入ることなく、VOCの汚染された土壌4bの掘削を行うことが可能である。掘削機3の地上からの遠隔操作については、通常のニューマチックケーソン工法と同じなので詳細は省略する。   By excavating the soil 4a under the work room 2 with the excavator 3 provided in the work room 2, the reinforced concrete frame 1 can be set down. The excavator 3 can be remotely operated from the ground, and can excavate the soil 4b contaminated with VOC without entering the work room 2. Since the remote operation from the ground of the excavator 3 is the same as the normal pneumatic caisson method, the details are omitted.

無人の作業室2内において、掘削機3により掘削したVOCに汚染された土砂は、撹拌して空気に曝すことにより、VOCを放出する。放出されたVOCは、鉄筋コンクリート躯体1を構築する際に埋設したパイプ6を通じて、地上の浄化処理設備12に送気する。パイプ6の下端は作業室天井15を貫通して作業室2内に連通しており、上端は浄化処理設備12に連通しているので、パイプ6を通して浄化処理設備12に送気されたVOCを含む気体は、図2に示すヒータ12fで加熱された後、活性炭層12cに送られ、VOCを活性炭に吸収させることにより気体を浄化する。VOCを吸引した活性炭は回収し、最終処分場で処分する。浄化された気体は、大気に放出する。 In the unmanned work chamber 2, the soil contaminated with VOC excavated by the excavator 3 is agitated and exposed to air to release VOC. The discharged VOC is sent to the ground purification treatment facility 12 through the pipe 6 embedded when the reinforced concrete frame 1 is constructed. The lower end of the pipe 6 is in communication with the working chamber 2 through the working chamber ceiling plate 15, the upper end is communicated with the cleaning process equipment 12, VOC, which is air for purification treatment facility 12 through the pipe 6 The gas containing is heated by the heater 12f shown in FIG. 2 and then sent to the activated carbon layer 12c to purify the gas by causing the activated carbon to absorb the VOC. The activated carbon that has sucked the VOC is collected and disposed of at the final disposal site. The purified gas is released into the atmosphere.

VOCを放出して浄化された土砂は、アースバケット8に積み込み、マテリアルシャフト11b及びマテリアルロック11aを通じて地上に搬出し、仮置きすることなく鉄筋コンクリート躯体1内に排土する。コンクリート躯体1内に排土された掘削土4cが、該コンクリート躯体1を立ち上がるマンシャフト10b及びマテリアルシャフト11bの周囲を埋め尽くすと、コンクリート躯体1を構築後、該マンシャフト10bとマテリアルシャフト11bを撤去できない不具合が生じる。この不具合を解消するため、本発明では、図1に示すようにマンシャフト10b及び、マテリアルシャフト11bの周辺を間隙を介して取囲んで保護管体19、20を設けている。この保護管体19、20は、コルゲートパイプなどの組立・分割自在なセグメントや、矢板などで構成される。   The soil that has been purified by discharging the VOC is loaded into the earth bucket 8, transported to the ground through the material shaft 11 b and the material lock 11 a, and discharged into the reinforced concrete frame 1 without being temporarily placed. When the excavated soil 4c discharged in the concrete frame 1 fills the man shaft 10b and the material shaft 11b rising up the concrete frame 1, the concrete shaft 1 is constructed, and then the man shaft 10b and the material shaft 11b are A defect that cannot be removed occurs. In order to eliminate this problem, in the present invention, as shown in FIG. 1, the surroundings of the man shaft 10 b and the material shaft 11 b are surrounded by a gap, and protective tube bodies 19 and 20 are provided. The protective tube bodies 19 and 20 are composed of segments that can be assembled and divided, such as corrugated pipes, and sheet piles.

また、ニューマチックケーソン工法では、地下水が作業室内に浸水するのを防ぐため、地上の送気設備9より作業室2に圧縮空気を送り作業室内の気圧を高く保っている。すなわち、地上に設置された送気設備9から導出された圧縮空気送気用パイプ9aは、第1、第2、第3の分岐パイプ9b、9c、9dに分岐されていて、分岐パイプの先端の接続部に圧縮空気を送気できる。第2、第3の分岐パイプ9c、9dは、それぞれマンロック10a、マテリアルロック11aに接続されていて各部に圧縮空気を送気できる。送気設備9から導出される圧縮空気送気用パイプ9eは、浄化処理設備の曝気槽12bに接続され、単独で曝気槽12bに圧縮空気を送気できる。   In the pneumatic caisson method, compressed air is sent from the ground air supply equipment 9 to the work chamber 2 to keep the atmospheric pressure in the work chamber high in order to prevent groundwater from entering the work chamber. That is, the compressed air supply pipe 9a led out from the air supply facility 9 installed on the ground is branched into first, second, and third branch pipes 9b, 9c, and 9d, and the tip of the branch pipe Compressed air can be sent to the connecting part. The second and third branch pipes 9c and 9d are connected to the manlock 10a and the material lock 11a, respectively, and can send compressed air to each part. The compressed air supply pipe 9e led out from the air supply facility 9 is connected to the aeration tank 12b of the purification treatment facility, and can supply compressed air to the aeration tank 12b alone.

