JP2005074297A - Cleaning method for hardly-gas/water-permeable contaminated soil and system - Google Patents

Cleaning method for hardly-gas/water-permeable contaminated soil and system Download PDF

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JP2005074297A
JP2005074297A JP2003306879A JP2003306879A JP2005074297A JP 2005074297 A JP2005074297 A JP 2005074297A JP 2003306879 A JP2003306879 A JP 2003306879A JP 2003306879 A JP2003306879 A JP 2003306879A JP 2005074297 A JP2005074297 A JP 2005074297A
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air
permeable
contaminated
gas
hardly
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Kazuo Toge
和男 峠
Michihiko Ishida
道彦 石田
Yoji Ishikawa
洋二 石川
Haruhiko Fujii
治彦 藤井
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Obayashi Corp
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<P>PROBLEM TO BE SOLVED: To provide a cleaning method for hardly-gas/water-permeable contaminated soil capable of certainly and efficiently recovering the contaminated substance existing in a hardly gas/water permeation layer, and a system. <P>SOLUTION: The cleaning system 1 for the hardly water permeable contaminated soil is provided with a high pressure air pressure-introduction mechanism 5 for intermittently feeding high pressure air to a contaminated area 4 contaminated with the contaminant 3 such as oil and dioxins or volatile organic chlorine compounds of an unsaturated hardly gas/water permeation layer 2 existing above underground water level; and a gas treatment facility 13 for sucking the contaminant 3 with air after the air intermittently introduced is raised through an unsaturated gas permeation layer 7 while the air carries the contaminant 3. The high pressure air pressure-introduction mechanism 5 intermittently introduces the high pressure air from an air compressor 12 to the contaminated area 4 through a pressure-introduction pipe 9 and can impart vibration to soil particles in the contaminated area. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は、難透気透水性汚染土壌に存在する汚染物質を回収浄化する浄化方法及びシステムに関する。   The present invention relates to a purification method and system for recovering and purifying contaminants present in hardly permeable and air permeable contaminated soil.

工場跡地の土壌内には、トリクロロエチレンなどで代表される揮発性有機塩素化合物、燃料油や機械油、ダイオキシン類、あるいはカドミウム、鉛、銅、亜鉛、ニッケル、クロムなどの重金属といったさまざまな汚染物質が土壌に混入していることがある。   Various pollutants such as volatile organic chlorine compounds such as trichlorethylene, fuel oils and machine oils, dioxins, and heavy metals such as cadmium, lead, copper, zinc, nickel and chromium are found in the soil of the factory site. May be in the soil.

かかる汚染物質で汚染された汚染土をそのまま放置すると、該土に混入している汚染物質が周囲に拡散し、周辺住民の生活に支障を来すとともに、雨水によって土粒子から遊離した場合には、地下水等に混入して水質を汚濁させる原因ともなる。そのため、上述した汚染物質で汚染された土については、さまざまな方法を使って浄化しなければならない。   If the contaminated soil contaminated with such pollutants is left as it is, the contaminants mixed in the soil will diffuse to the surroundings, hindering the lives of the surrounding residents, and if it is released from the soil particles by rainwater In addition, it may cause contamination of groundwater by contaminating water quality. Therefore, the soil contaminated with the above-mentioned pollutants must be cleaned using various methods.

土壌内の汚染物質を原位置で浄化処理する方法としては、従来からさまざまな方法が開発されており、土壌ガス吸引法、汚染土壌に注水しこれを揚水して地上で処理するいわゆる通水洗浄法、空気を送り込んでその気泡に汚染物質を連行させる、いわゆる気泡連行浄化法、空気圧入とガス吸引を組み合わせたエアスパージング法、土中菌の微生物活性を利用したバイオレメディエーションによる方法など多種多様な方法が知られている。   Various methods have been developed to purify pollutants in the soil in-situ, so-called water-cleaning methods that use the soil gas suction method, injecting water into the contaminated soil, pumping it up, and treating it on the ground. Various methods, such as the so-called bubble entrainment purification method, which sends air in and entrains the pollutants in the bubbles, the air sparging method that combines pneumatic injection and gas suction, and the bioremediation method that utilizes the microbial activity of soil fungi The method is known.

特開2002−119952号公報JP 2002-119952 A 特開2001−205248号公報JP 2001-205248 A

しかしながら、汚染物質が粘土層やシルト層といった難透気透水層に存在する場合には上述した方法を採用することができない。すなわち、これらの難透気透水層は、透気性及び透水性が悪いため、汚染物質が入り込む懸念は比較的少ないものの、かかる難透気透水層にいったん汚染物質が混入すると、上述したように透気性及び透水性が悪いことがかえって浄化の支障となり、難透気透水層内から汚染物質を回収することがきわめて困難になるという問題を生じていた。   However, when the pollutant is present in a hardly air permeable water permeable layer such as a clay layer or a silt layer, the above-described method cannot be employed. That is, since these hardly permeable air permeable layers have poor air permeability and water permeability, there is relatively little concern about the entry of contaminants. However, once the contaminants are mixed into the hardly permeable air permeable layer, as described above. On the other hand, the poor tempering and water permeability impeded purification, which caused the problem that it was very difficult to recover the pollutants from the hardly permeable air permeable layer.

