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JP2002254062A - In situ restoration method and restoration equipment for organic contaminated soil - Google Patents

In situ restoration method and restoration equipment for organic contaminated soil

Info

Publication number
JP2002254062A
JP2002254062A JP2001055282A JP2001055282A JP2002254062A JP 2002254062 A JP2002254062 A JP 2002254062A JP 2001055282 A JP2001055282 A JP 2001055282A JP 2001055282 A JP2001055282 A JP 2001055282A JP 2002254062 A JP2002254062 A JP 2002254062A
Authority
JP
Japan
Prior art keywords
situ
contaminated soil
organic
contaminated
soil
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.)
Granted
Application number
JP2001055282A
Other languages
Japanese (ja)
Other versions
JP4671073B2 (en
Inventor
Ryuzo Tazawa
龍三 田澤
Kazuo Okamura
和夫 岡村
Masaharu Tazaki
雅晴 田崎
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.)
Shimizu Construction Co Ltd
Shimizu Corp
Original Assignee
Shimizu Construction Co Ltd
Shimizu 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 Shimizu Construction Co Ltd, Shimizu Corp filed Critical Shimizu Construction Co Ltd
Priority to JP2001055282A priority Critical patent/JP4671073B2/en
Publication of JP2002254062A publication Critical patent/JP2002254062A/en
Application granted granted Critical
Publication of JP4671073B2 publication Critical patent/JP4671073B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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  • Investigation Of Foundation Soil And Reinforcement Of Foundation Soil By Compacting Or Drainage (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

(57)【要約】 【課題】 有機物汚染土壌を浄化するに際して、エアス
パージング法を適用する時に分子量の大きな油分を含む
重油等の有機物を低分子化してエアスパージング法の適
用を容易にすることで、汚染土壌を掘削搬出することな
く原位置において廉価に浄化できる有機物汚染土壌の原
位置浄化方法と修復装置を提供する。 【解決手段】 本発明による有機物汚染土壌の原位置修
復法と修復装置は、有機物を生物処理する有機物汚染土
壌の原位置修復法において、酸化剤を注入した後にエア
スパージングすることを特徴としており、重油等の分子
量の大きな油分を含む有機物を低分子化することによっ
て生物分解を容易にしている。この際に、酸化剤を液状
にしたり、ガス状にして注入帯を区別して効率化を図っ
ている。
[PROBLEMS] To purify organic soil contaminated by reducing the molecular weight of organic substances such as heavy oil containing oil with a high molecular weight when applying the air sparging method to facilitate the application of the air sparging method. In addition, the present invention provides an in-situ purification method and a remediation device for organic-contaminated soil that can be purified in situ at low cost without excavating and transporting the contaminated soil. SOLUTION: The in-situ restoration method and the restoration apparatus of the organic matter-contaminated soil according to the present invention are characterized in that in the in-situ restoration method of the organic matter-contaminated soil for biologically treating organic matter, air sparging is performed after injecting an oxidizing agent. Biodegradation is facilitated by reducing the molecular weight of organic substances containing oils having a large molecular weight, such as heavy oil. At this time, the oxidizing agent is made liquid or gaseous so that the injection zone is distinguished for efficiency.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は、有機物汚染土壌の
原位置修復法と修復装置に関し、特に難分解性の有機物
をエアスパージングし易いように処置する有機物汚染土
壌の原位置修復法と修復装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an in-situ restoration method and a restoration apparatus for organic-contaminated soil, and more particularly to an in-situ restoration method and an restoration apparatus for organic-contaminated soil, which treats hardly decomposable organic matter so as to easily perform air sparging. About.

【0002】[0002]

【従来の技術】近年、市街地の再開発等に伴う工場跡地
等における地盤調査において、有機物に汚染されている
汚染土壌が露呈する事態が各地で起こっており、汚染土
壌の処理が社会的な問題点になっている。
2. Description of the Related Art In recent years, in soil surveys on a site of a factory due to redevelopment of an urban area, etc., contaminated soil contaminated with organic substances has been exposed in various places, and treatment of the contaminated soil is a social problem. Has become a point.

【0003】汚染された土壌の場合は、通常、掘削、搬
出した後に、洗浄・分離、熱処理等の物理化学的方法や
ランドファーミング等の生物学的方法で修復されてい
る。
[0003] In the case of contaminated soil, it is usually repaired by physicochemical methods such as washing / separation and heat treatment and biological methods such as land farming after excavation and removal.

【0004】又、汚染された地下水は、揚水後に、エア
レーションで揮散分離したり、あるいは生物処理、活性
炭等による吸着処理によって修復している。
[0004] Further, the contaminated groundwater is recovered by pumping, volatilization and separation by aeration, biological treatment, or adsorption treatment with activated carbon or the like.

【0005】そして、汚染土壌の掘削、搬出は、環境問
題を含んでいると同時にコストも嵩張ることから、土壌
を掘削したり、地下水を揚水することを無くして、原位
置で処理することも検討されている。
[0005] Excavation and unloading of contaminated soil involves not only environmental problems but also a high cost. Therefore, it is also considered to treat the soil in situ without excavating the soil or pumping groundwater. Have been.

