JP2007105595A - Contamination cleaning method for clay layer - Google Patents

Contamination cleaning method for clay layer Download PDF

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JP2007105595A
JP2007105595A JP2005297527A JP2005297527A JP2007105595A JP 2007105595 A JP2007105595 A JP 2007105595A JP 2005297527 A JP2005297527 A JP 2005297527A JP 2005297527 A JP2005297527 A JP 2005297527A JP 2007105595 A JP2007105595 A JP 2007105595A
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clay layer
layer
soil
contaminated
permeable layer
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JP4645403B2 (en
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Koji Shimizu
巧治 清水
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Panasonic Holdings Corp
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Matsushita Electric Industrial Co Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To efficiently restore a contamination substance such as oils and an organic chlorine based compound existing in a clay layer at an original position without requiring a large number of facilities or the like. <P>SOLUTION: In the contamination cleaning method for the clay layer, a division wall 5 is installed to a water-permeable layer 2 positioned at a lower part of the upper clay layer 1 contaminated with the contamination substance and a surfactant and a nutrition source of a microorganism are poured to the upper clay layer 1 in the division wall 5 at a high pressure to remove and elute the contamination substance from soil particles of the upper clay layer 1. Further, the removed and eluted contamination substance and the nutrition source are moved to the water-permeable layer 2 to promote microorganism decomposition. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は、本発明は、油類、有機塩素化合物等に汚染された地下領域に土着している微生物の活動を利用して、原位置修復する土壌の浄化技術に関するものである。   The present invention relates to a soil purification technique for restoring in situ by utilizing the activities of microorganisms indigenous to underground areas contaminated with oils, organic chlorine compounds and the like.

工場跡地等の地中土壌内には、トリクロロエチレンなどで代表される有機塩素化合物、軽油、重油等の油類、その他の汚染物質が混入している場合がある。これらにより汚染された土壌の浄化事業を進めることは必要不可欠であり、より一層確実にかつ低コストの浄化技術の開発が望まれている。   In the underground soil such as factory ruins, organic chlorine compounds represented by trichlorethylene, oils such as light oil and heavy oil, and other pollutants may be mixed. It is indispensable to proceed with the purification business of soil contaminated by these, and there is a demand for the development of a more reliable and low-cost purification technology.

特に、汚染領域が粘土層(シルト層)の場合には、土壌の粘性が高く、飽和状態で水流による水分の移動がない。さらに土壌粒子表面および土壌粒子間に汚染物質が強く吸着している。このため汚染物質の浄化がより困難となる課題を有している。   In particular, when the contaminated area is a clay layer (silt layer), the viscosity of the soil is high and there is no movement of moisture due to water flow in a saturated state. Furthermore, contaminants are strongly adsorbed between the soil particle surface and between the soil particles. For this reason, it has the subject that purification of a pollutant becomes more difficult.

従来、汚染された土壌を浄化する各種の方法が開発されているが、汚染された地下領域を原位置で修復する代表的な方法として下記のものがある。   Conventionally, various methods for purifying contaminated soil have been developed. As typical methods for repairing a contaminated underground area in situ, there are the following methods.

地下水位より上に存在する所定層としての不飽和難透気透水層のうち、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で汚染されている汚染領域に通気用空気を送り込む通気用空気圧入機構と、汚染領域に振動を付与する振動付与機構と、通気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するガス処理設備とを備える。振動付与機構は、不飽和難透気透水層まで掘削された立坑と該立坑の掘削底に設置された起振機とからなり、該起振機を駆動することにより所望の周波数の振動を不飽和難透気透水層の汚染領域に付与し、汚染物質を回収して処理方法である(例えば、特許文献1参照)。   Ventilation air pressure that feeds ventilation air to contaminated areas contaminated with contaminants such as oil, dioxins, or volatile organic chlorine compounds, among the unsaturated low-permeability water-permeable layers that exist above the groundwater level. An inlet mechanism, a vibration applying mechanism that applies vibration to the contaminated area, and a gas processing facility that sucks the contaminants entrained in the aerated air together with the air. The vibration imparting mechanism comprises a shaft excavated up to the unsaturated hardly-permeable air-permeable layer and an exciter installed at the excavation bottom of the shaft, and the vibration is not generated by driving the exciter. This is a treatment method in which a contaminant is collected by applying to a contaminated region of a saturated hardly permeable air permeable layer (see, for example, Patent Document 1).