本発明は、上述した事情を考慮してなされたもので、難透気透水層に存在する汚染物質を確実かつ効率的に回収可能な難透気透水性汚染土壌の浄化方法及びシステムを提供することを目的とする。   The present invention has been made in consideration of the above-described circumstances, and provides a purification method and system for hardly permeable and air permeable contaminated soil capable of reliably and efficiently recovering contaminants present in the hardly permeable and air permeable layer. For the purpose.

上記目的を達成するため、本発明に係る難透気透水性汚染土壌の浄化方法は請求項1に記載したように、不飽和難透気透水層のうち、汚染物質で汚染されている汚染領域に高圧空気を間欠的に送り込み、次いで、該高圧空気の間欠圧入によって前記汚染領域内の土粒子に振動を付与し、次いで、間欠圧入された空気に前記汚染物質を連行させながら前記汚染物質を前記空気とともに吸引して浄化処理を行うものである。   In order to achieve the above object, the method for purifying hardly permeable and air permeable contaminated soil according to the present invention is as described in claim 1, wherein in the unsaturated hardly permeable and air permeable layer, a contaminated area contaminated with a contaminant. High pressure air is intermittently fed to the soil, and then the soil particles in the contaminated region are vibrated by intermittent press-fitting of the high-pressure air, and then the contaminants are entrained while entraining the contaminants in the intermittently-pressurized air. A purification process is performed by suction with the air.

また、本発明に係る難透気透水性汚染土壌の浄化システムは請求項2に記載したように、不飽和難透気透水層のうち、汚染物質で汚染されている汚染領域に高圧空気を間欠的に送り込み該高圧空気の間欠圧入によって前記汚染領域内の土粒子に振動を付与する高圧空気圧入機構と、間欠圧入された空気に連行された汚染物質を該空気とともに吸引して除荷処理を行うガス処理設備とを備えたものである。   In addition, the system for purifying hardly permeable and air permeable contaminated soil according to the present invention intermittently applies high-pressure air to a contaminated area contaminated with a contaminant in the unsaturated permeable and air permeable layer. A high-pressure pneumatic injection mechanism that applies vibrations to the soil particles in the contaminated area by intermittently injecting the high-pressure air, and sucking out contaminants entrained in the intermittently injected air together with the air to perform unloading processing. Gas treatment equipment to be performed.

また、本発明に係る難透気透水性汚染土壌の浄化システムは、前記高圧空気圧入機構を、高圧空気吐出口が前記不飽和難透気透水層の汚染領域に位置するように埋設される圧入管と、圧力容器及び空気タンクを介して該圧入管に接続されたエアコンプレッサーとから構成するとともに、前記ガス処理設備を、前記不飽和難透気透水層の上方に拡がる不飽和透気層に埋設された吸引管と、該吸引管に接続された気液分離槽と、該気液分離槽の気相空間に連通接続された吸引ブロアと、該吸引ブロアに接続された有害物質除去装置と、前記気液分離槽の液相空間に連通接続された水処理設備とから構成したものである。   Further, in the purification system for hardly permeable and air permeable contaminated soil according to the present invention, the high pressure / pneumatic injection mechanism is press-fitted so that a high pressure air discharge port is located in a contaminated region of the unsaturated hardly permeable and air permeable layer. And an air compressor connected to the press-fitting pipe through a pressure vessel and an air tank, and the gas treatment facility is formed into an unsaturated air permeable layer extending above the unsaturated hardly air permeable water layer. A buried suction pipe, a gas-liquid separation tank connected to the suction pipe, a suction blower connected to the gas phase space of the gas-liquid separation tank, and a harmful substance removing device connected to the suction blower And a water treatment facility connected to the liquid phase space of the gas-liquid separation tank.

本発明に係る難透気透水性汚染土壌の浄化方法及びシステムにおいては、不飽和難透気透水層のうち、汚染物質で汚染されている汚染領域に高圧空気を高圧空気圧入機構で間欠的に送り込み、該高圧空気の間欠圧入によって汚染領域内の土粒子に振動を付与する。   In the method and system for purifying hardly permeable and air permeable contaminated soil according to the present invention, high-pressure air is intermittently supplied to a contaminated area contaminated with the pollutant in the unsaturated permeable and air-permeable permeable layer by a high-pressure pneumatic injection mechanism. By feeding and intermittently injecting the high-pressure air, vibration is imparted to the soil particles in the contaminated area.