【0006】有機物を原位置で修復する方法としては、
不飽和帯を対象とした真空抽出、バイオべンティング等
の方法があり、飽和帯を対象とする場合は、空気を飽和
帯に吹き込むことで汚染物質を揮散させながら、不飽和
帯で真空抽出するエアスパージング法も一般化してい
る。
As a method of repairing organic matter in situ,
There are methods such as vacuum extraction and bioventing for the unsaturated zone, and for the saturated zone, air is blown into the saturated zone to evaporate contaminants and vacuum extraction in the unsaturated zone. The air sparging method is also common.

【0007】エアスパージング法は、土壌を掘削するこ
となく原位置で汚染物質を除去、分解できる修復法とし
て期待されているが、分子量の大きな油分成分は揮散効
果が低く、また生物分解も非常に遅い。
[0007] The air sparging method is expected as a restoration method capable of removing and decomposing contaminants in situ without excavating soil. However, an oil component having a large molecular weight has a low volatilization effect and is very biodegradable. slow.

【0008】そのために、重油等の分子量の大きな油分
を含む有機物で汚染されている土壌を修復する場合に
は、完全に修復を完了させようとすると非常に多くの時
間を要してしまうか、場合によっては全く分解できない
こともある。
For this reason, when repairing soil contaminated with organic matter containing a high molecular weight oil such as heavy oil, it takes a very long time to complete the restoration completely. In some cases, it cannot be completely disassembled.

【0009】しかして、この様な汚染土壌を早期に処理
するためには、掘削、搬出後に、洗浄もしくは焼却処埋
をするしかなく、非常にコストのかかる浄化となってい
る。
However, in order to treat such contaminated soil at an early stage, cleaning or incineration must be performed after excavation and unloading, resulting in very costly purification.

【0010】従って、分子量の大きな難溶・難分解性の
有機物によって汚染された土壌に対しては、原位置処理
できる適切な修復法が提案されていないのが実情であ
る。
[0010] Therefore, in reality, there has not been proposed an appropriate remediation method capable of in-situ treatment of soil contaminated with a hardly soluble or hardly decomposable organic substance having a large molecular weight.

【0011】[0011]

【発明が解決しようとする課題】本発明は、以上の問題
点に鑑みてその解決を図るために提案するものであり、
有機物汚染土壌を浄化するに際して、エアスパージング
法を適用する時に重油等の分子量が大きな油分を含む有
機物を低分子化して、エアスパージング法の適用を容易
にすることで、汚染土壌を掘削搬出することなく原位置
において廉価に浄化できる有機物汚染土壌の原位置浄化
方法と修復装置を提供している。
SUMMARY OF THE INVENTION The present invention has been made in view of the above problems, and has been proposed in order to solve the problems.
Excavation and removal of contaminated soil by purifying organic matter-contaminated soil by reducing the molecular weight of organic matter containing heavy oil and other high molecular weight oils when applying the air sparging method to facilitate the application of the air sparging method. The present invention provides an in-situ purification method and a remediation device for organic-contaminated soil that can be purified in situ at a low cost.

【0012】[0012]

【課題を解決するための手段】請求項1に記載の発明で
ある有機物汚染土壌の原位置修復法は、有機物を生物処
理する有機物汚染土壌の原位置修復法において、酸化剤
を注入した後にエアスパージングすることを特徴として
おり、分子量の大きな油分を含む重油等の有機物を低分
子化することによって生物分解を容易にしている。
According to a first aspect of the present invention, there is provided an in-situ repair method for an organic substance-contaminated soil in which an organic substance is biologically treated. It is characterized by sparging and facilitates biodegradation by reducing the molecular weight of organic substances such as heavy oils containing oils having a large molecular weight.

【0013】請求項2に記載の発明である有機物汚染土
壌の原位置修復法は、請求項1に記載の有機物汚染土壌
の原位置修復法において、酸化剤を液状にして不飽和帯
に注入することを特徴としており、上記機能に加えて、
酸化剤を降下させて汚染土壌土壌への浸透を図ってい
る。
According to a second aspect of the present invention, there is provided an in-situ restoration method for organic-contaminated soil, wherein the oxidizing agent is liquidized and injected into an unsaturated zone. It is characterized by the fact that, in addition to the above functions,
The oxidant is lowered to permeate the contaminated soil.

【0014】請求項3に記載の発明である有機物汚染土
壌の原位置修復法は、請求項1又は2に記載の有機物汚
染土壌の原位置修復法において、酸化剤をガス状にして
飽和帯に注入されることを特徴としており、上記機能に
加えて、酸化剤を上昇させて汚染土壌土壌への浸透を図
っている。
According to a third aspect of the present invention, there is provided an in-situ method for repairing an organic substance-contaminated soil according to the first or second aspect, wherein the oxidizing agent is converted into a gaseous state to a saturated zone. It is characterized by being injected, and in addition to the above functions, raises the oxidizing agent to permeate the contaminated soil.