第1分岐パイプ9bは、鉄筋コンクリート躯体1の内部を通って作業室2に連通しており、作業室2内に地下水が進入することなく掘削できるように作業室2を所定の気圧に保っている。本発明では、掘削機3によるVOCに汚染された土壌4bの掘削時において、作業室2の気圧と地下水位により作用する刃口金物7の刃口深さの水圧で生じる圧力差を、わずかに作業室2の空気圧が低くなるように調整することにより、作業室2内にVOCに汚染された地下水5を浸水させることが可能とする。これにより作業室2に浸水させたVOCに汚染された地下水5は、作業室2内に設置した水中ポンプ5aで吸引し、鉄筋コンクリート躯体1を構築の際に埋設したパイプ5bを通じて地上の浄化処理設備12に送水する。   The first branch pipe 9b communicates with the work chamber 2 through the inside of the reinforced concrete housing 1, and keeps the work chamber 2 at a predetermined pressure so that excavation can be performed without entering the work water 2 into the work chamber 2. . In the present invention, when excavating the soil 4b contaminated with VOC by the excavator 3, the pressure difference caused by the water pressure of the blade edge depth of the blade metal fitting 7 acting by the atmospheric pressure in the working chamber 2 and the groundwater level is slightly increased. By adjusting the air pressure in the work chamber 2 to be low, the ground water 5 contaminated with VOC can be immersed in the work chamber 2. As a result, the groundwater 5 contaminated by the VOC immersed in the work room 2 is sucked by the submersible pump 5a installed in the work room 2, and the ground purification treatment equipment is provided through the pipe 5b embedded when the reinforced concrete frame 1 is constructed. 12 to water.

パイプ5bを通じて 浄化処理設備12に送水されたVOCに汚染された地下水5は、図2示すように、地下水受槽12aにて土砂21などの不純物を取り除き、土砂21は堆積土砂ビット12eに集積される。また土砂21が取り除かれた汚染地下水22は水中ポンプ5aにて曝気槽12b送られ、この曝気槽12bにて空気に曝すことにより、VOCを脱気する。脱気されたVOCを含む気体はヒータ12fに導かれ、活性炭層12cにて活性炭に吸着させて浄化し、大気に放出される。また、曝気槽12bにてVOCが脱気された汚染地下水は処理水槽12dに送水され、この処理水槽12dで処理され、無害化された地下水22aは水中ポンプ5aにて公共地下水道に放流され、または、井戸23に排水して地下に戻す。   As shown in FIG. 2, the groundwater 5 contaminated with the VOC sent to the purification treatment facility 12 through the pipe 5b removes impurities such as earth and sand 21 in the underground water receiving tank 12a, and the earth and sand 21 is accumulated in the sediment earth and sand bit 12e. . The contaminated ground water 22 from which the earth and sand 21 has been removed is sent to the aeration tank 12b by the submersible pump 5a, and the VOC is degassed by exposure to air in the aeration tank 12b. The degassed gas containing VOC is guided to the heater 12f, adsorbed on the activated carbon by the activated carbon layer 12c, purified, and released to the atmosphere. In addition, the contaminated groundwater from which the VOC has been degassed in the aeration tank 12b is sent to the treated water tank 12d. The treated groundwater 22a is treated in this treated water tank 12d, and the detoxified groundwater 22a is discharged into the public underground water system by the submersible pump 5a. Or drain into the well 23 and return to the basement.

また、図1に示すように、浄化処理して埋め戻した土壌の状態を定期的に調査するための観測井13を設ける場合は、地下構造物1aの構築方法の場合と同様に、作業室2の沈下に伴い観測井13を構築していくことで、浄化処理終了と略同時に観測井13を完成することが可能となる。   Moreover, as shown in FIG. 1, when providing the observation well 13 for regularly investigating the state of the soil that has been purified and backfilled, the working room is the same as in the construction method of the underground structure 1a. By constructing the observation well 13 along with the subsidence of 2, the observation well 13 can be completed almost simultaneously with the end of the purification process.