このようにすると、従来行われていた単なる空気圧入とは異なり、土粒子同士がぶつかり合って該土粒子間にあらたな間隙が生じたり、元の大きさよりも間隙が大きくなったり、土粒子の骨格が破壊されたりするとともに、土粒子同士が擦れ合うことで該土粒子の表面に付着していた汚染物質が該表面から剥がれる。   In this way, unlike the conventional method of simply entering air pressure, the soil particles collide with each other to create a new gap between the soil particles, the gap becomes larger than the original size, While the skeleton is destroyed, the soil particles are rubbed against each other, so that contaminants attached to the surface of the soil particles are peeled off from the surface.

かかる状態においては、間欠圧入された空気が土粒子間の間隙を流れる際、その流動抵抗は大幅に低下するとともに、土粒子に付着していた汚染物質が土粒子間の間隙に遊離してくるため、汚染物質も空気に連行されやすくなる。   In such a state, when the intermittently injected air flows through the gap between the soil particles, the flow resistance is greatly reduced, and the contaminants attached to the soil particles are released into the gap between the soil particles. Therefore, contaminants are also easily taken to the air.

そのため、間欠圧入された空気に汚染物質を連行させながら、汚染物質を空気とともにガス処理設備で吸引し浄化処理を行うようにすれば、従来のエアスパージング法等では不可能だった難透気透水性汚染土壌の浄化を確実かつ効率よく行うことが可能となる。   Therefore, if the contaminants are taken into the intermittently injected air and the contaminants are sucked together with the air in the gas treatment facility and purified, the impermeable air permeation that is impossible with the conventional air sparging method, etc. It is possible to reliably and efficiently purify soil with soil contamination.

汚染物質は、主として油や揮発性有機化合物(揮発性有機塩素化合物を含む)が対象となるが、ダイオキシン類など、空気連行可能な物質であればすべて本発明でいうところの汚染物質に含まれる。   Contaminants mainly include oil and volatile organic compounds (including volatile organic chlorine compounds), but any substance that can be air-entrained, such as dioxins, is included in the contaminants referred to in the present invention. .

不飽和難透気透水層でいう難透気透水層とは、主としてシルト層や粘土層を意味するが、透気性及び透水性が悪いために通水洗浄、ガス吸引、エアスパージング法等の従来法では汚染物質を回収することができないのであれば、シルト又は粘土のほかに砂を含む土層も当然本発明でいう難透気透水層に含まれる。   The hardly permeable air permeable layer in the unsaturated permeable air permeable layer mainly means a silt layer or a clay layer, but because of poor air permeability and water permeability, conventional methods such as water washing, gas suction, air sparging method, etc. If the pollutant cannot be recovered by the law, a soil layer containing sand in addition to silt or clay is naturally included in the hardly permeable air permeable layer referred to in the present invention.

高圧空気の間欠圧入は、汚染領域内の土粒子に振動を付与することで上述した作用を土粒子に及ぼすことができるのであれば、圧力の大きさや間欠の継続時間については、例えば不飽和難透気透水層の透気係数やその分布状況に応じて適宜定めればよい。   If intermittent press-fitting of high-pressure air can exert the above-mentioned action on the soil particles by applying vibration to the soil particles in the contaminated area, the magnitude of the pressure and the duration of the intermittent are, for example, difficult to unsaturated. What is necessary is just to determine suitably according to the air permeability coefficient of an air permeation-permeable layer, and its distribution condition.

ここで、本発明における空気圧入は、従来のような単なる圧入ではなく、間欠圧入であることを重ねて付言しておく。すなわち、単なる空気圧入では、難透気透水層の透気性を向上させることは困難であり、むしろ、土粒子間の間隙が元の大きさ以下に小さくなって、透気性が低下する場合も考えられる。   Here, it should be reiterated that the air pressure insertion in the present invention is not a mere press-fitting as in the prior art but an intermittent press-fitting. That is, it is difficult to improve the air permeability of the hardly permeable water permeable layer by simply introducing air pressure. Rather, the gap between the soil particles becomes smaller than the original size, and the air permeability may be lowered. It is done.

本出願人は、高圧空気の間欠圧入によって土粒子を振動させ、それによって上述した作用を生ぜしめ、ひいては難透気透水層の透気性を改善することができることを新規に見いだしたものであり、産業上きわめて有用な知見であるとともに、従来技術に比して顕著な作用効果を有するものである。   The present applicant has newly found that the soil particles are vibrated by intermittent press-fitting of high-pressure air, thereby causing the above-described action, and thus improving the air permeability of the hardly permeable air permeable layer. This is a very useful knowledge in the industry and has a remarkable effect as compared with the prior art.