【0015】請求項4に記載の発明である有機物汚染土
壌の原位置修復法は、請求項1乃至3のいずれかに記載
の有機物汚染土壌の原位置修復法において、原位置の土
着微生物をエアスパージング時に混入することを特徴と
しており、汚染土壌中における微生物の活性化を強化し
ている。
According to a fourth aspect of the present invention, there is provided an in-situ method for repairing an organic matter-contaminated soil according to any one of the first to third aspects, wherein the in-situ indigenous microorganisms are removed by air. It is characterized by being mixed during sparging, and enhances the activation of microorganisms in contaminated soil.

【0016】本発明による有機物汚染土壌の原位置修復
装置は、有機物で汚染されている土壌の修復装置におい
て、エアスパ−ジング法による原位置修復装置を配置
し、その原位置修復装置に酸化剤の注入機を併置させ、
酸化剤の注入機を複数に分割したり、少なくとも1つの
酸化剤注入機を原位置修復装置のスパージ井戸に結合す
ることを特徴としており、汚染土壌の有機物に対する原
位置浄化を容易にして安価な浄化処理を達成している。
The in-situ repair apparatus for soil contaminated with organic matter according to the present invention is a repair apparatus for soil contaminated with organic matter, in which an in-situ repair apparatus using an air sparging method is arranged, and the in-situ repair apparatus uses an oxidizing agent. With the injection machine juxtaposed,
The oxidizer injector is divided into a plurality of parts, and at least one oxidizer injector is connected to the sparge well of the in-situ restoration apparatus, thereby facilitating in-situ purification of organic substances in contaminated soil and reducing cost. Purification processing has been achieved.

【0017】[0017]

【発明の実施の形態】本発明による有機物汚染土壌の原
位置浄化方法と修復装置は、基本的に、有機物を生物処
理する有機物汚染土壌の原位置修復法において、酸化剤
を注入した後にエアスパージングすることを特徴として
おり、重油等の分子量の大きな油分を含む有機物を低分
子化することによって生物分解を容易にして原位置浄化
を可能にしている。以下に、本発明の実施の形態を図面
に基づいて詳細に説明する。
BEST MODE FOR CARRYING OUT THE INVENTION The in-situ purification method and repair apparatus for organic-contaminated soil according to the present invention are basically used in an in-situ repair method for organic-contaminated soil for biologically treating organic matter, after injecting an oxidizing agent and air sparging. It is characterized by reducing the molecular weight of organic matter containing a high molecular weight oil such as heavy oil, thereby facilitating biodegradation and enabling in situ purification. Hereinafter, embodiments of the present invention will be described in detail with reference to the drawings.

【0018】図1は、有機物汚染されている土壌に対し
て、本発明を実施するための修復装置を示す概要図であ
る。
FIG. 1 is a schematic diagram showing a repair apparatus for carrying out the present invention for soil contaminated with organic matter.

【0019】本発明を構成している修復装置1は、石
油、石炭ガス製造に起因するベンゼン、トルエン、キシ
レン、多核芳香族、機械油等の油分のような有機汚染物
質を浄化させるために、エアスパ−ジング法の適用を基
盤にしている。
The repair apparatus 1 according to the present invention is used to purify organic contaminants such as benzene, toluene, xylene, polynuclear aromatics, and machine oils caused by production of petroleum and coal gas. It is based on the application of the air sparging method.

【0020】本実施の形態では、空気を注入するための
コンプレッサー2と、このコンプレッサー2に接続させ
て飽和帯9に達しているスパージ井戸3及び不飽和帯に
配置される抽出井戸4からの汚染水を浄化するための水
処理装置5とガス処理装置6とから修復装置1を構成し
ている。
In the present embodiment, contamination from the compressor 2 for injecting air, the sparge well 3 connected to the compressor 2 and reaching the saturated zone 9 and the extraction well 4 arranged in the unsaturated zone is described. The restoration device 1 is composed of a water treatment device 5 for purifying water and a gas treatment device 6.

【0021】本実施の形態の修復装置における浄化処理
は、基本的に空気を汚染土壌の飽和帯9に吹き込むと共
に酸化剤を不飽和帯10に注入することで、有機汚染物
質である油分を低分子化して汚染水と共に不飽和帯10
の抽出井戸4から真空抽出しており、気液分離装置15
及び吸気ブロア16を経由させることで、汚染水と汚染
空気とに分離させながらそれぞれの浄化処理を施して清
浄化を図っている。
In the purification process of the restoration apparatus of the present embodiment, basically, air is blown into the saturated zone 9 of the contaminated soil and an oxidizing agent is injected into the unsaturated zone 10, so that oil, which is an organic pollutant, is reduced. Unsaturated zone 10 with molecular contaminated water
Vacuum extraction from the extraction well 4
In addition, by passing through the intake blower 16, respective purification treatments are performed while separating them into contaminated water and contaminated air, thereby purifying them.

【0022】本発明による原位置浄化方法は、図2、3
に示す形態によって実施されるものであり、以下の工程
によって有機物汚染土壌の浄化を行なっている。
The in-situ purification method according to the present invention is shown in FIGS.
In this embodiment, the soil contaminated with organic matter is purified by the following steps.