このようにして鉄筋コンクリート躯体1をVOCで汚染された土壌層の最下層(図1に示す深さ)まで沈設した後は、この鉄筋コンクリート躯体1の沈設に要した、アースバケット8、パイプ5b、6、9a、マンシャフト10b、マンロック10a、マテリアルシャフト11b、マテリアルロック11aや掘削機3等の機材を撤去する。保護管体19、20は最後に撤去する場合と、埋め殺しにする場合とがある。図3は、保護管体19、20を残して他の機材を撤去した状態を示し、この段階で作業室2の空間と作業室天井15の開口部17、18の空間には充填コンクリート24を充填する。その後、保護管体19、20を撤去する場合は、矢板の場合は上方に引き抜き、コルゲートパイプの場合は下部のセグメントから順次解体し、解体終了後、保護管体19,20が存在していた後の空間には土砂を埋める。保護管体19、20を埋め殺し処理するときは、該管体の内部空間に補充土砂を充填する。 After the reinforced concrete frame 1 is laid down to the lowest layer of the soil layer contaminated with VOC (the depth shown in FIG. 1), the earth bucket 8 and the pipes 5b, 6 required for the laying of the reinforced concrete frame 1 are obtained. , 9a, man shaft 10b, man lock 10a, material shaft 11b, material lock 11a, excavator 3, etc. are removed. The protective tube bodies 19 and 20 may be removed last or buried. 3, leaving a protective tube 19, 20 show a state in which removal of other equipment, filling concrete 24 in the space of the opening 17, 18 of the working chamber ceiling plate 15 and the working chamber 2 of the space at this stage Fill. Then, when removing the protective tube bodies 19 and 20, in the case of a sheet pile, it pulled out upwards, in the case of a corrugated pipe, it disassembled sequentially from the lower segment, and after the completion of the disassembly, the protective tube bodies 19 and 20 existed. The back space is filled with earth and sand. When the protective pipes 19 and 20 are buried and processed, the internal space of the pipes is filled with supplementary earth and sand.

図4は、最終工程を示し、鉄筋コンクリート躯体1内に浄化処理された掘削土4cが充満した状態で観測井13が同時に埋設されおり、かつ、鉄筋コンクリート躯体1の上部開口はコンクリート蓋25で閉鎖されて構築された構造物の基礎や地下設備等の地下構造物1aが示されている。   FIG. 4 shows the final process, in which the observation well 13 is buried simultaneously with the excavated soil 4c filled in the reinforced concrete housing 1 and the upper opening of the reinforced concrete housing 1 is closed with a concrete lid 25. An underground structure 1a such as a foundation of a structure constructed in this way and an underground facility is shown.

以上の方法により、浄化を行う土地に地下構造物1aを構築する場合は、作業室2下の掘削による鉄筋コンクリート躯体1bの沈設に伴い、上部鉄筋コンクリート躯体1cを構築していくことにより土壌の浄化と地下構造物1aの構築を並行して実施することが可能となり、汚染土壌4bの除去及び浄化処理の完了と略同時に地下構造物1aを完成することが可能となる。   When the underground structure 1a is constructed on the land to be purified by the above method, the soil is purified by constructing the upper reinforced concrete frame 1c as the reinforced concrete frame 1b is dug by excavation under the work room 2. The construction of the underground structure 1a can be performed in parallel, and the underground structure 1a can be completed substantially simultaneously with the completion of the removal and purification process of the contaminated soil 4b.

図5、図6は実施形態2を示す。VOC汚染土壌を浄化処理した後の土地の利用用途決まっておらず、VOCによる汚染土壌の浄化のみを目的とする場合は、図5、図6に示すように作業室2を形成する鉄筋コンクリート躯体1bを構築し、実施形態1と同じ掘削方法で作業室2下の土壌4aを掘削することにより該鉄筋コンクリート躯体1bを沈設する。すなわち、鉄筋コンクリート躯体1bの構築以降は、実施形態1の上部鉄筋コンクリート躯体1cに相当する躯体の構築は行わず、鉄筋コンクリート躯体1bを沈設しつつ、その作業室天井15の上面から地表面4までの範囲に渡って、かつ鉄筋コンクリート躯体1bの外形で囲まれる内側にVOCが放出された後の掘削土砂4cを埋め戻すことにより、沈設した鉄筋コンクリート躯体(ケーソン躯体)1bの上部の土壌の浄化を行って元の状態に戻すことが可能となる。図には浄化処理を実施した後の最終態様を示している。 5 and 6 show the second embodiment. When the purpose of use of the land after purifying the VOC-contaminated soil is not decided and only for the purpose of purifying the contaminated soil by the VOC, the reinforced concrete frame 1b forming the work chamber 2 as shown in FIGS. Is constructed, and the reinforced concrete frame 1b is sunk by excavating the soil 4a under the working chamber 2 by the same excavation method as in the first embodiment. That is, since the construction of reinforced concrete building frame 1b does not perform the construction of the building frame corresponding to the upper reinforced concrete skeleton 1c embodiment 1, while sinking a reinforced concrete skeleton 1b, from the upper surface of the working chamber ceiling plate 15 to the ground surface 4 By refilling the excavated earth and sand 4c after the release of VOC into the inside surrounded by the outer shape of the reinforced concrete frame 1b over the range, the soil above the set reinforced concrete frame (caisson frame) 1b is purified. It becomes possible to return to the original state. FIG. 6 shows the final mode after performing the purification process.