高圧空気圧入機構やガス処理設備の構成は任意であるが、例えば、前記高圧空気圧入機構を、高圧空気吐出口が前記不飽和難透気透水層の汚染領域に位置するように埋設される圧入管と、圧力容器及び空気タンクを介して該圧入管に接続されたエアコンプレッサーとから構成するとともに、前記ガス処理設備を、前記不飽和難透気透水層の上方に拡がる不飽和透気層に埋設された吸引管と、該吸引管に接続された気液分離槽と、該気液分離槽の気相空間に連通接続された吸引ブロアと、該吸引ブロアに接続された有害物質除去装置と、前記気液分離槽の液相空間に連通接続された水処理設備とから構成ことが考えられる。   The configuration of the high pressure / pneumatic injection mechanism and the gas processing equipment is arbitrary. For example, the high pressure / pneumatic injection mechanism is press-fitted so that the high pressure air discharge port is located in the contaminated region of the unsaturated hardly permeable air permeable layer. And an air compressor connected to the press-fitting pipe through a pressure vessel and an air tank, and the gas treatment facility is formed into an unsaturated air permeable layer extending above the unsaturated hardly air permeable water layer. A buried suction pipe, a gas-liquid separation tank connected to the suction pipe, a suction blower connected to the gas phase space of the gas-liquid separation tank, and a harmful substance removing device connected to the suction blower A water treatment facility connected to the liquid phase space of the gas-liquid separation tank can be considered.

特に、圧入管及び圧力容器は、バイオプスター工法で使用される装置を転用することが可能である。なお、バイオプスター工法とは、パルス状の高圧の空気を一定の間隔で地中に送り込み、地中の好気性微生物を活性化させる工法であり、本発明とはその用途あるいは目的を全く異にする。   In particular, it is possible to divert an apparatus used in the Biopster construction method for the press-fitting pipe and the pressure vessel. The biopster method is a method in which pulsed high-pressure air is sent into the ground at regular intervals to activate the aerobic microorganisms in the ground, and its use or purpose is completely different from the present invention. To.

以下、本発明に係る難透気透水性汚染土壌の浄化方法及びシステムの実施の形態について、添付図面を参照して説明する。なお、従来技術と実質的に同一の部品等については同一の符号を付してその説明を省略する。   DESCRIPTION OF EMBODIMENTS Hereinafter, embodiments of a purification method and system for hardly permeable and air permeable contaminated soil according to the present invention will be described with reference to the accompanying drawings. Note that components that are substantially the same as those of the prior art are assigned the same reference numerals, and descriptions thereof are omitted.

図1は、本実施形態に係る難透気透水性汚染土壌の浄化システムを示した図である。本実施形態に係る難透気透水性汚染土壌の浄化システム1は同図に示すように、飽和層6に位置する地下水位より上に存在する不飽和難透気透水層2のうち、油やダイオキシン類あるいは揮発性有機塩素化合物といった汚染物質3で汚染されている汚染領域4に高圧空気を間欠的に送り込む高圧空気圧入機構5と、間欠圧入された空気が汚染物質3を連行しながら不飽和透気層7を上昇した後、汚染物質3を空気とともに吸引して浄化処理を行うガス処理設備13とを備える。   FIG. 1 is a view showing a purification system for hardly air permeable and contaminated soil according to the present embodiment. As shown in the figure, the hardly permeable and air permeable contaminated soil purification system 1 according to the present embodiment includes an oil or an oil permeable layer of the unsaturated permeable and air permeable layer 2 existing above the groundwater level located in the saturated layer 6. Unsaturation while intermittently injected air entrains the pollutant 3 and the high-pressure air injection mechanism 5 that intermittently sends high-pressure air to the contaminated area 4 that is contaminated with the pollutant 3 such as dioxins or volatile organic chlorine compounds After the air-permeable layer 7 is raised, a gas processing facility 13 that performs a purification process by sucking the contaminant 3 together with air is provided.

不飽和難透気透水層2は、シルト、粘土又は粘性土を主成分とする土からなるため、透気性に劣り、そのままの状態ではガス吸引が困難な土層であり、それに対し、不飽和透気層7は、透気性を有する例えば砂質土からなる土層となっている。   The unsaturated hardly permeable air permeable layer 2 is composed of soil mainly composed of silt, clay, or clay soil, and therefore is poor in air permeability, and is a soil layer in which gas suction is difficult as it is. The air permeable layer 7 is a soil layer made of sandy soil having air permeability, for example.