【0023】図2は、エアスパージングを実施する前に
有機物汚染土壌に対する処理工程を示している。
FIG. 2 shows a process for treating organic contaminated soil before performing air sparging.

【0024】有機物汚染土壌に対する処理工程を実施す
るに際しては、土壌の表面にカバー14を敷設して汚染空
気が空中に発散することを防止しており、注入機7のバ
ルブ11を開放しながら、コンプレッサー2のバルブ1
3を閉鎖している。
In carrying out the treatment step for the organic-contaminated soil, a cover 14 is laid on the surface of the soil to prevent the contaminated air from escaping into the air, and while opening the valve 11 of the injector 7, Valve 1 of compressor 2
3 is closed.

【0025】しかして、注入機7には、オゾンガス、液
状酸化剤等の酸化剤が貯蔵されているので、コンプレッ
サー2からの空気が汚染土壌に注入される前に、酸化剤
がスパージ井戸3を通じて飽和帯9に注入されることに
なる。
Since the oxidizing agent such as ozone gas and liquid oxidizing agent is stored in the injector 7, the oxidizing agent passes through the sparge well 3 before the air from the compressor 2 is injected into the contaminated soil. It will be injected into the saturation zone 9.

【0026】これによって、オゾンガス、液状酸化剤等
の酸化剤を、図示のように油分が存在している飽和帯9
及び不飽和帯10に拡散することによって、土壌や地下
水中に在る分子量の大きな油分を抽出可能な低分子物質
の状態に分解している。
As a result, the oxidizing agent such as ozone gas or liquid oxidizing agent is removed from the saturated zone 9 where oil exists as shown in FIG.
And, by diffusing into the unsaturated zone 10, it decomposes into a low-molecular substance state in which oil having a large molecular weight existing in soil or groundwater can be extracted.

【0027】そして、酸化剤の注入は、汚染土壌の状況
に応じて間欠的に複数回に亘って実施されることによっ
て、空気の注入前に油分の低分子化が確実に行われる
が、状況によっては、空気の注入と同時一体的に行なう
ことによって工期の短縮を図ることも意図されることに
なる。
The injection of the oxidizing agent is intermittently performed a plurality of times according to the condition of the contaminated soil, so that the oil content can be reduced to a low molecular weight before the air is injected. In some cases, it is intended to shorten the construction period by performing the injection simultaneously with the air injection.

【0028】上記の工程においては、エアスパージング
を実施する前の処理工程を示したが、図3は、油分が低
分子化してエアスパージングの適用が効率的になるよう
に処理された後の有機物汚染土壌に対する処理工程を示
している。
In the above steps, the processing steps before the air sparging are shown. FIG. 3 shows the organic matter after the oil content is reduced to a low molecular weight and the air sparging is efficiently applied. 3 shows a treatment process for contaminated soil.

【0029】本処理工程では、注入機7のバルブ11閉
鎖して、コンプレッサー2のバルブ13を開放してお
り、エアスパージングによる処理を実施している。
In this processing step, the valve 11 of the injector 7 is closed and the valve 13 of the compressor 2 is opened, and the processing by air sparging is performed.

【0030】コンプレッサー2からの空気は、スパージ
井戸3から汚染土壌の飽和帯9に吹き込まれると共に酸
化剤が不飽和帯10に注入されていることから、油分を
低分子化しながら揮散させることで汚染水と共に不飽和
帯10の抽出井戸4から真空抽出しており、気液分離装
置15及び吸気ブロア16を経由させることで、汚染水
と汚染空気とに分離させながらそれぞれの浄化処理を施
して清浄化を図っている。
The air from the compressor 2 is blown into the saturated zone 9 of the contaminated soil from the sparge well 3 and the oxidizing agent is injected into the unsaturated zone 10, so that the oil is volatilized while being reduced in molecular weight. It is vacuum-extracted from the extraction well 4 of the unsaturated zone 10 together with water, and is passed through the gas-liquid separator 15 and the intake blower 16 to be subjected to respective purification treatments while being separated into contaminated water and contaminated air. It is trying to make it.

【0031】従って、本実施の形態では、分子量の大き
な難溶性の油分低分子化して生物分解が可能な状態に処
理することでエアスパージング処理を効率的にしてか
ら、有機物を土壌中から抽出して浄化処理しており、有
機物汚染している土壌を現位置において確実に清浄化し
ている。
Therefore, in the present embodiment, the air sparging treatment is efficiently performed by reducing the molecular weight of the hardly soluble oil having a large molecular weight to a state capable of biodegradation, and then the organic matter is extracted from the soil. The soil that has been contaminated with organic matter is surely cleaned at the current location.

【0032】そして、注入機から注入している酸化剤の
種類と濃度、注入する時期をエアスパージングによる処
理の前にするか同時にするかの選択、さらには注入を一
度にするか間欠的に複数回にするか否かについては、汚
染土壌の汚染物質、濃度レベル及び汚染の範囲等に合わ
せて適宜に調整するものであり、状況に合わせて柔軟に
対処できることから、有機物汚染された土壌の現位置処
理について幅広く対応できる。
The type and concentration of the oxidizing agent injected from the injector and the timing of the injection are selected before or simultaneously with the treatment by air sparging, and the injection is performed once or intermittently. The decision as to whether or not to recycle is appropriately adjusted in accordance with the pollutants, concentration level, range of contamination, etc. of the contaminated soil. Can handle a wide range of position processing.

