JP4645403B2 - Clay layer contamination purification method - Google Patents
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- JP4645403B2 JP4645403B2 JP2005297527A JP2005297527A JP4645403B2 JP 4645403 B2 JP4645403 B2 JP 4645403B2 JP 2005297527 A JP2005297527 A JP 2005297527A JP 2005297527 A JP2005297527 A JP 2005297527A JP 4645403 B2 JP4645403 B2 JP 4645403B2
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- 239000004927 clay Substances 0.000 title claims description 46
- 238000000746 purification Methods 0.000 title claims description 19
- 238000000034 method Methods 0.000 title claims description 16
- 238000011109 contamination Methods 0.000 title claims description 11
- 239000002689 soil Substances 0.000 claims description 49
- 239000002245 particle Substances 0.000 claims description 26
- 235000015097 nutrients Nutrition 0.000 claims description 23
- 239000000356 contaminant Substances 0.000 claims description 22
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 19
- 239000004094 surface-active agent Substances 0.000 claims description 18
- 244000005700 microbiome Species 0.000 claims description 15
- 238000005192 partition Methods 0.000 claims description 13
- IIZPXYDJLKNOIY-JXPKJXOSSA-N 1-palmitoyl-2-arachidonoyl-sn-glycero-3-phosphocholine Chemical group CCCCCCCCCCCCCCCC(=O)OC[C@H](COP([O-])(=O)OCC[N+](C)(C)C)OC(=O)CCC\C=C/C\C=C/C\C=C/C\C=C/CCCCC IIZPXYDJLKNOIY-JXPKJXOSSA-N 0.000 claims description 6
- 235000021355 Stearic acid Nutrition 0.000 claims description 6
- 239000000787 lecithin Substances 0.000 claims description 6
- 229940067606 lecithin Drugs 0.000 claims description 6
- 235000010445 lecithin Nutrition 0.000 claims description 6
- QIQXTHQIDYTFRH-UHFFFAOYSA-N octadecanoic acid Chemical group CCCCCCCCCCCCCCCCCC(O)=O QIQXTHQIDYTFRH-UHFFFAOYSA-N 0.000 claims description 6
- OQCDKBAXFALNLD-UHFFFAOYSA-N octadecanoic acid Natural products CCCCCCCC(C)CCCCCCCCC(O)=O OQCDKBAXFALNLD-UHFFFAOYSA-N 0.000 claims description 6
- 239000008117 stearic acid Substances 0.000 claims description 6
- 238000000354 decomposition reaction Methods 0.000 claims description 5
- 239000003344 environmental pollutant Substances 0.000 description 17
- 231100000719 pollutant Toxicity 0.000 description 17
- 230000000694 effects Effects 0.000 description 8
- 239000003921 oil Substances 0.000 description 7
- 150000004045 organic chlorine compounds Chemical class 0.000 description 6
- 230000015556 catabolic process Effects 0.000 description 4
- 238000006731 degradation reaction Methods 0.000 description 4
- 238000011065 in-situ storage Methods 0.000 description 4
- 238000009423 ventilation Methods 0.000 description 4
- 239000003673 groundwater Substances 0.000 description 3
- 239000000463 material Substances 0.000 description 3
- 230000000813 microbial effect Effects 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 230000002411 adverse Effects 0.000 description 2
- 238000009412 basement excavation Methods 0.000 description 2
- 230000000903 blocking effect Effects 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000000295 fuel oil Substances 0.000 description 2
- 239000011148 porous material Substances 0.000 description 2
- 238000005067 remediation Methods 0.000 description 2
- 229920006395 saturated elastomer Polymers 0.000 description 2
- 238000003860 storage Methods 0.000 description 2
- 239000005995 Aluminium silicate Substances 0.000 description 1
- XSTXAVWGXDQKEL-UHFFFAOYSA-N Trichloroethylene Chemical group ClC=C(Cl)Cl XSTXAVWGXDQKEL-UHFFFAOYSA-N 0.000 description 1
- 238000013019 agitation Methods 0.000 description 1
- 235000012211 aluminium silicate Nutrition 0.000 description 1
- 239000000440 bentonite Substances 0.000 description 1
- 229910000278 bentonite Inorganic materials 0.000 description 1
- SVPXDRXYRYOSEX-UHFFFAOYSA-N bentoquatam Chemical compound O.O=[Si]=O.O=[Al]O[Al]=O SVPXDRXYRYOSEX-UHFFFAOYSA-N 0.000 description 1
- 238000005352 clarification Methods 0.000 description 1
- 150000002013 dioxins Chemical class 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 238000003780 insertion Methods 0.000 description 1
- 230000037431 insertion Effects 0.000 description 1
- NLYAJNPCOHFWQQ-UHFFFAOYSA-N kaolin Chemical compound O.O.O=[Al]O[Si](=O)O[Si](=O)O[Al]=O NLYAJNPCOHFWQQ-UHFFFAOYSA-N 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 229930014626 natural product Natural products 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
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- Processing Of Solid Wastes (AREA)
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、汚染物質を回収する処理方法である(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. This is a treatment method for applying to a contaminated area of a saturated hardly permeable air permeable layer and recovering the pollutant (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)。
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
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.
地表面から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を囲う区画壁を設置し、高圧ポンプに接続された供給管の先端を前記区画壁内の粘土層に開口し、前記高圧ポンプにより前記供給管を介して界面活性剤および微生物の栄養源を前記粘土層に高圧で注入し、前記界面活性剤により汚染物質を前記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、この透水層において微生物の育成と前記汚染物質の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。
Install a partition wall that surrounds the ground surface to the water permeable layer located below the clay layer that is contaminated with contaminants, open the tip of the supply pipe connected to the high-pressure pump to the clay layer in the partition wall , wherein via the supply pipe by a high-pressure pump injecting a surfactant and a nutrient source for microorganisms at high pressure into the clay layer, leaving the contaminant by the surfactant from the soil particles of the clay layer, eluted, further withdrawal The clay layer contamination purification method is characterized in that the eluted pollutants and nutrient sources are moved to the water permeable layer, and the growth of microorganisms and the decomposition of the contaminants are promoted in the water permeable layer .
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離脱、溶出させ、この汚染物質および栄養源を透水層に移動させることにより、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せることができるので、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ができる。 According to the present invention, the contaminants that are strongly adsorbed between the soil particle surface and the soil particles of the clay layer are separated and eluted by the surfactant, and the contaminants and nutrient sources are moved to the permeable layer. Because it is possible to enhance the growth and decomposition activity of microorganisms in the layer and promote the purification of pollutants, the pollutants such as oils and organochlorine compounds present in the clay layer can be efficiently and in situ It can be restored without the need for other equipment.
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せることができる。 Thus, it is Rukoto to promote remediation of contaminated material to increase the growth and degradation activity of the microorganisms in the aquifer.
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。 Because the clay layer is composed of kaolin, bentonite, etc., 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
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
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
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
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
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
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せることができる。
According to the present invention, contaminants that are strongly adsorbed between the soil particle surfaces 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 in the clay layer are transferred to the permeable layer, which is gravel soil. Thus, it is Rukoto to promote remediation of contaminated material to increase the growth and degradation activity of the microorganisms in the aquifer.
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.
1 上部粘土層(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
1 Upper clay layer (clay layer)
2 Water-
Claims (2)
The method of claim 1, wherein the surfactant is lecithin and the nutrient source is stearic acid.
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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 |
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Publication number | Priority date | Publication date | Assignee | Title |
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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 |
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