高圧空気圧入機構5は、エアコンプレッサー12と、該エアコンプレッサーから送気されてきた高圧空気を中間貯留する空気タンク11と、該空気タンク11から送気されてきた高圧空気の圧力を調整する圧力容器10と、該圧力容器に接続され高圧空気吐出口8が不飽和難透気透水層2の汚染領域4に位置するように埋設される圧入管9とから構成してあり、エアコンプレッサー12からの高圧空気を圧入管9を介して汚染領域4に間欠圧入し、該汚染領域内の土粒子に振動を付与することができるようになっている。   The high-pressure / pneumatic injection mechanism 5 includes an air compressor 12, an air tank 11 that intermediately stores high-pressure air sent from the air compressor, and a pressure that adjusts the pressure of the high-pressure air sent from the air tank 11. It is composed of a container 10 and a press-fit pipe 9 that is connected to the pressure container and embedded so that the high-pressure air discharge port 8 is located in the contaminated region 4 of the unsaturated hardly permeable air permeable layer 2. The high-pressure air is intermittently pressed into the contaminated area 4 through the press-fit pipe 9, and vibration can be imparted to the soil particles in the contaminated area.

ここで、圧入管9及び圧力容器10は、バイオプスター工法で使用される装置を転用することが可能である。   Here, as the press-fitting pipe 9 and the pressure vessel 10, it is possible to divert an apparatus used in the Biopster construction method.

ガス処理設備13は、不飽和難透気透水層2の上方に拡がる不飽和透気層7に埋設された吸引管14と、該吸引管に接続された気液分離槽15と、該気液分離槽の気相空間に連通接続された吸引ブロア16と、該吸引ブロアに接続された有害物質除去装置としての活性炭フィルター槽17と、気液分離槽の液相空間に連通接続された水処理設備18とから構成してある。   The gas treatment facility 13 includes a suction pipe 14 embedded in the unsaturated gas permeable layer 7 extending above the unsaturated hardly gas permeable water layer 2, a gas-liquid separation tank 15 connected to the suction pipe, and the gas liquid A suction blower 16 communicatively connected to the gas phase space of the separation tank, an activated carbon filter tank 17 as a harmful substance removal device connected to the suction blower, and a water treatment communicatively connected to the liquid phase space of the gas-liquid separation tank It is composed of equipment 18.

本実施形態に係る難透気透水性汚染土壌の浄化システム1を設置するには、まず、不飽和難透気透水層2のうち、汚染物質で汚染されている汚染領域4に高圧空気圧入機構5の圧入管9を建て込む。   In order to install the purification system 1 of the hardly permeable and air permeable contaminated soil according to the present embodiment, first, a high-pressure pneumatic mechanism is installed in the contaminated region 4 of the unsaturated permeable and air permeable layer 2 that is contaminated with the contaminant. 5 press-fit pipes 9 are installed.

圧入管9を建て込むにあたっては、あらかじめ該当位置をボーリングし、次いで該ボーリング孔に圧入管9を挿入し、しかる後、高圧空気吐出口8が閉塞されることがないよう、圧入管9とボーリング孔との間に所定量の砂を先行充填して透気性を確保する一方、圧入管9の揺れを防止すべく、ボーリング孔との隙間には高圧空気吐出口8よりも浅い箇所において、モルタル、ベントナイトなどを充填する。   When the press-fit pipe 9 is installed, the corresponding position is bored in advance, and then the press-fit pipe 9 is inserted into the bore hole, and then the press-fit pipe 9 and the bore are prevented from being blocked. In order to ensure air permeability by pre-filling a predetermined amount of sand between the holes, the mortar is placed in a space shallower than the high-pressure air discharge port 8 in the gap with the bore hole to prevent the press-fitting pipe 9 from shaking. Fill with bentonite and so on.

次に、圧入管9の上端に圧力容器10を取り付けるとともに、空気タンク11及びエアコンプレッサー12を順次接続する。   Next, the pressure vessel 10 is attached to the upper end of the press-fit pipe 9, and the air tank 11 and the air compressor 12 are sequentially connected.

一方、不飽和透気層7に吸引管14を埋設するとともに該吸引管に気液分離装置15を接続し、しかる後、上述したようにその気相空間に連通するように吸引ブロア16及び活性炭フィルター槽17を順次接続するとともに、その液相空間に連通するように水処理設備18を接続する。   On the other hand, a suction pipe 14 is embedded in the unsaturated gas permeable layer 7 and a gas-liquid separation device 15 is connected to the suction pipe. Thereafter, as described above, the suction blower 16 and activated carbon are communicated with the gas phase space. The filter tank 17 is sequentially connected, and the water treatment facility 18 is connected so as to communicate with the liquid phase space.

このように設置された浄化システム1を用いて難透気透水性汚染土壌、本実施形態では不飽和難透気透水層2の汚染領域4を浄化するには、まず、エアコンプレッサー12、空気タンク11及び圧力容器10を適宜作動させることで不飽和難透気透水層2の汚染領域4に高圧空気を間欠的に送り込み、該高圧空気の間欠圧入によって汚染領域4内の土粒子に振動を付与する。   In order to purify the hardly permeable and air permeable contaminated soil, in this embodiment the contaminated region 4 of the unsaturated permeable and permeable water permeable layer 2 using the purification system 1 installed in this way, first, an air compressor 12 and an air tank 11 and the pressure vessel 10 are appropriately operated to intermittently send high-pressure air into the contaminated region 4 of the unsaturated hardly permeable air permeable layer 2, and impart vibration to the soil particles in the contaminated region 4 by intermittent press-fitting of the high-pressure air. To do.