【0033】又、本発明の他の実施例を図4に示してい
る。本実施の形態で示す修復装置20では、上述した実
施の形態における修復装置1に追加して不飽和帯10に
臨ませる注入機8を配置している。
FIG. 4 shows another embodiment of the present invention. In the repairing apparatus 20 shown in the present embodiment, an injector 8 that faces the unsaturated zone 10 is arranged in addition to the repairing apparatus 1 in the above-described embodiment.

【0034】注入機7は、バルブ11を介してスパージ
井戸3に接続され、注入機8は、バルブ12を介して不
飽和帯10に臨ませており、コンプレッサー2とスパー
ジ井戸3との間に設けられているバルブ13との開閉操
作によって注入抽出作業を実施している。
The injector 7 is connected to the sparge well 3 via a valve 11, and the injector 8 faces the unsaturated zone 10 via a valve 12, and is located between the compressor 2 and the sparge well 3. The injection extraction operation is performed by opening and closing the valve 13 provided.

【0035】本実施の形態の修復装置における浄化処理
は、空気を汚染土壌の飽和帯9に吹き込む前に酸化剤を
飽和帯9と不飽和帯10に注入することで、分子量の大
きな油分を低分子化してエアスパージングの実施を効率
的にしており、油分を不飽和帯10の抽出井戸4から真
空抽出し、気液分離装置15及び吸気ブロア16を経由
させることで、汚染水と汚染空気とに分離させながらそ
れぞれの浄化処理を施して清浄化を図っている。
In the purification treatment in the repairing apparatus of the present embodiment, an oxidizing agent is injected into the saturated zone 9 and the unsaturated zone 10 before air is blown into the saturated zone 9 of the contaminated soil, so that oil having a large molecular weight can be reduced. The air is sparged efficiently to carry out air sparging, and the oil is vacuum extracted from the extraction well 4 of the unsaturated zone 10 and passed through the gas-liquid separator 15 and the intake blower 16 to remove contaminated water and contaminated air. Each purification process is performed while separating them to achieve purification.

【0036】本実施の形態の原位置浄化方法は、図5、
6に示す形態によって実施されるものであり、以下の工
程によって有機物汚染土壌の浄化を行なっている。
The in-situ purification method of this embodiment is shown in FIG.
6 and the purification of the organic-contaminated soil is performed by the following steps.

【0037】図5は、エアスパージングを実施する前の
有機物汚染土壌に対する処理工程を示している。
FIG. 5 shows a process for treating organic contaminated soil before air sparging is performed.

【0038】有機物汚染土壌に対する処理工程を実施す
るに際しては、土壌の表面にカバー14を敷設して汚染空
気が空中に発散することを防止しており、注入機7、8
のバルブ11、12を開放しながら、コンプレッサー2
のバルブ13を閉鎖している。
In carrying out the treatment step for the organic-contaminated soil, a cover 14 is laid on the surface of the soil to prevent contaminated air from escaping into the air.
Compressor 2 while opening valves 11 and 12
Valve 13 is closed.

【0039】しかして、注入機7には、オゾンガス等の
気体状の酸化剤が貯蔵され、注入機8には、過酸化水素
等の液体状の酸化剤が貯蔵されているので、コンプレッ
サー2からの空気が汚染土壌に注入される前に、気体状
の酸化剤がスパージ井戸3を通じて飽和帯9に注入され
ており、液体状の酸化剤がバルブ12を通じて不飽和帯
10に注入されることになる。
The injector 7 stores a gaseous oxidant such as ozone gas, and the injector 8 stores a liquid oxidant such as hydrogen peroxide. Before the air is injected into the contaminated soil, a gaseous oxidant is injected into the saturated zone 9 through the sparge well 3 and a liquid oxidant is injected into the unsaturated zone 10 through the valve 12. Become.

【0040】これによって、気体状の酸化剤が飽和帯9
から上昇拡散すると共に液体状の酸化剤が不飽和帯10
から降下することによって、土壌や地下水中に在る分子
量の大きな有機汚染物質を抽出可能な低分子化した状態
に処理している。
As a result, the gaseous oxidizing agent is
From the unsaturated zone 10
As a result, the organic contaminants having a high molecular weight in the soil and groundwater are reduced to a low molecular weight state.

【0041】そして、酸化剤の注入は、上記実施の形態
と同様に汚染土壌の状況に応じて間欠的に複数回に亘っ
て実施されることによって、空気の注入前に有機汚染物
質の低分子化が確実に行われるが、状況によっては、空
気の注入と同時一体的に行なうことによって工期の短縮
を図ることも意図されることになる。
The injection of the oxidizing agent is carried out intermittently a plurality of times according to the condition of the contaminated soil as in the above-described embodiment, so that the low-molecular organic contaminants are injected before the air is injected. However, depending on the situation, it may be intended to shorten the construction period by performing the injection simultaneously with the air injection.