実施形態2によるVOCに汚染された土壌の浄化処理時には、図5に示すように鉄筋コンクリート躯体1bの上端14の上方に、複数のセグメントからなる簡易な土留め壁26を組立てながらコンクリート躯体1bを沈設して行く。これにより周囲の土砂の壁が沈設コンクリート躯体1bの上側に崩れ落ちることがなく、VOCが放出された掘削土砂をアースバケット8でコンクリート躯体1bの上側に円滑に排土することができる。コンクリート躯体1bをVOC汚染土壌の最下層まで沈設した後は、土留め壁26は解体その他の手段で地上に引き上げる。勿論、埋め殺しにしてもよい。   At the time of purification treatment of soil contaminated with VOC according to the second embodiment, the concrete frame 1b is set up while assembling a simple earth retaining wall 26 composed of a plurality of segments above the upper end 14 of the reinforced concrete frame 1b as shown in FIG. Go. Accordingly, the surrounding earth and sand wall does not collapse to the upper side of the set-up concrete frame 1b, and the excavated earth and sand from which the VOC has been released can be smoothly discharged to the upper side of the concrete frame 1b by the earth bucket 8. After the concrete frame 1b is set to the lowest layer of the VOC-contaminated soil, the retaining wall 26 is pulled up to the ground by dismantling or other means. Of course, it may be buried.

以上のように実施形態2によると、VOC汚染土壌の浄化処理後の土地の利用、用途が未定であって汚染土壌の浄化のみを目的とする場合は、作業室2を形成する鉄筋コンクリート躯体1bのみを沈設し、その後は躯体の構築は行わずに、浄化した土壌を躯体の上に埋め戻すことにより、VOCに汚染されていた土地を浄化して元の状態に復元することが可能となる。   As described above, according to the second embodiment, when the use and use of land after purification treatment of VOC-contaminated soil is undecided and the purpose is only to purify contaminated soil, only the reinforced concrete frame 1b forming the work chamber 2 is used. Then, without constructing the enclosure, the purified soil is backfilled on the enclosure, so that the land contaminated with VOC can be purified and restored to its original state.

[作用]
本発明のニューマチックケーソン工法によるVOC汚染土壌の浄化処理方法によると、鉄筋コンクリートで構築されたケーソン躯体の最下部に設けられている作業室の空間に配備した掘削機で作業室下の汚染土壌を掘削することにより該ケーソン躯体の沈設が可能となる。また、掘削機は地上からの遠隔操作が可能であり、作業室内に人が入ることなくVOCに汚染された土壌の掘削を行うことが可能である。
[Action]
According to the method for purifying VOC-contaminated soil by the pneumatic caisson method of the present invention, the contaminated soil under the work room is removed by an excavator provided in the work room space provided at the bottom of the caisson housing constructed of reinforced concrete. The caisson housing can be set by excavating. Further, the excavator can be remotely operated from the ground, and can excavate soil contaminated with VOCs without entering a work room.

また、無人の作業室内で掘削機により掘削したVOCに汚染された土壌を撹拌して空気に曝すことによりVOCを土壌より放出し、作業室と地上の浄化処理設備をつなぐパイプを通じて浄化処理設備に送気し、浄化処理を行う。VOCを放出した掘削土はアースバケットに積み込み地上に搬出し、仮置きすることなくケーソン躯体に連設の鉄筋コンクリート躯体内または作業室を形成するケーソン躯体の上部側に排出する。   In addition, VOC is discharged from the soil by agitating the soil contaminated with VOC excavated by an excavator in an unmanned working chamber and exposing it to the air, and it becomes a purification processing facility through a pipe connecting the working chamber and the ground purification processing facility. Air is supplied and purification is performed. The excavated soil from which the VOC has been discharged is loaded into an earth bucket, transported to the ground, and discharged to the upper side of the caisson housing forming the work room or the reinforced concrete housing connected to the caisson housing without being temporarily placed.