また、汚染土壌を取り囲むように土中に四角状に止水壁を設ける。止水壁に囲まれた汚染エリアにおいて、地表部に位置する非汚染土壌を予め搬出し、仮置きしておく。汚染エリア2に必要な栄養剤を添加しながら、前記汚染土壌と地下水を撹拌装置により撹拌して、泥土状にするとともに、汚染土壌内に通気管を挿入し同時に十分通気する汚染土壌の生物化学的浄化方法である(例えば、特許文献2参照)。
特開2005−74276号公報 特開2003−71430号公報
In addition, a water blocking wall is provided in a square shape in the soil so as to surround the contaminated soil. In a contaminated area surrounded by a water blocking wall, uncontaminated soil located on the surface is carried out in advance and temporarily placed. While adding necessary nutrients to the contaminated area 2, the contaminated soil and groundwater are agitated by a stirrer to form a mud, and a biochemical chemistry of the contaminated soil that ventilates the contaminated soil and simultaneously vents sufficiently. Purification method (for example, see Patent Document 2).
JP 2005-74276 A JP 2003-71430 A

しかしながら、特許文献1に記載のものは、汚染領域に通気用空気を送り込む通気用空気圧入機構、汚染領域に振動を付与する振動付与機構(起振機)、通気された空気に連行された汚染物質を空気とともに吸引するガス処理設備等の多くの設備構成および大型の設備を必要とし、振動対策を要する等の課題がある。   However, the one described in Patent Document 1 includes a ventilation air pressure insertion mechanism that sends ventilation air to the contaminated area, a vibration imparting mechanism (vibrator) that imparts vibration to the contaminated area, and contamination that is entrained in the aerated air. Many equipment configurations such as gas treatment equipment that sucks substances together with air and large equipment are required, and there is a problem that vibration measures are required.

また起振機による所望の周波数の振動を不飽和難透気透水層の汚染領域に付与する際に、地下汚染箇所の諸状況により振動伝播にバラツキを生じやすく、土粒子の表面に付着していた汚染物質の剥離が不十分となり、汚染物質を完全に吸引することが困難な場合がある。   In addition, when applying vibration of the desired frequency by the vibrator to the contaminated area of the unsaturated permeable air permeable layer, the vibration propagation tends to vary depending on the situation of the underground contaminated part, and it adheres to the surface of the soil particles. In some cases, the peeling of the pollutant becomes insufficient, and it is difficult to completely suck the pollutant.

また、前記した特許文献2に記載のものは、土中に四角状に止水壁の設置、地表部に位置する非汚染土壌の掘削と搬出、汚染エリアの汚染土壌と地下水との撹拌、泥土状化、浄化完了後仮置きした非汚染土壌を汚染エリアへの埋め戻しをするための重機等の大型の設備等を必要し、また作業工程が多い。   Moreover, the thing of above-mentioned patent document 2 installs a water stop wall in the shape of a square in the soil, excavates and carries out non-contaminated soil located on the surface, agitation of contaminated soil and groundwater in the contaminated area, mud soil Large equipment such as heavy machinery for backfilling uncontaminated soil temporarily placed in the contaminated area after completion of clarification and purification is required, and there are many work processes.

また、掘削による土壌を保管する広大なスペースを必要とするという課題もある。   There is also a problem that a vast space for storing soil by excavation is required.

本発明は、前記従来の課題を解決するもので、粘土層に存在する油類、有機塩素系化合物等の汚染物質を、原位置で効率的に、かつ多くの設備等を必要とせずに修復することを目的とするものである。   The present invention solves the above-mentioned conventional problems, and restores pollutants such as oils and organochlorine compounds existing in the clay layer efficiently in situ without requiring many facilities. It is intended to do.