このようにすると、従来行われていた単なる空気圧入とは異なり、高圧空気の間欠圧入により、土粒子同士がぶつかり合って該土粒子間にあらたな間隙が生じたり、元の大きさよりも間隙が大きくなったり、粘性土の骨格が破壊されたりするとともに、土粒子同士が擦れ合うことで該土粒子の表面に付着していた汚染物質が該表面から剥がれる。   In this way, unlike the conventional simple air pressure insertion, the intermittent press-fitting of high-pressure air causes the soil particles to collide with each other, resulting in a new gap between the soil particles, or a gap larger than the original size. As the soil becomes larger or the skeleton of the clay soil is destroyed, the soil particles are rubbed against each other, so that the contaminants attached to the surface of the soil particles are peeled off from the surface.

図2は、それらのうち、粘性土の骨格破壊が生じる場合を例に挙げたものであって、同図(a)は、高圧空気の間欠圧入を行っている様子、同図(b)は高圧空気の間欠圧入を行う前の粘性土の骨格、同図(c)は高圧空気の間欠圧入を行った後の粘性土の骨格の様子を示したものである。   Fig. 2 shows an example of the case where a skeletal fracture of cohesive soil occurs. Fig. 2 (a) shows intermittent press-fitting of high-pressure air, and Fig. 2 (b) Fig. 2 (c) shows the state of the viscous soil skeleton after intermittent high-pressure air injection.

これらの図でわかるように、粘性土の骨格は、高圧空気の間欠圧入により破壊されて土粒子がばらばらになり、空隙21があらたに生じるとともに、土粒子表面に付着していた汚染物質3は該土粒子から剥離する。   As can be seen from these figures, the clay skeleton is broken by intermittent press-fitting of high-pressure air and the soil particles are separated, and voids 21 are newly generated, and the contaminant 3 attached to the surface of the soil particles is Peel from the soil particles.

骨格が破壊されない場合も、高圧空気の間欠圧入によってあらたな間隙が生じたり、元の間隙が大きくなったりすることに変わりはなく、かくして、間欠圧入された空気22は、土粒子間の間隙21を流れる際、その流動抵抗が大幅に低下して流れやすくなるとともに、土粒子に付着していた汚染物質3が土粒子間の間隙21に遊離しているため、汚染物質3も空気22に連行されやすくなる。   Even when the skeleton is not destroyed, there is no change in that a new gap is generated by the intermittent press-fitting of high-pressure air, or the original gap is increased. Thus, the intermittently press-fitted air 22 is a gap 21 between soil particles. The flow resistance is greatly reduced when flowing through the soil, and it becomes easy to flow, and the contaminant 3 adhering to the soil particles is released in the gap 21 between the soil particles, so the contaminant 3 is also entrained in the air 22. It becomes easy to be done.

次に、間欠圧入された空気22が汚染物質3を連行しながら不飽和透気層7を上昇した後、汚染物質3を空気22とともにガス処理設備13で吸引し浄化処理を行う。吸引は、吸引ブロア16を作動させることにより行う。   Next, after the intermittently injected air 22 moves up the unsaturated air permeable layer 7 while entraining the pollutant 3, the pollutant 3 is sucked together with the air 22 by the gas treatment facility 13 to perform a purification process. Suction is performed by operating the suction blower 16.

次に、吸引された汚染物質連行空気を気液分離槽15で液体と気体に分離し、気体については、活性炭フィルター槽17に通して汚染物質3を活性炭に吸着させ、その後、大気に放出するとともに、液体については、水処理設備18で汚染物質3を除去し、その後、河川等に放流する。   Next, the sucked pollutant entrained air is separated into liquid and gas in the gas-liquid separation tank 15, and the gas is passed through the activated carbon filter tank 17 to adsorb the pollutant 3 on the activated carbon, and then released to the atmosphere. At the same time, for the liquid, the pollutant 3 is removed by the water treatment facility 18 and then discharged into a river or the like.

なお、不飽和透気層7といえども、吸引される物質は完全にガスだけではなく、降雨等の気象条件によっては多少なりとも水分も吸引されるため、気液分離槽15を介在させるとともに水処理設備18を設置するのが望ましいことは言うまでもない。   Even in the case of the unsaturated gas permeable layer 7, the substance to be sucked is not only gas but also moisture is sucked in some amounts depending on weather conditions such as rainfall, and therefore the gas-liquid separation tank 15 is interposed. Needless to say, it is desirable to install the water treatment facility 18.