また、作業室内の気圧を地下水位により作用するケーソン刃口金物の刃先深さの水圧とで生じる圧力差をわずかに作業室内の気圧が小さくなるように調整することで、作業室内部にVOCに汚染された地下水を浸水させ、水中ポンプにより鉄筋コンクリート躯体に埋設したパイプを通じて地上の浄化処理設備に送水し、浄化処理を行う。   In addition, by adjusting the pressure difference caused by the water pressure at the blade tip depth of the caisson blade fitting that works according to the groundwater level to slightly reduce the atmospheric pressure in the work chamber, The contaminated groundwater is submerged, and the water is sent to the ground purification facility through a pipe buried in the reinforced concrete frame by a submersible pump.

以上の方法により、浄化を行う土地に構造物の基礎や地下設備を構築することが予め分かっている場合は、作業室を形成する鉄筋コンクリート躯体(ケーソン躯体)の沈設に伴い上部に鉄筋コンクリート製の躯体を構築していくことで、汚染土壌の浄化処理と地下構造物の構築を並行して実施することが可能となり、VOCに汚染された土壌の浄化と鉄筋コンクリート製の地下構造物の構築が従来の方法より短期間で施工することが可能となる。   If it is known in advance that the foundation of the structure and underground facilities will be constructed on the land to be cleaned by the above method, the reinforced concrete frame will be placed on the upper part of the reinforced concrete frame (caisson frame) that forms the work room. As a result, it becomes possible to carry out the purification process of contaminated soil and the construction of underground structures in parallel, and the purification of soil contaminated with VOCs and the construction of underground structures made of reinforced concrete have It becomes possible to construct in a shorter time than the method.

浄化を行う土地の利用用途が未定であって汚染土壌の浄化のみを目的とする場合は、作業室形成する鉄筋コンクリート躯体のみを構築し、掘削機による作業室下の掘削に伴い前記コンクリート躯体を沈設し、その後はコンクリート躯体の構築は行わずに、浄化した土壌をコンクリート躯体の上に埋め戻すことにより、VOCに汚染されていた土地を浄化して元の状態に復元することが可能となる。   If the purpose of use of the land to be purified is undecided and the purpose is only to purify contaminated soil, only the reinforced concrete frame that forms the work room is constructed, and the concrete frame is subsidized by excavation under the work room by an excavator Then, without constructing the concrete frame, the purified soil is backfilled on the concrete frame, so that the land contaminated with VOC can be purified and restored to its original state.

浄化処理して埋め戻した土壌の状態を定期的に調査するための観測井を設ける場合は、作業室の沈設に伴い観測井を構築していくことが可能となる。
When an observation well is provided for regularly investigating the condition of the soil that has been reclaimed and backfilled, it becomes possible to construct the observation well as the work room is set up.

実施形態1を示し、VOCに汚染された土壌を浄化するためのコンクリート製のケーソン躯体の沈設時の縦断面図である。FIG. 3 is a longitudinal sectional view of the concrete caisson housing for purifying the soil contaminated with VOC according to the first embodiment. 地上のVOC浄化設備の実施形態を示す側面図である。It is a side view showing an embodiment of ground VOC purification equipment. ケーソン躯体の沈設後のケーソン沈下設備を撤去する工程の縦断面図である。It is a longitudinal cross-sectional view of the process of removing the caisson subsidence equipment after the caisson housing is installed. VOCに汚染された土壌の浄化終了と同時に地下構造物を構築した状態の縦断面図である。It is the longitudinal cross-sectional view of the state which constructed | assembled the underground structure simultaneously with completion | finish of the purification | cleaning of the soil contaminated with VOC. 実施形態2を示し、VOCに汚染された土壌を浄化するためのコンクリート製のケーソン躯体の沈設時の縦断面図である。FIG. 5 is a longitudinal cross-sectional view of a concrete caisson housing for purifying soil contaminated with VOCs according to a second embodiment. VOCに汚染された土壌の浄化終了と同時に、浄化処理された土砂をケーソン躯体の上部に埋め戻した状態の縦断面図である。It is the longitudinal cross-sectional view of the state which backfilled the earth and sand by which the purification process was carried out simultaneously with the completion | finish of purification | cleaning of the soil contaminated with VOC.