汚染物質で汚染されている粘土層の下部に位置する透水層まで区画壁を設置し、前記区画壁内の粘土層に界面活性剤および微生物の栄養源を高圧で注入し、汚染物質を粘土層の土粒子から離脱、溶出させ、さらに離脱、溶出させた汚染物質および栄養源を透水層に移動させて微生物分解を促進させることを特徴とする粘土層の汚染浄化方法としたものである。   A partition wall is installed up to the permeable layer located under the clay layer contaminated with the pollutant, and a surfactant and a nutrient source of microorganisms are injected into the clay layer in the partition wall at a high pressure, and the contaminant is put into the clay layer. It is a method for decontaminating a clay layer, characterized in that the pollutants and nutrients separated and eluted from the soil particles are moved to the water-permeable layer to promote microbial degradation.

本発明によれば、粘土層に存在する油類、有機塩素系化合物等の汚染物質を、原位置で効率的に、かつ多くの設備等を必要とせずに修復することができる。   According to the present invention, pollutants such as oils and organochlorine compounds existing in the clay layer can be repaired efficiently in situ without requiring many facilities.

第1の発明は、汚染物質で汚染されている粘土層の下部に位置する透水層まで区画壁を設置し、前記区画壁内の粘土層に界面活性剤および微生物の栄養源を高圧(10MPa)で注入し、汚染物質を粘土層の土粒子から離脱、溶出させ、さらに離脱、溶出させた汚染物質および栄養源を透水層に移動させて微生物分解を促進させることを特徴とする粘土層の汚染浄化方法としたものである。   1st invention sets a partition wall to the water-permeable layer located in the lower part of the clay layer contaminated with the pollutant, and puts a surfactant and a microbial nutrient source on the clay layer in the partition wall under high pressure (10 MPa) Contamination of clay layer by injecting and leaching pollutants from soil particles in clay layer, and further detaching and eluting pollutants and nutrients to permeable layer to promote microbial degradation This is a purification method.

これによって、粘土層の土壌粒子表面および土壌粒子間に強く吸着している汚染物質を界面活性剤により土壌粒子表面および土壌粒子間から含有水分に離脱、溶出させる。   As a result, the contaminants that are strongly adsorbed between the soil particle surface and between the soil particles of the clay layer are desorbed and eluted from the surface of the soil particles and between the soil particles by the surfactant.

さらに、粘土層の土壌粒子表面および土壌粒子間から含有水分に離脱、溶出した汚染物質および栄養源を砂礫土壌である透水層に移動させる。   Furthermore, the pollutants and nutrients that are released from the surface and between the soil particles of the clay layer are transferred to the permeable layer that is gravel soil.

これによって透水層において微生物の生育および分解活性を高めて汚染物質の浄化を促進さることができる。   As a result, the growth and decomposition activity of microorganisms can be increased in the water permeable layer to promote the purification of contaminants.

なぜなら、粘土層は、カオリン、ベントナイト等で構成されており、微生物よりも土粒子(約2μm)の方が細かく、微生物が土粒子の隙間に付着した汚染物質を分解することが困難であるためである。   This is because the clay layer is composed of kaolin, bentonite, etc., and the soil particles (about 2 μm) are finer than the microorganisms, and it is difficult for the microorganisms to decompose the contaminants adhering to the gaps between the soil particles. It is.

また浄化設備をより簡素化することもできる。   Moreover, the purification equipment can be further simplified.

さらに、粘土層から透水層への汚染物質の溶出による二次公害を、透水層下部までの区画壁により防止できる。   Furthermore, secondary pollution due to the elution of contaminants from the clay layer to the permeable layer can be prevented by the partition wall to the lower part of the permeable layer.

第2の発明は、第1の発明において、界面活性剤がレシチンであり、栄養源がステアリン酸を主成分とするものである粘土層の汚染浄化方法としたものである。   The second invention is a method for decontaminating a clay layer according to the first invention, wherein the surfactant is lecithin and the nutrient source is stearic acid as a main component.