以上説明したように、本実施形態に係る難透気透水性汚染土壌の浄化方法及びシステムによれば、従来行われていた単なる空気圧入とは異なり、土粒子同士がぶつかり合って該土粒子間にあらたな間隙が生じたり、元の大きさよりも間隙が大きくなったり、土粒子の骨格が破壊されたりするとともに、土粒子同士が擦れ合うことで該土粒子の表面に付着していた汚染物質3が該表面から剥がれる。   As described above, according to the purification method and system for hardly permeable and air permeable contaminated soil according to the present embodiment, unlike the conventional method of simply entering air pressure, the soil particles collide with each other, Contaminant 3 attached to the surface of the soil particles due to the formation of a new gap, the gap becoming larger than the original size, the skeleton of the soil particles being destroyed, and the soil particles rubbing against each other Peels from the surface.

かかる状態においては、間欠圧入された空気22が土粒子間の間隙を流れる際、その流動抵抗は大幅に低下するとともに、土粒子に付着していた汚染物質3が土粒子間の間隙に遊離してくるため、汚染物質3も空気22に連行されやすくなる。   In such a state, when the intermittently injected air 22 flows through the gap between the soil particles, the flow resistance is greatly reduced, and the contaminant 3 adhering to the soil particles is released into the gap between the soil particles. Therefore, the pollutant 3 is also easily taken to the air 22.

そのため、間欠圧入された空気22が汚染物質3を連行しながら不飽和透気層7を上昇した後、汚染物質3を空気22とともに吸引し浄化処理を行うようにすれば、従来のエアスパージング法等では不可能だった不飽和難透気透水層2の浄化を確実かつ効率よく行うことが可能となる。   For this reason, if the intermittently injected air 22 moves up the unsaturated air permeable layer 7 while entraining the pollutant 3, and if the pollutant 3 is sucked together with the air 22 to perform the purification process, the conventional air sparging method is performed. Thus, it becomes possible to reliably and efficiently purify the unsaturated hardly permeable air permeable layer 2 that could not be obtained by the above method.

本実施形態では、高圧空気圧入機構5を、エアコンプレッサー12と、該エアコンプレッサーから送気されてきた高圧空気を中間貯留する空気タンク11と、該空気タンク11から送気されてきた高圧空気の圧力を調整する圧力容器10と、該圧力容器に接続され高圧空気吐出口8が不飽和難透気透水層2の汚染領域4に位置するように埋設される圧入管9とから構成したが、高圧空気の間欠圧入によって汚染領域4内の土粒子に振動を付与することができるのであれば、どのような構成でもかまわない。   In the present embodiment, the high-pressure / pneumatic injection mechanism 5 includes an air compressor 12, an air tank 11 that intermediately stores high-pressure air supplied from the air compressor, and high-pressure air supplied from the air tank 11. The pressure vessel 10 is configured to adjust the pressure, and the press-fit pipe 9 is connected to the pressure vessel and embedded so that the high-pressure air discharge port 8 is located in the contaminated region 4 of the unsaturated hardly permeable air permeable layer 2. Any configuration may be used as long as vibration can be imparted to the soil particles in the contaminated region 4 by intermittent injection of high-pressure air.

本実施形態に係る難透気透水性汚染土壌の浄化システムの概略図。Schematic of the purification system of the hardly air permeable water-contaminated soil which concerns on this embodiment. 本実施形態に係る難透気透水性汚染土壌の浄化方法の作用の一例を示した模式図。The schematic diagram which showed an example of the effect | action of the purification method of the hardly air permeable permeation | contamination soil which concerns on this embodiment.

符号の説明Explanation of symbols

1 難透気透水性汚染土壌の浄化システム
2 不飽和難透気透水層
3 汚染物質
4 汚染領域
5 高圧空気圧入機構
7 不飽和透気層
9 圧入管
10 圧力容器
11 空気タンク
12 エアコンプレッサー
13 ガス処理設備
14 吸引管
15 気液分離槽
16 吸引ブロア
17 活性炭フィルター槽(有害物質除去装置)
18 水処理設備
DESCRIPTION OF SYMBOLS 1 Purification system of hardly air permeable permeability contaminated soil 2 Unsaturated hardly air permeable water layer 3 Pollutant 4 Contaminated area 5 High-pressure pneumatic injection mechanism 7 Unsaturated air permeable layer 9 Press-in pipe 10 Pressure vessel 11 Air tank 12 Air compressor 13 Gas Treatment equipment 14 Suction tube 15 Gas-liquid separation tank 16 Suction blower 17 Activated carbon filter tank (Toxic substance removal device)
18 Water treatment facilities

Claims (3)