【0042】上記の工程においては、エアスパージング
を実施する前の処理工程を示したが、図6は、エアスパ
ージングの適用が効率的になるように処理された後の有
機物汚染土壌に対する処理工程を示している。
In the above steps, the processing steps before the air sparging is performed are shown. FIG. 6 shows the processing steps for the organic contaminated soil after the air sparging is processed so as to be effective. Is shown.

【0043】本処理工程では、注入機7、8のバルブ1
1、12を閉鎖して、コンプレッサー2のバルブ13を
開放しており、エアスパージングによる浄化処理を実施
している。
In this processing step, the valves 1 of the injectors 7 and 8 are used.
The valves 1 and 12 are closed, the valve 13 of the compressor 2 is opened, and a purification process by air sparging is performed.

【0044】コンプレッサー2からの空気は、スパージ
井戸3から汚染土壌の飽和帯9に吹き込まれると共に、
酸化剤が飽和帯9と不飽和帯10に注入されていること
から、生物処理された有機物が汚染水と共に不飽和帯1
0の抽出井戸4から真空抽出されており、気液分離装置
15及び吸気ブロア16を経由させることで、汚染水と
汚染空気とに分離させながらそれぞれの浄化処理を施し
て清浄化を図っている。
The air from the compressor 2 is blown from the sparge well 3 into the saturated zone 9 of the contaminated soil,
Since the oxidizing agent is injected into the saturated zone 9 and the unsaturated zone 10, the biologically treated organic matter is mixed with the contaminated water in the unsaturated zone 1.
0 is extracted in vacuum from the extraction well 4 and is passed through the gas-liquid separation device 15 and the intake blower 16 so as to be separated into contaminated water and contaminated air while being subjected to respective purification treatments to achieve purification. .

【0045】従って、本実施の形態では、酸化剤を気体
状の酸化剤と液体状の酸化剤に区別して別途に貯蔵する
ことで、その特性に合わせながら飽和帯9と不飽和帯1
0に注入しているので、有機物汚染している土壌を現位
置において確実に清浄化している。
Therefore, in the present embodiment, the oxidizing agent is separately stored as a gaseous oxidizing agent and a liquid oxidizing agent, so that the saturated zone 9 and the unsaturated zone 1 are stored in accordance with the characteristics.
Since it is injected at zero, soil contaminated with organic matter is reliably cleaned at the current position.

【0046】図7に示す他の実施の形態では、使用した
酸化剤の濃度等によって土壌中に土着している微生物の
活性が著しく損なわれたと判断される場合の対処例を示
している。
Another embodiment shown in FIG. 7 shows an example of a case where it is determined that the activity of microorganisms indigenous to soil is significantly impaired due to the concentration of the oxidizing agent used or the like.

【0047】本実施の形態で示す修復装置30では、図
1に示した実施の形態の修復装置1に酸化の影響を受け
ない箇所に抽出井戸17を設置して、土壌から地下水を
揚水している。
In the repairing apparatus 30 shown in this embodiment, an extraction well 17 is installed in a place not affected by oxidation in the repairing apparatus 1 of the embodiment shown in FIG. 1, and groundwater is pumped from soil. I have.

【0048】揚水地下水は、活性微生物を含んでいるの
でこれをスパージ井戸に注入する空気に混入させること
によって、微生物の活性が著しく損なわれたと認識され
た土壌に分解微生物を供給している。
Since the pumped groundwater contains active microorganisms, it is mixed with the air injected into the sparge well to supply decomposed microorganisms to the soil which has been recognized as having significantly impaired the activity of the microorganisms.

【0049】これによって、汚染土壌の有機物を生物処
理する効率が向上されて、工期の短縮を図ることができ
る。
As a result, the efficiency of biological treatment of the organic matter in the contaminated soil is improved, and the construction period can be shortened.

【0050】本発明による有機物汚染土壌の原位置浄化
方法と修復装置は、以上のように構成されているので、
有機物、シアン化合物及び重金属で汚染されている有機
物汚染土壌に対しても、シアン化合物及び重金属の不溶
化による固定化やシアン化合物の分解によるエアスパー
ジング処理の効率化によって、全ての汚染物質に対して
原位置修復することを可能にしている。
The in-situ purification method and the remediation device for organic-contaminated soil according to the present invention are configured as described above.
Organic contaminated soil contaminated with organic matter, cyanide and heavy metals can also be reduced by reducing the amount of all contaminants by immobilizing cyanide and heavy metals by insolubilization and increasing the efficiency of air sparging by decomposing cyanide. It is possible to repair the position.

【0051】以上、本発明による有機物汚染土壌の原位
置修復法と修復装置を、その実施の形態に基づいて詳細
に説明してきたが、本発明は上記実施の形態に何等限定
されるものでなく、有機物や酸化剤の種類等について酸
化剤を注入した後にエアスパ−ジングするという、発明
の趣旨に反しない範囲において、各種の変更が可能であ
ることは当然である。
Although the in-situ method and apparatus for repairing soil contaminated with organic matter according to the present invention have been described in detail based on the embodiments, the present invention is not limited to the above-described embodiments. Naturally, various changes can be made within a range not inconsistent with the gist of the invention, that is, air sparging is performed after injecting the oxidizing agent for the kind of the organic substance and the oxidizing agent.