これによって、レシチンおよびステアリン酸が天然の産出物質であり周囲環境への悪影響を抑制することができる。   As a result, lecithin and stearic acid are natural production substances, which can suppress adverse effects on the surrounding environment.

以下、本発明の一実施例の粘土層の汚染浄化方法を、図1を参照しながら説明する。図1は本発明の一実施例の粘土層の汚染浄化方法を示す断面部分の基本構成図である。   Hereinafter, a clay layer contamination purification method according to an embodiment of the present invention will be described with reference to FIG. FIG. 1 is a basic configuration diagram of a cross-sectional portion showing a clay layer contamination purification method according to an embodiment of the present invention.

以下、本発明の一実施例を図面に基づいて説明する。   Hereinafter, an embodiment of the present invention will be described with reference to the drawings.

地表面から上部粘土層1、透水層2、下部粘土層3からなる基本的な地下領域において、上部粘土層1または上部粘土層1と透水層2の境界部分に油類、有機塩素化合物等の汚染領域4が存在する例である。汚染物質である重油等は、原液状で存在しているか、または土壌や土壌中の有機物に吸着されている。   In the basic underground area consisting of the upper clay layer 1, the water permeable layer 2, and the lower clay layer 3 from the ground surface, oil, organic chlorine compounds, etc. are applied to the upper clay layer 1 or the boundary between the upper clay layer 1 and the water permeable layer 2. This is an example in which a contaminated area 4 exists. Heavy oil or the like that is a pollutant exists in a raw liquid state, or is adsorbed by soil or organic matter in the soil.

汚染物質で汚染されている上部粘土層1の下部に位置する透水層2まで汚染領域4を囲うように区画壁5を設置する。透水層2に位置する区画壁5には透水性の材質あるいは多数の細孔5aが穿設されている。区画壁5内の上部粘土層1に供給管6の先端を開口させ、供給管6の他端は注入手段である高圧ポンプ7に接続されている。さらに高圧ポンプ7に界面活性剤であるレシチンおよび栄養源であるステアリン酸の貯留容器8、9が接続されている。また透水層2の下端まで観測用井戸10を設置し、少なくとも透水層2の汚染濃度、栄養源量等をモニタリングする。   The partition wall 5 is installed so as to surround the contaminated area 4 up to the water permeable layer 2 located below the upper clay layer 1 contaminated with the pollutant. The partition wall 5 located in the water permeable layer 2 is formed with a water permeable material or a large number of pores 5a. The upper end of the supply pipe 6 is opened in the upper clay layer 1 in the partition wall 5, and the other end of the supply pipe 6 is connected to a high-pressure pump 7 that is an injection means. Furthermore, the high-pressure pump 7 is connected to reservoirs 8 and 9 for lecithin as a surfactant and stearic acid as a nutrient source. Moreover, the observation well 10 is installed to the lower end of the permeable layer 2, and at least the contamination concentration of the permeable layer 2, the amount of nutrients, etc. are monitored.

高圧ポンプ7によって界面活性剤であるレシチンおよび栄養源であるステアリン酸を例えば10MPaの圧力で供給管6を介して上部粘土層1に注入する。これによって上部粘土層1の土壌粒子表面および土壌粒子間に強く吸着している汚染物質を界面活性剤により土壌粒子表面および土壌粒子間から含有水分に離脱、溶出させる。   The high-pressure pump 7 injects the surfactant lecithin and the nutrient source stearic acid into the upper clay layer 1 through the supply pipe 6 at a pressure of 10 MPa, for example. As a result, the contaminants strongly adsorbed between the soil particle surfaces of the upper clay layer 1 and between the soil particles are separated from the surface of the soil particles and between the soil particles into the contained water and eluted by the surfactant.