符号の説明Explanation of symbols

1 鉄筋コンクリート躯体
1a 地下構造物
1b 作業室を(形成)構成する躯体
2 作業室
3 掘削機
4 地表面
4a 掘削地盤
4b VOCに汚染された土壌
4c 浄化した掘削土
4d 撹拌した掘削土壌
5 作業室に浸水させた地下水
5a 水中ポンプ
5b VOC汚染水送水用パイプ
6 VOC汚染気体送気用パイプ
7 刃口金物
8 アースバケット
9 送気設備
10 人用出入室システム
10a マンロック
10b マテリアルロック
11 材料用出入室システム及び掘削土壌搬出用システム
12 浄化処理設備
12a 地下水槽
12b 曝気槽
12c 活性炭層
12d 処理水槽
12e 堆積土砂ピット
12f ヒーター
13 観測井
14 上端
15 作業室天井
16 周壁部
17 開口部
18 開口部
19 保護管体
20 保護管体
21 土砂
22 汚染地下水
22a 地下水
23 井戸
24 充填コンクリート
25 コンクリート蓋
26 土留め壁
DESCRIPTION OF SYMBOLS 1 Reinforced concrete frame 1a Underground structure 1b Frame which forms work room 2 Work room 3 Excavator 4 Ground surface 4a Excavated ground 4b Soil contaminated with VOC 4c Purified excavated soil 4d Stirred excavated soil 5 In work room Submerged groundwater 5a Submersible pump 5b VOC-contaminated water supply pipe 6 VOC-contaminated gas supply pipe 7 Blade fitting 8 Earth bucket 9 Air supply equipment 10 Person entrance / exit system 10a Manlock 10b Material lock 11 Material entry / exit room system and excavating soil unloading system 12 purification treatment equipment 12a underground water tank 12b aeration tank 12c charcoal layer 12d treating tank 12e sediment pits 12f heater 13 borehole 14 upper 15 working chamber ceiling plate 16 the peripheral wall portion 17 opening 18 opening 19 protection Tube 20 Protective tube 21 Sediment 22 Soil Groundwater 22a groundwater 23 wells 24 filled concrete 25 concrete lid 26 braced wall

Claims (9)