【0052】[0052]

【発明の効果】請求項1に記載の発明である有機物汚染
土壌の原位置修復法は、有機物を生物処理する有機物汚
染土壌の原位置修復法において、酸化剤を注入した後に
エアスパージングすることを特徴としているので、重油
等の分子量の大きな油分を含む有機物を低分子化するこ
とによって生物分解を容易にして以下の効果を発揮して
いる。
According to the first aspect of the present invention, the in-situ restoration method for organic-contaminated soil, which is the invention for in-situ restoration of organic-substance-contaminated soil for biological treatment of organic matter, comprises injecting an oxidizing agent and then performing air sparging. Since it is a feature, the organic matter containing a high molecular weight oil such as heavy oil is reduced in molecular weight to facilitate biodegradation and exhibit the following effects.

【0053】 揮散と生物分解が困難な有機物汚染土
壌を原位置で修復できる。 掘削、洗浄、焼却等の作業・処理法と比較して、コ
ストを節約できる。 エアスパージング装置の改良で済むことから装置を
小型に構成できる。 修復装置の維持管理が容易でトラブルの発生も少な
くできる。
Organic contaminated soils that are difficult to volatilize and biodegrade can be repaired in situ. Costs can be reduced compared to work / treatment methods such as excavation, cleaning, and incineration. Since the improvement of the air sparging device is sufficient, the device can be made compact. The maintenance and management of the restoration device is easy and the occurrence of troubles can be reduced.

【0054】請求項2に記載の発明である有機物汚染土
壌の原位置修復法は、請求項1に記載の有機物汚染土壌
の原位置修復法において、酸化剤を液状にして不飽和帯
に注入することを特徴としているので、上記効果に加え
て、酸化剤を降下させて汚染土壌土壌への浸透を図れる
効果を発揮している。
According to the in-situ restoration method for organic-contaminated soil according to the second aspect of the present invention, in the in-situ restoration method for organic-contaminated soil according to the first aspect, the oxidizing agent is liquefied and injected into the unsaturated zone. Therefore, in addition to the above-mentioned effects, an effect of lowering the oxidizing agent and permeating the contaminated soil is exhibited.

【0055】請求項3に記載の発明である有機物汚染土
壌の原位置修復法は、請求項1又は2に記載の有機物汚
染土壌の原位置修復法において、酸化剤をガス状にして
飽和帯に注入されることを特徴としているので、上記効
果に加えて、酸化剤を上昇させて汚染土壌土壌への浸透
を図れる効果を発揮している。
In the in-situ repair method for organic-contaminated soil according to the third aspect of the present invention, in the in-situ repair method for organic-contaminated soil according to the first or second aspect, the oxidizing agent is gasified to form a saturated zone. Since it is characterized by being injected, in addition to the above effects, it has the effect of increasing the oxidizing agent and permeating the contaminated soil.

【0056】請求項4に記載の発明である有機物汚染土
壌の原位置修復法は、請求項1乃至3のいずれかに記載
の有機物汚染土壌の原位置修復法において、原位置の分
解微生物をエアスパージング時に混入することを特徴と
しているので、上記効果に加えて、汚染土壌中における
微生物の活性化を強化できる効果を発揮している。
According to a fourth aspect of the present invention, there is provided an in-situ method for repairing an organic matter-contaminated soil according to any one of the first to third aspects. Since it is characterized by being mixed at the time of sparging, in addition to the above effects, it has the effect of enhancing the activation of microorganisms in contaminated soil.

【0057】本発明による有機物汚染土壌の原位置修復
装置は、有機物で汚染されている土壌の修復装置におい
て、エアスパ−ジング法による原位置修復装置を配置
し、その原位置修復装置に酸化剤の注入機を併置させ、
酸化剤の注入機を複数に分割したり、少なくとも1つの
酸化剤注入機を原位置修復装置のスパージ井戸に結合す
ることを特徴としているので、汚染土壌の有機物に対す
る原位置浄化を容易にして安価な浄化処理を達成できる
効果を発揮している。
The in-situ repairing apparatus for soil contaminated with organic matter according to the present invention is a repairing apparatus for soil contaminated with organic matter, wherein the in-situ repairing apparatus is disposed by an air sparging method, and the in-situ repairing apparatus is provided with an oxidizing agent. With the injection machine juxtaposed,
Since the oxidizer injector is divided into a plurality of parts and at least one oxidizer injector is connected to the sparge well of the in-situ restoration apparatus, in-situ purification of organic substances in contaminated soil is facilitated and inexpensive. It has the effect of achieving an effective purification treatment.

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

【 図1】本発明による有機物汚染土壌の原位置浄化方
法と修復装置の概要図
FIG. 1 is a schematic diagram of an in-situ purification method and a remediation device for organic contaminated soil according to the present invention.

【 図2】本発明による有機物汚染土壌の原位置浄化方
法と修復装置におけるエアスパージング前の工程図
FIG. 2 is a process diagram before an air sparging in an in-situ purification method and a restoration apparatus for organic contaminated soil according to the present invention.