さらに、上部粘土層1の土壌粒子表面および土壌粒子間から含有水分に離脱、溶出した汚染物質および栄養源を砂礫土壌である透水層2に移動させる。これによって透水層2において、微生物の生育および分解活性を高めて汚染物質の浄化を促進さることができる。また浄化設備をより簡素化することができる。   Furthermore, the contaminants and nutrients that have been separated and eluted from the surface of the upper clay layer 1 and between the soil particles are transferred to the permeable layer 2 that is gravel soil. As a result, in the water permeable layer 2, the growth and decomposition activity of microorganisms can be increased and the purification of contaminants can be promoted. Moreover, the purification equipment can be further simplified.

界面活性剤としてレシチン、栄養源としてステアリン酸を用いることによって、これらが天然の産出物質であることから周囲環境への悪影響を抑制することができる。また透水層2の下端まで観測用井戸10を設置し、少なくとも透水層2の汚染濃度、栄養源量等をモニタリングして、上部粘土層1に供給する界面活性剤、栄養源を最適な状態に調節する。   By using lecithin as a surfactant and stearic acid as a nutrient source, since these are natural products, adverse effects on the surrounding environment can be suppressed. In addition, an observation well 10 is installed to the lower end of the permeable layer 2, and at least the contamination concentration and nutrient amount of the permeable layer 2 are monitored to optimize the surfactant and nutrient source supplied to the upper clay layer 1. Adjust.

界面活性剤、栄養源とともに、嫌気性微生物を必要に応じて透水層2に供給してもよい。これによって、微生物を常に透水層に確保し、また栄養源を供給による微生物の分解活性を維持して汚染物質を確実に分解することができる。   You may supply anaerobic microorganisms to the water-permeable layer 2 with a surfactant and a nutrient source as needed. This ensures that microorganisms are always secured in the water permeable layer, and that the contaminants can be reliably decomposed while maintaining the decomposition activity of the microorganisms by supplying nutrient sources.

以上のように本発明は、汚染物質で汚染されている上部粘土層1の下部に位置する透水層2まで区画壁5を設置し、前記区画壁5内の上部粘土層1に界面活性剤および微生物の栄養源を高圧で注入し、汚染物質を上部粘土層1の土粒子から離脱、溶出させ、さらに離脱、溶出させた汚染物質および栄養源を透水層2に移動させて微生物分解を促進させることを特徴とする粘土層の汚染浄化方法としたものである。   As described above, in the present invention, the partition wall 5 is installed up to the water permeable layer 2 located below the upper clay layer 1 contaminated with the pollutant, and the surfactant and the surfactant are placed on the upper clay layer 1 in the partition wall 5. Injecting nutrient sources of microorganisms at a high pressure, detaching and eluting pollutants from the soil particles of the upper clay layer 1, and further detaching and eluting contaminants and nutrient sources to the permeable layer 2 to promote microbial degradation. This is a method for purifying clay layer contamination.

本発明によれば、粘土層の土壌粒子表面および土壌粒子間に強く吸着している汚染物質を界面活性剤により土壌粒子表面および土壌粒子間から含有水分に離脱、溶出させる。さらに粘土層の土壌粒子表面および土壌粒子間から含有水分に離脱、溶出した汚染物質および栄養源を砂礫土壌である透水層に移動させる。これによって透水層において微生物の生育および分解活性を高めて汚染物質の浄化を促進さることができる。   According to the present invention, the contaminants that are strongly adsorbed between the soil particle surface and between the soil particles of the clay layer are separated from the surface of the soil particles and between the soil particles by the surfactant, and are eluted. In addition, the contaminants and nutrients that are released from the surface and between the soil particles of the clay layer are transferred to the permeable layer, which is gravel soil. As a result, the growth and decomposition activity of microorganisms can be increased in the water permeable layer to promote the purification of contaminants.

また浄化設備をより簡素化することができる。   Moreover, the purification equipment can be further simplified.

有害物質の汚染された土壌の浄化処理における広範囲の用途にも適用できる。   It can be applied to a wide range of uses in the purification of soil contaminated with harmful substances.