不飽和難透気透水層のうち、汚染物質で汚染されている汚染領域に高圧空気を間欠的に送り込み、次いで、該高圧空気の間欠圧入によって前記汚染領域内の土粒子に振動を付与し、次いで、間欠圧入された空気に前記汚染物質を連行させながら前記汚染物質を前記空気とともに吸引して浄化処理を行うことを特徴とする難透気透水性汚染土壌の浄化方法。 High pressure air is intermittently sent to the contaminated area contaminated with the pollutant among the unsaturated hardly permeable air permeable layer, and then vibration is imparted to the soil particles in the contaminated area by intermittent injection of the high pressure air. Next, a method for purifying hardly air-permeable and permeable contaminated soil, wherein the pollutant is sucked together with the air while the pollutant is entrained in intermittently injected air, and the purification process is performed. 不飽和難透気透水層のうち、汚染物質で汚染されている汚染領域に高圧空気を間欠的に送り込み該高圧空気の間欠圧入によって前記汚染領域内の土粒子に振動を付与する高圧空気圧入機構と、間欠圧入された空気に連行された汚染物質を該空気とともに吸引して浄化処理を行うガス処理設備とを備えたことを特徴とする難透気透水性汚染土壌の浄化システム。 A high-pressure pneumatic injection mechanism that intermittently feeds high-pressure air to a contaminated area contaminated with a pollutant in the unsaturated hardly permeable air-permeable layer and applies vibration to the soil particles in the contaminated area by intermittent injection of the high-pressure air. And a gas treatment facility for performing a purification treatment by sucking together with the air the pollutant entrained in the intermittently injected air, and a purification system for hardly permeable and air permeable contaminated soil. 前記高圧空気圧入機構を、高圧空気吐出口が前記不飽和難透気透水層の汚染領域に位置するように埋設される圧入管と、圧力容器及び空気タンクを介して該圧入管に接続されたエアコンプレッサーとから構成するとともに、前記ガス処理設備を、前記不飽和難透気透水層の上方に拡がる不飽和透気層に埋設された吸引管と、該吸引管に接続された気液分離槽と、該気液分離槽の気相空間に連通接続された吸引ブロアと、該吸引ブロアに接続された有害物質除去装置と、前記気液分離槽の液相空間に連通接続された水処理設備とから構成した請求項2記載の難透気透水性汚染土壌の浄化システム。 The high-pressure air-injection mechanism was connected to the press-in pipe through a pressure-in pipe and an air tank embedded in such a manner that a high-pressure air discharge port is located in the contaminated region of the unsaturated hardly permeable air permeable layer. A suction pipe embedded in the unsaturated gas permeable layer extending above the unsaturated hardly permeable gas permeable layer, and a gas-liquid separation tank connected to the suction pipe. A suction blower connected to the gas phase space of the gas-liquid separation tank, a harmful substance removing device connected to the suction blower, and a water treatment facility connected to the liquid phase space of the gas-liquid separation tank The purification system for hardly permeable and air permeable contaminated soil according to claim 2, comprising:
JP2003306879A 2003-08-29 2003-08-29 Cleaning method for hardly-gas/water-permeable contaminated soil and system Pending JP2005074297A (en)

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010227733A (en) * 2009-03-25 2010-10-14 Ohbayashi Corp Method and system for cleaning contaminated soil in situ
JP2011050958A (en) * 2010-11-10 2011-03-17 Ohbayashi Corp In situ cleaning method for contaminated ground or contaminated groundwater
CN103350104A (en) * 2013-07-17 2013-10-16 中国科学院地理科学与资源研究所 In-polluted-site heat-intensifying vapor extracting and repairing integrated device and application method
CN108994076A (en) * 2018-08-22 2018-12-14 成都理工大学 Half built-in type soil remediation ball of one kind and its application method
CN115532810A (en) * 2022-09-28 2022-12-30 上海勘察设计研究院(集团)有限公司 Intelligent soil remediation project medicament injection device that can dynamically adjust

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010227733A (en) * 2009-03-25 2010-10-14 Ohbayashi Corp Method and system for cleaning contaminated soil in situ
JP2011050958A (en) * 2010-11-10 2011-03-17 Ohbayashi Corp In situ cleaning method for contaminated ground or contaminated groundwater
CN103350104A (en) * 2013-07-17 2013-10-16 中国科学院地理科学与资源研究所 In-polluted-site heat-intensifying vapor extracting and repairing integrated device and application method
CN108994076A (en) * 2018-08-22 2018-12-14 成都理工大学 Half built-in type soil remediation ball of one kind and its application method
CN108994076B (en) * 2018-08-22 2020-03-27 成都理工大学 Semi-embedded soil remediation ball and using method thereof
CN115532810A (en) * 2022-09-28 2022-12-30 上海勘察设计研究院(集团)有限公司 Intelligent soil remediation project medicament injection device that can dynamically adjust
CN115532810B (en) * 2022-09-28 2023-12-19 上海勘察设计研究院(集团)股份有限公司 Intelligent soil repair engineering agent injection device that can dynamically adjust

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