VOCに汚染された土壌の掘削方法としてニューマチックケーソン工法を用い、作業室天井の外周に周壁部を設けその下端に刃口金物を具備してなる作業室形成用の鉄筋コンクリート躯体(ケーソン躯体)の作業室内に地上からの遠隔操作が可能な掘削機を配備し、この掘削機によりケーソン下の汚染土壌を掘削し撹拌して空気に曝すことによりVOCを土壌より放出し、放出されたVOC汚染気体と汚染水を地上に設置した浄化処理設備に導き浄化処理すると共に、VOCを放出した掘削土をケーソン躯体の沈下に伴って作業室天井の上側に排土することを特徴とする汚染土壌の浄化処理方法。 Using pneumatic caisson method as drilling method of contaminated soil in VOC, working chamber ceiling plate outer circumferential peripheral wall portion provided on the reinforced concrete skeleton of the working chamber for forming consisting comprises a blade cap was at the lower end of (caisson building frame) An excavator that can be remotely operated from the ground is installed in the work room of this factory, and the excavator excavates the contaminated soil under the caisson, agitates it, and exposes it to the air to release VOC from the soil. while the purification treatment led to purification treatment facility installed gas and contaminated water on the ground, the excavated soil which emit VOC, characterized in that earth removal on the upper side of the working chamber ceiling plate with the subsidence of the caisson skeleton contaminated soil Purification treatment method. 請求項1記載の汚染土壌の浄化処理方法において、汚染土壌を撹拌して空気にさらすことにより放出させたVOCを、ケーソン作業室と地上に設置した浄化設備をつなぐパイプを通じて該浄化設備に送気し、浄化処理を行うことを特徴とする汚染土壌の浄化処理方法。   2. The method for purifying contaminated soil according to claim 1, wherein the VOC released by agitating the contaminated soil and exposing it to air is sent to the purification facility through a pipe connecting the caisson work room and the purification facility installed on the ground. And a purification treatment method for contaminated soil, wherein the purification treatment is performed. 請求項1または2記載の汚染土壌の浄化処理方法において、作業室内の気圧と地下水位により作用するケーソン刃口金物の刃先深さの水圧とで生じる圧力差を、作業室内の気圧が小さくなるように調整することで、作業室内部にVOCに汚染された地下水を浸水させ、水中ポンプによりケーソン作業室と地上に設置した浄化設備をつなぐパイプを通じて該浄化設備に送水し、浄化処理を行うことにより、汚染物質を散逸させることなく回収し、浄化処理することを特徴とする汚染土壌の浄化処理方法。 In the purification method of processing contaminated soil according to claim 1, the pressure difference generated by the cutting edge depth of water pressure caisson blade die which act by pressure and groundwater level of the working chamber, pressure in the working chamber is reduced By adjusting as described above, groundwater contaminated with VOCs is submerged in the work chamber, and water is sent to the purification equipment through a pipe connecting the caisson work room and the purification equipment installed on the ground by a submersible pump to perform purification treatment. The method for purifying contaminated soil, characterized in that the pollutant is collected without being dissipated and purified. 請求項1〜3の何れか1項に記載の汚染土壌の浄化処理方法において、浄化する土地の利用用途として、構造物の基礎や地下設備等の地下構造物を構築することが予め分かっている場合は、ケーソン下の掘削による作業室形成用のコンクリート躯体の沈設に伴いその上端に上部鉄筋コンクリート躯体を構築していくと共に、その上部鉄筋コンクリート躯体の内側に浄化した掘削土を排土することで汚染土壌の浄化処理と地下構造物の構築を並行して行うことを特徴とする汚染土壌の浄化処理方法。 In the purification treatment method of the contaminated soil according to any one of claims 1 to 3, it is known in advance that an underground structure such as a foundation of a structure or an underground facility is constructed as a use application of the land to be purified. In this case , the upper reinforced concrete frame is constructed at the upper end of the concrete frame for forming the work room by excavation under the caisson, and the purified excavated soil is discharged inside the upper reinforced concrete frame. A method for purifying contaminated soil, comprising performing soil purification treatment and construction of an underground structure in parallel. 請求項1〜3の何れか1項に記載の汚染土壌の浄化処理方法において、浄化した土地の利用用途が未定で土地の浄化のみのための実施においては、作業室を形成する鉄筋コンクリート躯体のみを掘削に伴い沈設し、該コンクリート躯体の沈設により作業室天井の上側に浄化した掘削土を埋め戻すことによりコンクリート躯体を沈設した後を浄化処理した土の状態とすることを特徴とする汚染土壌の浄化処理方法。 In the purification treatment method of the contaminated soil according to any one of claims 1 to 3, in the implementation only for the purification of land where the use of the purified land is undecided, only the reinforced concrete frame forming the work room is used. and sinking with the drilling, characterized in that the state of soil and purifying processes after sinking the concrete skeleton by backfilling the excavation soil was cleaned on the upper side of the working chamber ceiling plate by sinking of the concrete skeleton contaminated soil Purification treatment method. 請求項1〜4の何れか1項に記載の汚染土壌の浄化処理方法において、埋め戻された土壌の状態を定期的に調査するための観測井を、鉄筋コンクリート躯体の沈設に伴い構築していくことを特徴とする汚染土壌の浄化処理方法。 In the purification processing method of the contaminated soil of any one of Claims 1-4 , the observation well for investigating the state of the backfilled soil regularly is constructed with the subsidence of the reinforced concrete frame. A method for purifying contaminated soil. 請求項1〜3及び5の何れか1項に記載の汚染土壌の浄化処理方法において、埋め戻された土壌の状態を定期的に調査するための観測井を、鉄筋コンクリート躯体の沈設に伴い構築していくことを特徴とする汚染土壌の浄化処理方法。  In the purification method of the contaminated soil of any one of Claims 1-3 and 5, the observation well for investigating the state of the backfilled soil regularly is constructed with the sunk of the reinforced concrete frame. A method for purifying contaminated soil, characterized by being followed. 請求項1〜4及び請求項6の何れか1項記載の汚染土壌の浄化処理方法により、基礎や地下設備等の地下構造物として構築された構造物であって、作業室を形成する鉄筋コンクリート躯体の上部に上部鉄筋コンクリート躯体が連設されており、上部鉄筋コンクリート躯体内に、VOCが放出された後の掘削土が排土されていることを特徴とする地下構造物。   Reinforced concrete frame which is a structure constructed as an underground structure such as a foundation or an underground facility by the contaminated soil purification treatment method according to any one of claims 1 to 4 and claim 6 and forms a work room An underground structure in which an upper reinforced concrete frame is continuously connected to the upper part of the reinforced concrete, and excavated soil after VOC is discharged is discharged into the upper reinforced concrete frame. 請求項1〜3及び請求項5、の何れか1項記載の汚染土壌の浄化処理方法を土地利用未決定で、土地浄化のみのために実施した地中構造であって、作業室を形成する鉄筋コンクリート躯体が、VOC汚染土壌の最深層まで沈設されており、前記鉄筋コンクリート躯体を沈設した後の作業室天井の上面から地上までの範囲に渡って、かつケーソン躯体の外形で囲まれる内側が、VOCが放出された後の掘削土で埋め戻されていることを特徴とする地中構造。 An underground structure in which the method for purifying contaminated soil according to any one of claims 1 to 3 and claims 5 and 7 is implemented for land purification only, with no land use yet, and a work room is formed. Reinforced precursor to the are sinking to the deepest layer of VOC contaminated soil, the inner said reinforced concrete skeleton from the top surface of the working chamber ceiling plate after sinking over a range up to the ground, and is surrounded by the outer shape of the caissons skeleton An underground structure characterized by being backfilled with excavated soil after the VOC has been released.
JP2004286610A 2004-09-30 2004-09-30 Purification method of contaminated soil, underground structure and underground structure Expired - Fee Related JP4528080B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2004286610A JP4528080B2 (en) 2004-09-30 2004-09-30 Purification method of contaminated soil, underground structure and underground structure