本発明の一実施例の粘土層の汚染浄化方法を示す断面部分の基本構成図The basic block diagram of the cross-sectional part which shows the contamination purification method of the clay layer of one Example of this invention

符号の説明Explanation of symbols

1 上部粘土層
2 透水層
3 下部粘土層
4 汚染領域
5 区画壁
5a 細孔
6 供給管
7 高圧ポンプ
8 貯留容器
9 貯留容器
10 観測用井戸
DESCRIPTION OF SYMBOLS 1 Upper clay layer 2 Permeable layer 3 Lower clay layer 4 Contaminated area 5 Partition wall 5a Pore 6 Supply pipe 7 High pressure pump 8 Storage container 9 Storage container 10 Observation well

Claims (2)

汚染物質で汚染されている粘土層の下部に位置する透水層まで区画壁を設置し、前記区画壁内の粘土層に界面活性剤および微生物の栄養源を高圧で注入し、汚染物質を粘土層の土粒子から離脱、溶出させ、さらに離脱、溶出させた汚染物質および栄養源を透水層に移動させて微生物分解を促進させることを特徴とする粘土層の汚染浄化方法。 A partition wall is installed up to the permeable layer located under the clay layer contaminated with the pollutant, and a surfactant and a nutrient source of microorganisms are injected into the clay layer in the partition wall at a high pressure, and the contaminant is put into the clay layer. A method for decontaminating a clay layer, characterized in that the contaminants and nutrients separated and eluted from the soil particles are moved to the water-permeable layer to promote microbial degradation. 前記界面活性剤がレシチンであり、前記栄養源がステアリン酸である請求項1に記載の粘土層の汚染浄化方法。

The method of claim 1, wherein the surfactant is lecithin and the nutrient source is stearic acid.

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
RU2503511C1 (en) * 2012-08-07 2014-01-10 Общество с ограниченной ответственностью "Научно-исследовательский институт природных газов и газовых технологий-Газпром ВНИИГАЗ" Method of removal oil products from contaminants
JPWO2018043507A1 (en) * 2016-08-29 2019-07-04 株式会社竹中工務店 Underground soil remediation method

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH09276841A (en) * 1996-04-12 1997-10-28 Canon Inc Method and apparatus for purifying contaminated soil
JP2004025158A (en) * 2002-05-10 2004-01-29 Tanaka Kankyo Kaihatsu Kk Cleaning method of polluted stratum and apparatus therefor
JP2004057953A (en) * 2002-07-30 2004-02-26 Okumura Corp Decontamination method of contaminated soil at original position
JP2004195321A (en) * 2002-12-17 2004-07-15 Matsushita Electric Ind Co Ltd Soil or ground water treatment method
JP2004322073A (en) * 2002-10-29 2004-11-18 Katayama Chem Works Co Ltd Treatment method for contaminated soil
JP2005262107A (en) * 2004-03-19 2005-09-29 Internat Center For Environmental Technol Transafer Method for cleaning matter contaminated with organochlorine compound

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH09276841A (en) * 1996-04-12 1997-10-28 Canon Inc Method and apparatus for purifying contaminated soil
JP2004025158A (en) * 2002-05-10 2004-01-29 Tanaka Kankyo Kaihatsu Kk Cleaning method of polluted stratum and apparatus therefor
JP2004057953A (en) * 2002-07-30 2004-02-26 Okumura Corp Decontamination method of contaminated soil at original position
JP2004322073A (en) * 2002-10-29 2004-11-18 Katayama Chem Works Co Ltd Treatment method for contaminated soil
JP2004195321A (en) * 2002-12-17 2004-07-15 Matsushita Electric Ind Co Ltd Soil or ground water treatment method
JP2005262107A (en) * 2004-03-19 2005-09-29 Internat Center For Environmental Technol Transafer Method for cleaning matter contaminated with organochlorine compound

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
RU2503511C1 (en) * 2012-08-07 2014-01-10 Общество с ограниченной ответственностью "Научно-исследовательский институт природных газов и газовых технологий-Газпром ВНИИГАЗ" Method of removal oil products from contaminants
JPWO2018043507A1 (en) * 2016-08-29 2019-07-04 株式会社竹中工務店 Underground soil remediation method

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