【 図3】本発明による有機物汚染土壌の原位置浄化方
法と修復装置におけるエアスパージング工程図
FIG. 3 is a diagram showing an air sparging process in an in-situ purification method and a remediation apparatus for organic-contaminated soil according to the present invention.

【 図4】本発明による有機物汚染土壌の原位置浄化方
法と修復装置における他の実施形態の概要図
FIG. 4 is a schematic view of another embodiment of an in-situ purification method and a remediation device for organic-contaminated soil according to the present invention.

【 図5】原位置浄化方法と修復装置における他の実施
形態におけるエアスパージング前の工程図
FIG. 5 is a process diagram before air sparging in another embodiment of the in-situ cleaning method and the repair apparatus.

【 図6】原位置浄化方法と修復装置における他の実施
形態におけるエアスパージング工程図
FIG. 6 is an air sparging process diagram in another embodiment of the in-situ cleaning method and the repair apparatus.

【 図7】原位置浄化方法と修復装置における土着微生
物の活性化を示す実施形態図
FIG. 7 is an embodiment diagram showing activation of indigenous microorganisms in the in-situ purification method and the restoration apparatus.

【符号の説明】[Explanation of symbols]

1、20、30 修復装置、 2 コンプレッサー、
3 スパージ井戸、4、17 抽出井戸、 5 水処理
装置、 6 ガス処理装置、7、8注入機、 9 飽和
帯、 10 不飽和帯、11、12、13 バルブ、
14 カバー、 15 気液分離装置、16 吸気ブロ
ア、
1, 20, 30 Restoration device, 2 Compressor,
3 sparge well, 4, 17 extraction well, 5 water treatment device, 6 gas treatment device, 7, 8 injector, 9 saturated zone, 10 unsaturated zone, 11, 12, 13 valve,
14 cover, 15 gas-liquid separator, 16 intake blower,

───────────────────────────────────────────────────── フロントページの続き (72)発明者 田崎 雅晴 東京都港区芝浦一丁目2番3号 清水建設 株式会社内 Fターム(参考) 2D043 CA20 DA01 EA10 4D004 AA41 AB02 AC07 CA19 CA36 CC01 CC02 CC11  ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Masaharu Tazaki 1-3-2 Shibaura, Minato-ku, Tokyo Shimizu Corporation F-term (reference) 2D043 CA20 DA01 EA10 4D004 AA41 AB02 AC07 CA19 CA36 CC01 CC02 CC11

Claims (7)

【特許請求の範囲】[Claims] 【請求項1】 有機物を生物処理する有機物汚染土壌の
原位置修復法であって、酸化剤を注入した後にエアスパ
ージングすることを特徴とする有機物汚染土壌の原位置
修復法。
1. An in situ restoration method for an organic substance-contaminated soil in which an organic substance is biologically treated, the method comprising injecting an oxidizing agent and then performing air sparging.
【請求項2】 酸化剤が、液状であって不飽和帯に注入
されることを特徴とする請求項1に記載の有機物汚染土
壌の原位置修復法。
2. The method according to claim 1, wherein the oxidizing agent is in a liquid state and injected into the unsaturated zone.
【請求項3】 酸化剤が、ガス状であって飽和帯に注入
されることを特徴とする請求項1又は2に記載の有機物
汚染土壌の原位置修復法。
3. The method according to claim 1, wherein the oxidizing agent is gaseous and injected into a saturated zone.
【請求項4】 原位置の土着微生物が、エアスパージン
グ時に混入されることを特徴とする請求項1乃至3のい
ずれかに記載の有機物汚染土壌の原位置修復法。
4. The method according to claim 1, wherein in situ indigenous microorganisms are mixed during air sparging.
【請求項5】 有機物で汚染されている土壌の修復装置
であって、エアスパ−ジング法による原位置修復装置を
配置し、該エアスパ−ジング法による原位置修復装置に
酸化剤の注入機を併置させることを特徴とする有機物汚
染土壌の原位置修復装置。
5. An apparatus for repairing soil contaminated with organic matter, comprising: an in-situ repair apparatus by an air sparging method; and an injecting machine for an oxidant in the in-situ repair apparatus by the air sparging method. An in-situ restoration apparatus for organic-contaminated soil, characterized in that the soil is repaired.
【請求項6】 酸化剤の注入機が、複数に分割して配置
されることを特徴とする請求項5に記載の有機物汚染土
壌の原位置修復装置。
6. The in-situ repair apparatus for organic-contaminated soil according to claim 5, wherein the oxidant injector is divided into a plurality of parts and arranged.
【請求項7】 少なくとも1つの酸化剤注入機が、原位
置修復装置のスパージ井戸に結合されることを特徴とす
る請求項6に記載の有機物汚染土壌の原位置修復装置。
7. The in-situ remediation apparatus for organically contaminated soil according to claim 6, wherein at least one oxidizer injector is coupled to the sparge well of the in-situ remediation apparatus.
JP2001055282A 2001-02-28 2001-02-28 In-situ repair method for soil contaminated with organic matter Expired - Lifetime JP4671073B2 (en)

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