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2004286610A JP4528080B2 (en) 2004-09-30 2004-09-30 Purification method of contaminated soil, underground structure and underground structure

Publications (2)

Publication Number Publication Date
JP2006095464A JP2006095464A (en) 2006-04-13
JP4528080B2 true JP4528080B2 (en) 2010-08-18

Family

ID=36235782

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2004286610A Expired - Fee Related JP4528080B2 (en) 2004-09-30 2004-09-30 Purification method of contaminated soil, underground structure and underground structure

Country Status (1)

Country Link
JP (1) JP4528080B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5700678B2 (en) * 2011-10-20 2015-04-15 鹿島建設株式会社 Air supply method and air supply device to work room in pneumatic caisson
CN115121598B (en) * 2022-07-12 2023-06-27 江苏交水建智能装备研究院有限公司 Prefabricated assembly pile for heat treatment of polluted soil

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6198823A (en) * 1984-10-18 1986-05-17 Shiraishi:Kk Method of preventing leak of air through cutting edge part in pneumatic caisson process
JP2000202425A (en) * 1999-01-12 2000-07-25 Ebara Corp Soil purification method
JP2004044242A (en) * 2002-07-12 2004-02-12 Toda Constr Co Ltd Caisson sinking control method and caisson structure used in the method
JP3957607B2 (en) * 2002-10-15 2007-08-15 鹿島建設株式会社 Pneumatic caisson and pneumatic caisson method

Also Published As

Publication number Publication date
JP2006095464A (en) 2006-04-13

Similar Documents

Publication Publication Date Title
JP6034121B2 (en) Construction method of underground structure
KR101109520B1 (en) Construction method of soil barrier using steel pipe pile
JP3508997B2 (en) How to clean contaminated soil
JP4528080B2 (en) Purification method of contaminated soil, underground structure and underground structure
JP5142269B2 (en) Casing installation device and buried object laying method
JP2003010832A (en) Contaminated soil purification method
Angel et al. Groundwater Control Issues in Transportation Engineering: A Short Review of Dewatering Methods and Lessons Learned.
KR100741883B1 (en) Apparatus and method for treating ground water using foamed urethane packer
KR20090115702A (en) Ground Excavation Method for Construction of Large Diameter Foundation Piles
JP2003126837A (en) How to repair contaminated soil
CN104912126A (en) Polluted-soil restoration system applicable to soft-soil foundation and restoration method
JP2006263557A (en) Excavation method for unnecessary deposits
KR100457230B1 (en) Gas discharging apparatus for waste reclaimed land, and method for manufacturing the same
JP3164196B2 (en) Impermeable wall and method of constructing the same
JP2006116373A (en) Containment method and replacement of contaminated soil, purification method and purification treatment equipment
KR101838676B1 (en) Soil remediation method by in-situ replacement of contaminated soil considering structural stability of small areas and polluted blocks adjacent to facilities
JP6138024B2 (en) Contaminated water block area generation method and apparatus
JP3684981B2 (en) Contaminated soil purification method
JP2004257173A (en) Deep well construction method
JP5441192B2 (en) Contaminated soil purification method
JP2007130602A (en) Containment method for contaminated soil and groundwater
JP2005161124A (en) Contaminated groundwater purification system and purification method
JP2011005383A (en) Contaminated soil cleaning method
CN111733890A (en) Polluted underground water blocking treatment method
JP3724967B2 (en) How to repair contaminated soil

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20070523

A711 Notification of change in applicant

Free format text: JAPANESE INTERMEDIATE CODE: A712

Effective date: 20071211

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20090119

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20100309

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20100510

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20100525

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20100604

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130611

Year of fee payment: 3

R150 Certificate of patent or registration of utility model

Ref document number: 4528080

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130611

Year of fee payment: 3

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130611

Year of fee payment: 3

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

LAPS Cancellation because of no payment of annual fees